RE PORTS O F THE FINNI S H E N V I RO N M E N T I N ST I TUTE 4 0 | 2 0 1 4 Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia Tapio Lindholm, Jevgeni Jakovlev & Alexey Kravchenko (eds.) Fi n n i sh E nv i ronme nt Ins t itu te REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 40 | 2014 Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia Tapio Lindholm, Jevgeni Jakovlev & Alexei Kravchenko (eds.) Helsinki 2014 Finnish Environment Institute REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 40 | 2014 Finnish Environment Institute Natural Environment Centre Layout: Pia Kauppinen Cover photo: Clouded Apollo, Parnassius mnemosyne and Rough Hawkbit, Leontodon hispidus meet in Zaonezhye. Andrei Humala. English revision: Minna Hartikainen The publication is also available in the internet: www.syke.i/julkaisut | helda.helsinki.i/syke Juvenes Print, 2015 ISBN 978-952-11-4404-2 (pbk.) ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 (printed) ISSN 1796-1726 (online) 441 729 Painotuote FOREWORD Anna Kuhmonen Zaonezhye Peninsula has a distinctive and diverse natural heritage, and its unique habitats are included in regional nature conservation plans. Although the value of its habitats and landscapes has been known for a long time, the documentation necessary for the establishment of a protected area has been lacking and high conservation value forests have been threatened by forest logging. The Barents Protected Area Network (BPAN) project promotes and supports the establishment of a representative network of protected areas in the Barents Region. Protected area networks are an important tool in biodiversity conservation as well as climate change adaptation and mitigation. A representative network of protected areas safeguards biodiversity, supports natural ecosystems and maintains ecosystem services. In addition to evaluating the network of protected areas in Northwest Russia, the BPAN project has implemented pilot projects in high conservation value areas in order to support the establishment of new protected areas. All the countries in the Barents Region - Russia, Finland, Sweden and Norway - are parties to the Convention on Biological Diversity. In 2010, the parties committed to halting the loss of biodiversity by 2020 and set the 20 Aichi Biodiversity Targets. The Aichi Target 11 calls for at least 17% protection of terrestrial and inland water areas, especially areas of particular importance for biodiversity and ecosystem services, by 2020. Protected areas cover 13.4 % of the Barents Region, while the level of protection in the Republic of Karelia is 4.7 % (2013). Regional and national conservation plans include 59 400 km2 of planned protected areas in the whole Barents Region. However, implementation of conservation plans takes time, and the global targets have been set for 2020. The results of the BPAN project show that the implementation of conservations plans should be quicker and more effective. In 2012, the BPAN project selected ive territories in Northwest Russia where nature conservation was to be promoted through ield studies as well as other activities. In the Republic of Karelia, a pilot project was implemented in the high conservation value forests of Zaonezhye Peninsula. Earlier studies on the peninsula showed that the area supported valuable habitats and species. However, even though forests were included in the regional conservation plan, they were at the same time leased by forestry companies and threatened by logging. Between 2013 and 2014, the BPAN project carried out ield work and documented natural values within the planned Zaonezhye nature park, focusing on high conservation value forests. These activities were conducted by the Finnish Environment Institute, Karelian Research Centre and the Directorate of regional protected areas of the Republic of Karelia in cooperation with experts from the Universities of Helsinki and Eastern Finland, and the Finnish Nature League. This publication presents information on hundreds of red-listed species and valuable habitats. Promoting the protection of high conservation value forests on Zaonezhye Peninsula has been an important part of the BPAN project. We are grateful to all researchers for their valuable input into the ield work as well as this publication. For inancing this work we thank the Nordic Council of Ministers, Ministry of the Environment and Ministry for Foreign Affairs of Finland, Sweden and Norway, and WWF-Russia. We hope that this publication contributes to establishing the valuable nature areas of Zaonezhye Peninsula as statutory protected areas. CONTENTS Foreword ............................................................................................................................ 3 Zaonezhye Peninsula – The pearl of Lake Onega ..........................................7 Introduction ........................................................................................................7 Old villages and traditional land use in Zaonezhye .................................... 9 Nature studies in Zaonezhye ......................................................................... 10 Conservation activities in Zaonezhye ........................................................... 12 Threatened species and proposals for their protection.............................. 13 Acknowledgements .........................................................................................14 1 Geology and physical geography of Zaonezhye Peninsula area ............17 1.1 1.2 1.3 1.4 1.5 1.6 Geological description of Zaonezhye Peninsula......................................17 Introduction ......................................................................................................17 Geomorphology and Quaternary deposits of Zaonezhye ........................ 26 Igneous rocks, mineralogeny and commercial minerals of Zaonezhye Peninsula ..................................................................................29 Geomorphology and Quaternary deposits of Zaonezhye .....................35 Introduction ......................................................................................................35 Geomorphology ...............................................................................................37 Hydrological characteristics of Zaonezhye Peninsula ............................ 41 Introduction ......................................................................................................41 Results................................................................................................................41 Soils and their characteristics on Zaonezhye Peninsula ........................ 53 Introduction ......................................................................................................53 Soil types and their characteristics ............................................................... 53 Conclusions ...................................................................................................... 55 Paleogeography of Zaonezhye Peninsula .................................................. 57 Introduction ......................................................................................................57 Geological Periods ........................................................................................... 60 Nature protected areas in Zaonezhye ......................................................... 75 Introduction ......................................................................................................75 Overview of protected areas in Karelia........................................................ 75 Protected areas on Zaonezhye Peninsula and its adjacent islands........... 76 Planned protected areas on Zaonezhye Peninsula .....................................77 2 Biomes and biogeography of Zaonezhye Peninsula area .........................81 2.1 Modern landscapes of Zaonezhye Peninsula ........................................... 81 2.2 Landscape structure of Zaonezhye Peninsula ........................................103 Introduction ....................................................................................................103 Results..............................................................................................................104 The structure of forest land and forest stands in Zaonezhye Peninsula ................................................................................... 111 Introduction .................................................................................................... 111 Results.............................................................................................................. 111 Forest structures and human impact on Zaonezhye Peninsula: a classiication and case studies ................................................................. 125 Introduction ....................................................................................................125 Methods........................................................................................................... 126 Results and discussion ..................................................................................126 Mires of the Zaonezhye Peninsula............................................................131 Introduction ....................................................................................................131 Study area ....................................................................................................... 132 Material and methods ...................................................................................132 Results and discussion ..................................................................................132 Mires conservation in Zaonezhye ............................................................... 137 Meadows in Zaonezhye ...............................................................................147 Introduction ....................................................................................................147 History of the study of the Zaonezhye’ grasslands ................................. 148 Future of grasslands in Zaonezhye ............................................................. 150 2.3 2.4 2.5 2.6 Reports of the Finnish Environment Institute 40 | 2014 5 3 Flora and fauna in Zaonezhye Peninsula area.............................................153 3.1 3.2 3.3 3.4 3.5 3.6 3.7 Vascular plant lora of Zaonezhye Peninsula ......................................... 153 Introduction ....................................................................................................153 History of loristic studies on the peninsula ............................................. 155 The following century ................................................................................... 156 Recent decades ...............................................................................................157 Present knowledge......................................................................................... 160 List of vascular plant species of Zaonezhye, with annotations for threatened and indicator species............................ 164 Bryophyte lora of Zaonezhye Peninsula ............................................... 193 Abstract ...........................................................................................................193 Introduction ....................................................................................................193 Conclusions .....................................................................................................198 Appendix List of mosses from Zaonezhye Peninsula .............................. 200 List of lichens and allied fungi collected on Zaonezhye Peninsula ...................................................................................207 History of the studies of lichens in Zaonezhye Peninsula and adjacent islands ............................................... 207 Acknowledgements .......................................................................................209 Red-listed and indicator lichens of Zaonezhye Peninsula...................223 Introduction ....................................................................................................223 Material and methods ...................................................................................224 Results..............................................................................................................224 Epiphytes of deciduous trees ....................................................................... 224 Usnea lichens and other fruticose epiphytes ............................................ 226 Epiphytes of spruce ....................................................................................... 227 Lichens on dead wood ................................................................................. 228 Basic and siliceous cliffs................................................................................229 Discussion .......................................................................................................230 Aphyllophoroid fungi of Zaonezhye Peninsula.....................................233 Introduction ....................................................................................................233 Mycological studies in Zaonezhye Peninsula and adjacent areas ..........233 Results..............................................................................................................234 Species conined to pine................................................................................236 Species conined to spruce............................................................................ 236 Species conined to aspen ............................................................................. 236 The most noteworthy indings of threatened and rare species of saproxylic fungi ...........................................................237 Appendix......................................................................................................... 244 Insect fauna of Zaonezhye Peninsula and adjacent islands ................ 257 Introduction ....................................................................................................257 History of entomological studies on Zaonezhye Peninsula .................... 257 Study area and methods ............................................................................... 258 Results..............................................................................................................260 Conclusions .....................................................................................................262 Acknowledgements .......................................................................................263 Annotated list of the insect species included in Red Data Book of the Republic of Karelia (Ivanter & Kuznetsov 2007) and other noteworthy insect species .................................................................................................. 263 List of insect species recorded in Zaonezhye and adjacent islands ....... 275 Localities in Zaonezhye area used in species lists of vascular plants, bryophytes, lichens, fungi and insects, and their toponyms .............. 339 Document page ........................................................................................................ 357 Ли и ия и ции ................................................................................... 358 Kuvailulehti ..............................................................................................................359 Presentationsblad.....................................................................................................360 6 Reports of the Finnish Environment Institute 40 | 2014 Zaonezhye Peninsula – The pearl of Lake Onega Tapio Lindholm*, Jevgeni Jakovlev * and Alexei Kravchenko** * The Finnish Environment Institute (SYKE), P.O.Box 140, 00251 Helsinki, Finland. ** * Forest Research Institute of the Karelian Research Center of the Russian Academy of Sciences, Petrozavodsk, 11 Pushkinskaya St., RU-185910 Petrozavodsk, Karelia, Russia Introduction The Republic of Karelia is located mostly in the eastern part of the Baltic shield, which is composed of Precambrian crystalline rock. However, it includes areas that differ markedly in their geological background, soils and vegetation. Zaonezhye Peninsula is a particularly interesting area in terms of the variety of landscapes, habitats and species. Zaonezhye Peninsula (Zaonezhsky Peninsula; in Russian transcription) is situated on the northwestern coast of Lake Onega. Its eastern shores are washed by the Gulf of Zaonezhye. In the north the peninsula is bordered by Povenetskiy Bay, while to the west it is bounded by Lizhma Bay and the Gulf of Bolshoe Onego (Fig. 1). “Zaonezhye” is used here in a wider sense to include Zaonezhye Peninsula as well as two adjacent peninsulas, Lizhma and Sjar, which are separated by the long and narrow bays of Lake Onega. In the south, Zaonezhye Peninsula shelters an archipelago of numerous islands, also known as Kizhi skerries or the Kizhi archipelago. The archipelago includes two relatively large islands, Bolshoy Klimenetsky and Bolshoy Lelikovsky, which have several old villages, fertile valleys of unique grassland and patches of old-growth forest. The most famous among the islands is Kizhi Island where monumental 17th century churches, included in the UNESCO World Heritage List, are preserved. Often the whole area on the opposite shore of Lake Onega is called Zaonezhye. It is separated from the city of Petrozavodsk by a mere few dozen kilometers of water and has therefore good connections by boat. Zaonezhye is considered a separate biogeographic region (Ramenskaya 1983). According to modern estimates (e.g. Elina et al. 2010), the territory of Zaonezhye is unique in that it contains nearly every type of terrain and unconsolidated sediment known in the vast expanses of northwest Russia. It is characterized by a high diversity of basic limestone and carbonate rocks that determine the fertility of local soils as well Reports of the Finnish Environment Institute 40 | 2014 7 as the unique diversity of habitats, lora and fauna. Numerous rare calciphile plant and lichen species are found here, as well as rich, eutrophic wetlands. Long-term farming and animal husbandry have led to a large number of grassland communities in the area. As a result, a mosaic structure of diverse habitats has evolved here. Europe’s second largest lake, Lake Onega, with its clear and deep waters also affect the local climate by making it milder. Fig.1. Geographical location on Zaonezhye Peninsula 8 Reports of the Finnish Environment Institute 40 | 2014 Old villages and traditional land use in Zaonezhye The late-medieval villages of Zaonezhye Peninsula and the Kizhi archipelago maintained a vibrant rural society until the middle of the 20th century. According to the census of 1887 (Census of population 1904), in the end of the 19th century the population of Zaonezhye Peninsula consisted of 47 000 people. At the time, the population density of the peninsula was at its highest at 13.4 people per km2, while the population density of the entire Olonets Province (present-day Republic of Karelia) was only 2.8 people per km2. Nowadays most of the villages have been abandoned. However, extraordinary pieces of Russian wooden architecture remind us of their past glory. Many old churches are still standing thanks to summer residents who continue to repair them. Fig. 2. Old wooden church in the village of Tambitsy on the southeastern coast of Zaonezhye Peninsula (Photo: Andrei Humala) The southeastern parts of Zaonezhye Peninsula, together with the northern shores of Lake Ladoga, have the longest history of traditional land use in Karelia. The peninsula has been permanently inhabited for thousands of years. The irst traces of pollen of crop plants such as wheat, oat and rye appeared nearly 1 000 years ago (Lavrova et al. 2005). In the past, slash-and-burn-cultivation was the main type of agriculture in Zaonezhye. However, despite a gradual increase in the proportion of cultivated land, a large part of the area has stayed relatively intact. At present, Zaonezhye Peninsula incorporates near-natural landscapes in its central part and areas showing traces of past agricultural activities along the coast of Lake Onega. The central parts of Zaonezhye Peninsula consist of almost unpopulated ridge landscapes that have not been easily accessible for forestry or agriculture. Contrastingly, lowland areas on the southern and southeastern shores of Zaonezhye Peninsula as well as the islands of the Kizhi archipelago have been profoundly affected by slashand-burnt cultivation over time. The present distribution of forest types is mainly the result of the earlier human activities. Originally, lowland areas were covered with coniferous forests that were growing in close to optimal conditions and were therefore characterized by their high quality. Nowadays, near-natural coniferous forest stands Reports of the Finnish Environment Institute 40 | 2014 9 are preserved only in few places where logging is dificult, including paludiied areas and steep, rocky slopes close to the shoreline. A part of the preserved old-growth forests is located within the protected belts of water bodies. For example, the protected belt along the shores of Lake Onega is one kilometre wide. According to the Soviet classiication of forests (1943), which was used until the recent Forest Code (2006), forests along water bodies belonged to water protective forest group and were automatically excluded from logging. The rest of the forests have been affected by selective cuttings. Especially close to the villages, these forests have formed naturally on abandoned hay meadows and ields. According to the forest inventory of 1999 (Gromtsev & Krutov 2000), pine and spruce forests occupy nearly 60 percent of the forest cover, in approximately equal proportions. The remaining area is covered by forests, dominated by birch (ca. 30%), aspen (5%) or grey alder (6%). Intact mires are preserved mainly in the central part of the peninsula where they cover depressions between long and narrow ridges. In lowland areas, numerous small, eutrophic fens occupy narrow bays along the shoreline. In the past, the local population used the lowlands for haymaking. At present these areas combine mire and meadow vegetation, including many red-listed species. However, the hydrology of many mires and brookside forests is affected by the Canadian beaver (Castor canadensis), which is relatively common in the area. The native beaver species, Castor iber, has become extinct here. Nature studies in Zaonezhye There is a long history of nature studies in Zaonezhye that date back to the 19th century. At that time, Finnish researchers prepared and published detailed lists of plants, lichen (Norrlin 1871, 1876) and beetles (Poppius 1899) that are of international importance. Around the same time, Alexander Günther from Petrozavodsk collected and documented hundreds of plant and insect species that have later been recorded from Zaonezhye also by other researchers (See Chapters 3.1, 3.3 and 3.6). After a long break in the irst half of the 20th century, studies resumed irst by Finnish researchers in the 1940s and then by the Karelian Research Centre of the Russian Academy of Sciences (hereinafter KRC RAS) in Petrozavodsk. Until very recently, the lora and fauna of the area have remained largely unexplored. The Atlas of the distribution of vascular plants in northern Europe (Hulten 1971) fails to mention a number of local calciphile and other plants that require fertile soils. There are several scientiic publications on the Kizhi archipelago (e.g. Elina et al. 1999, Ieshko & Protasov 2005, etc) and the central part of Zaonezhye Peninsula (e.g. Gromtsev 2013). However, the irst report on the biodiversity inventories and studies of Zaonezhye (Gromtsev & Krutov 2000) still remains the only publication that covers the entire Zaonezhye Peninsula and the adjacent islands. Mire and meadow vegetation studies have been conducted during several expeditions of the Laboratory for mire ecosystems of the Institute of biology in the past 30 years. These studies have resulted in the establishment of several nature monuments for the protection of mires. Also new data on mire and meadow vegetation and dynamics have been created (See Chapters 2.5 and 2.6). Between 2nd and 8th July 2004, leading Finnish and Russian botanists and entomologists carried out the irst Finnish-Russian expedition on the “Ecolog” research vessel of the KRC RAS. Its goal was to visit hotspots of rare and threatened plant, lichen and insect species. The expedition included 12 participants: Alexei Kravchenko (vascular plants), Oleg Kuznetsov (mire vegetation), Margarita Boychuk (mosses), Margarita Fadeeva (lichens), Alexei Polevoi and Andrei Humala (insects) from the KRC RAS; Elena 10 Reports of the Finnish Environment Institute 40 | 2014 Fig. 3. Intact forest landscapes and mires on Zaonezhye Peninsula and the adjacent areas (after: Kobyakov & Jakovlev (2013), areas visited in 2013 and proposed nature monuments, 1-6. Reports of the Finnish Environment Institute 40 | 2014 11 Gnatyuk from the Petrozavodsk State University (vascular plants), Pertti Uotila and Mikko Piirainen from the Botanical Museum of the Finnish Museum of Natural History in Helsinki (vascular plants); Professor Emeritus Rauno Ruuhijärvi from the University of Helsinki (mire vegetation); Tapio Lindholm (mire vegetation and vascular plants) and Jevgeni Jakovlev (insects) from the Finnish Environment Institute. The following localities were studied: 1. Islands Paleostrov, Rechnoi and Meg-Ostrov near the northern tip of Zaonezhye Peninsula. Different grassland and forest biotopes (old spruce stands, black alder swamps). A large abandoned monastery on Paleostrov Island as well as its old meadows and tree alleys. 2. The southeastern shore of Zaonezhye Peninsula (in the vicinity of the villages of Kuzaranda and Tipinitsy) and the islands of Khedostrov, Shunevsky and Yuzhny Oleniy. High-quality spruce forests with Tilia cordata in the undergrowth. Yuzhny Oleniy Island is the only island in the area. It is also one of three islands in Karelia that are entirely formed of dolomite. 3. Bolshoi Klimenetsky and Bolshoi Lelikovsky Islands, Cape Radkolye. Oldgrowth spruce-dominated forests of Oxalis-Myrtillys type, spruce mires and forested lowland mires as well as grasslands in previously settled areas. Many regionally rare and threatened species of vascular plants, bryophytes, lichens and insects have been found here. The members of the expedition concluded that Zaonezhye contains unique biotopes and habitats of threatened species. They recorded a number of vascular plant, bryophyte, lichen and insect species that are considered rare or threatened in the Republic of Karelia and concluded that more detailed research is required. In the summer of 2013, another international nature expedition was carried out in the southern lowlands of Zaonezhye Peninsula in the framework of the Barents Protected Area Network (BPAN) project. The experts Alexei Kravchenko, Margarita Fadeeva, Andrei Humala, Alexei Polevoi, Boris Rayevsky and Anna Ruokolainen from the KRC RAS, Jevgeni Jakovlev and Kimmo Syrjänen from the Finnish Environment Institute, Timo Kuuluvainen from the University of Helsinki, Olli-Pekka Tikkanen from the University of Eastern Finland and Olli Manninen and Jyri Mikkola from the NGO Finnish Nature League studied natural forests and mires along the southern coast of Zaonezhye Peninsula as well as old-growth forests on Sjar Peninsula on the opposite shore of Lizhma Bay. The expedition aimed to study high conservation value forests (Fig.3) that were identiied between 2007 and 2011 within the “Gap analysis in northwest Russia” (Kobyakov & Jakovlev 2013). As a result of this expedition, new nature monuments were proposed (See Fig 3 and Chapter 1.6). Conservation activities in Zaonezhye Currently planned protected areas in the Republic of Karelia cover an area of 59 400 km2. However, the status of planned protected area alone does not secure nature values. The establishment of protected areas is a long process and in many cases valuable areas have been lost to forestry before the areas have been protected. In Zaonezhye, conservation activities began between 1965 and 1969. Initially, old wooden buildings of historical interest were transported to Kizhi Island where the Kizhi state open-air museum of history, architecture and ethnography was established. 12 Reports of the Finnish Environment Institute 40 | 2014 Later the federal Kizhi zoological nature reserve (Kizhskiy zakaznik) was established (22nd September 1989), based on the recommendations of Tatyana Khokhlova and Oleg Kuznetsov from the Institute of Biology of the KRC RAS. Between 1989 and 1998, ten nature monuments were established in Zaonezhye for the protection of mires (Khokhlova et al. 2000). These regional protected areas cover 1 512 hectares, including Lizh Peninsula, and contain both unique and characteristic Eastern European mire ecosystems. They were established on the basis of the recommendations by the Laboratory of mire ecosystems of the Institute of biology of the KRC RAS. In 1992 KRC RAS produced a feasibility study for the establishment of a nature park with an area of 115 000 ha on Zaonezhye Peninsula (Gromtsev et al. 1992). After detailed ield studies, KRC RAS published an assessment of the protected area (Gromtsev 2013). The proposed Zaonezhsky landscape reserve (zakaznik) covers 106 373 ha, of which 86 839 ha is on land. At the same time, the Karelian NGO “SPOK” prepared recommendations for the protection of southern and eastern Zaonezhye Peninsula (SPOK 2013) (See Chapter 2.3). In the Republic of Karelia, protected areas are created only in accordance with programmes approved by the Russian government. Therefore, planning the establishment of new protected areas is feasible only in cases where such plans are already included in the programmes of the Russian government (protected areas of federal importance: strict nature reserves and national parks) or the government of the Republic of Karelia (protected areas of regional importance: nature parks, nature reserves or zakazniks and nature monuments). The list of planned protected areas in the Republic of Karelia is a part of the Land use plan of the Republic of Karelia until 2030, approved by the government of the republic (Scheme 2012; directive № 102-P from 6th July 2007). It contains two lists concerning the establishment of new protected areas: The irst list includes protected areas that are planned to be established in the irst stage before 2020. Regional nature conservation authorities are presented with all necessary background material for the establishment of these protected areas, including detailed information about the area and its borders as well as ecological values, economic and social characteristics, and the proposed protection regime of the planned protected area. The second list includes perspective new protected areas where red-list species or other natural objects of high conservation value have been recorded. However, the necessary background material for their establishment has not been compiled yet. These protected areas are planned to be established in the second stage between 2020 and 2030. According to the latest changes to the Land use plan of the Republic of Karelia from July 2014 (Regulation 2014), Zaonezhsky landscape reserve, covering 106 373 ha in the northwestern part of Zaonezhye Peninsula, is included in the list of protected areas to be established before 2020. KRC RAS has prepared the background material necessary for the establishment of this protected area (Gromtsev et al. 2013). Another protected area, Zaonezhye nature park, which has been included in the Land use plan of the Republic of Karelia since 2007, is planned to be established in the second stage between 2020 and 2030. It covers 119 600 ha in the southeastern part of Zaonezhye Peninsula (partly overlapping the Zaonezhsky landscape reserve). Threatened species and proposals for their protection There is more than one concept of biodiversity but it is generally accepted that the basic unit of biodiversity is the species. For that reason, biodiversity studies provide the background for conservation. Records of threatened species, included in the Rus- Reports of the Finnish Environment Institute 40 | 2014 13 sian and regional red data books, are therefore of great importance. Establishing new protected areas or expanding existing ones to cover habitats of rare and threatened species is the main legislative tool to protect species and habitats. During the expeditions, the southeastern lowlands of Zaonezhye Peninsula were identiied as important for the conservation of biodiversity. The list of species recorded during these expeditions is impressive: it includes approximately 130 species that are red-listed in the Republic of Karelia (Ivanter & Kuznetsov 2007), more than 100 indicator species of valuable natural forests (according to Andersson et al. 2009) as well as numerous otherwise interesting or rare species, included in international lists of threatened species, such as the IUCN Red List (2014) and the Red Data Book of European Bryophytes (1995), or the 2010 Red List of Finnish species (Rassi et al. 2010). Furthermore, several species of fungi such as Ganoderma lucidum, lichens such as Lobaria pulmonaria and Bryoria fremontii and vascular plants such as Littorella unilora, Lobelia dortmanna and Isoetës lacustris are included in the latest Red list of plants and fungi of the Russian Federation (Trutnev 2008). Also, one butterly species, Clouded Apollo (Parnassius mnemosyne), is included in the Red list of animals of the Russian Federation (Danilov-Danilyan et al. 2001). Detailed descriptions of distributions and ecology of threatened species of federal and regional importance are presented in Chapter 3. The identiied habitats of these species serve as grounds for the establishment of nature monuments (see Chapter 1.6). Besides promoting conservation, the purpose of this book is to gather basic knowledge of the nature on Zaonezhye Peninsula and the adjacent islands. This publication consists of 19 articles on paleogeography, geology and geomorphology as well as the soils and hydrology of Zaonezhye Peninsula. It also includes descriptions of the landscapes and main ecosystems in the area, including forests, mires and meadows. In this book we present for the irst time full lists of vascular plant, bryophyte, lichen, wood-growing fungi and insect species recorded from the area to date. Acknowledgements This book has been prepared owing to great efforts by several researchers from the Karelian Research Centre of the Russian Academy of Sciences as well as the Finnish Environment Institute, Universities of Helsinki and Eastern Finland. We are grateful for all the researchers who took part in the ield work and the preparation of this publication. Professor Pertti Uotila from the University of Helsinki has made useful comments about the manuscript. Grigory Sokolov (Petrozavodsk) has translated some of the articles into English and Minna Hartikainen (London) has made linguistic corrections to this work. The maps (Fig. 1 and 3) have been prepared by Denis Dobrynin from the WWF Russia, Arkhangelsk. The Finnish-Russian working group on nature conservation, chaired by Aimo Saano (Parks & Wildlife Finland, Metsähallitus) and Tapio Lindholm (Finnish Environment Institute), inanced the ield work in 2004. The ield studies in 2013 were implemented by the BPAN pilot project, coordinated by Anna Kuhmonen and Jevgeni Jakovlev (Finnish Environment Institute) in cooperation with the Directorate of regional protected areas of the Republic of Karelia, lead by Denis Maksimov. This book is prepared and published as a part of the BPAN project, inanced by the Nordic Council of Ministers, governments of Finland, Sweden and Norway, and WWF-Russia. This support is cordially acknowledged. 14 Reports of the Finnish Environment Institute 40 | 2014 REFERENCES AЧНОrssШЧ, L., AХОбООЯК, N. M. & KЮгЧОЭsШЯК, E. S. (ОНs). 2009. ., . ., . . . ДSЮrЯОв ШП ЛТШХШРТМКХХв ЯКХЮКЛХО ПШrОsЭs ТЧ NШrЭС-АОsЭОrЧ EЮrШЩОКЧ RЮssТК. − VШХ. 2.IНОЧЭТiМКЭТШЧ ЦКЧЮКХ ШП sЩОМТОs ЭШ ЛО ЮsОН НЮrТЧР sЮrЯОв КЭ sЭКЧН ХОЯОХЖ. SЭ-PОЭОrsЛЮrР.258 Щ. (IЧ RЮssТКЧ). CОЧsЮs ШП ЩШЩЮХКЭТШЧ. 1904. , 1897 . ББVII. . 3( ). ДCОЧsЮs ШП ЭСО ЩШЩЮХКЭТШЧ ШП RЮssТКЧ EЦЩТrО. TСО ЭСТrН ЧШЭОЛШШФ (ЭСО ХКsЭ ШЧО), , 1897 . ББVII.Ж − SЭ.-PОЭОrsЛЮrР. 172 . DКЧТХШЯ-DКЧТХвКЧ ОЭ КХ. (ОНs.). 2001 . . . ( .). ( ). ДRОН DКЭК BШШФ ШП RЮssТКЧ FОНОrКЭТШЧ (КЧТЦКХs)Ж. – AsЭrОХ. MШsМШа. 862 Щ. (IЧ RЮssТКЧ). СЭЭЩ://ЛТШНКЭ.rЮ/НЛ/rЛ/ EХТЧК, G. A., IОsСФШ, E. P., KrКsТХЧТФШЯ, P. V., KЮгЧОЭsШЯ, O. L., LЮФКsСШЯ, A. D. & KСШФСХШЯК, T. ВЮ. (ОНs). 1999. . ., . ., . ., . ., . ., . . . ДKТгСТ ArМСТЩОХКРШ ТsХКЧНs. BТШРОШРrКЩСТМ НОsМrТЩЭТШЧЖ. − PrШМООНТЧРs ШП ЭСО KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs.SОr. BТШРОШРrКЩСв ШП KКrОХТК. IssЮО 1. 172 Щ. (IЧ RЮssТКЧ). EХТЧК, G. A., LЮФКsСШЯ, A. D. & ВЮrФШЯsФКвК T. K. 2010. LКЭО GХКМТКХ КЧН HШХШМОЧО ЩКХКОШРОШРrКЩСв ШП EКsЭОrЧ FОЧЧШsМКЧНТК. − TСО FТЧЧТsС ОЧЯТrШЧЦОЧЭ 4/2010. 1-304. FШrОsЭ CШНО 2006. 04. 12. 2006 N 200-FГ. ДFШrОsЭ CШНО ШП ЭСО RЮssТКЧ FОНОrКЭТШЧ ШЧ 04. 12. 2006 N 200-FГЖ. (IЧ RЮssТКЧ). − AЯКТХКЛХО ПШr НШаЧХШКН ПrШЦ ЭСО аОЛsТЭО СЭЭЩ:// ааа.МШЧsЮХЭКЧЭ.rЮ/ЩШЩЮХКr/ЧОааШШН/. GrШЦЭsОЯ, A. N. (ОН.). 2013. . . (Щ .). : , . ДSОХФК ХКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ МСКrКМЭОrТsЭТМs, LКЧН UsО, CШЧsОrЯКЭТШЧЖ. − KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 179 Щ. (IЧ RЮssТКЧ). GrШЦЭsОЯ, A. N. & KrЮЭШЯ, V. I. (ОНs). 2000. , . ., , . . ( .). ( ). ДBТШНТЯОrsТЭв ТЧЯОЧЭШrТОs КЧН sЭЮНТОs ТЧ ЭСО КrОКs ШП ГКШЧОгСвО PОЧТЧsЮХК КЧН NШrЭСОrЧ LКНШРК sСШrО (ОбЩrОss ТЧПШrЦКЭТШЧ ЦКЭОrТКХs)Ж. − KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 344 Щ. (IЧ RЮssТКЧ). GrШЦЭsОЯ, A. N., GШХЮЛОЯ, A. I., ГСЮrКЯХОЯ, A. P. & IОsСТЧК A. V. 1992. . ., . ., . ., . . К « К ». ДГКШЧОгСвО NКЭЮrО PКrФЖ. 1992. − PrОЩrТЧЭ ШП К presentation at a Presidium session of the Karelian Research Center of Russian Academy of Sciences. PetrozaЯШНsФ. 35 Щ. (IЧ RЮssТКЧ). HЮХЭцЧ, E. 1971. AЭХКs öЯОr ЯтбЭОrЧКs ЮЭЛrОНЧТЧР Т NШrНОЧ. FКЧОrШРКЦОr ШМС ШrЦЛЮЧФsЯтбЭОr. − 2ЧН ОН. – SЭШМФholm. 56+531 p. IОsСФШ, E. P. & PrШЭКsШЯ, ВЮ. G.(ОНs.) 2005.TОЧ вОКrs ШП ЭСО ОМШХШРТМКХ ЦШЧТЭШrТЧР ТЧ ЭСО KТгСТЦЮsОЮЦ-rОsОrЯО. RОsЮХЭs, ЩrШЛХОЦs, ЩОrsЩОМЭТЯОs.KКrОХТКЧ. − RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs, PОЭrШгКЯШНsФ.177 Щ. (IЧ RЮssТКЧ). IUCN 2014: IUCN RОН LТsЭ ШП TСrОКЭОЧОН SЩОМТОs. VОrsТШЧ 2014.3. URL: <СЭЭЩ://ааа.ТЮМЧrОНХТsЭ.ШrР>. DШаЧloaded on 22.10.2014. IЯКЧЭОr, E. V. & KЮгЧОЭsШЯ, O. L. (ОНs.). 2007. . ., . . ( .). ДRОН DКЭК BШШФ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТКЖ. − PОЭrШгКЯШНsФ. KКrОХТК. 368 Щ. (IЧ RЮssТКЧ). KСШФСХШЯК, T. ВЮ., AЧЭТЩТЧ, V. K. & TШФКrОЯ, P. N. 2000. . ., . ., . . ДNКЭЮrО ЩrШЭОМЭОН КrОКs ШП KКrОХТКЖ. − KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs, PОЭrШгКЯШНsФ. 300 Щ. (IЧ RЮssТКЧ). KШЛвКФШЯ, K & JКФШЯХОЯ, J. (ОНs.). 2013. AЭХКs ШП СТРС МШЧsОrЯКЭТШЧ ЯКХЮО КrОКs, КЧН КЧКХвsТs ШП РКЩs КЧН rОЩrОsОЧЭКЭТЯОЧОss ШП ЭСО ЩrШЭОМЭОН КrОК ЧОЭаШrФ ТЧ ЧШrЭСаОsЭ RЮssТК: ArФСКЧРОХsФ,VШХШРНК, LОЧТЧРrКН, КЧН MЮrЦКЧsФ RОРТШЧs, RОЩЮЛХТМ ШП KКrОХТК, КЧН CТЭв ШП SЭ. PОЭОrsЛЮrР. − FТЧЧТsС EЧЯТrШЧЦОЧЭ IЧsЭТЭЮЭО. HОХsТЧФТ. 517Щ. СЭЭЩ://ааа.sвФО.i/ОЧ-US/RОsОКrМС KЮСЦШЧОЧ, A., AФsОЧШЯ, D., DШЛrвЧТЧ, D., FШssЮЦ, K., HöУОr, O., JШЧssШЧ, B-G., JЮЯШЧОЧ, S-K., KСrвsЭКХОЯК, J., LТЧНСШХЦ, T., MКФsТЦШЯ, D., PОЭrШЯ, V., SСТЛОФШ, V., SШЛШХОЯ, N., SЮЭФКТЭТs, O. & TвЮЩОЧФШ, T. 2013: BКrОЧЭs PrШЭОМЭОН ArОК NОаШrФ. RОМШЦЦОЧНКЭТШЧs ПШr sЭrОЧРЭСОЧТЧР ЭСО PrШЭОМЭОН КrО NОЭаШrФ ТЧ ЭСО BКrОЧЭs RОРТШЧ - BPAN ЩШХТМв ЛrТОП. 4 ЩЩ. FТЧЧТsС EЧЯТrШЧЦОЧЭ IЧsЭТЭЮЭО. LКЯrШЯК, N. B., DОЦТНШЯ, I. N., SЩТrТНШЧШЯ . ., GОrЦКЧ K. E., & MОХЧТФШЯ I. V. 2007. . ., . ., . ., . ., . . ДOЧ ЭСО ЛОРТЧЧТЧР ШП КРrТМЮХЭЮrО ТЧ ЭСО ЧШrЭСОrЧ LКФО OЧОРК КrОК. PКХвЧШХШРТМКХ НКЭКЖ. − IЧ: GОШХШРв КЧН МШЦЦОrМТКХ ЦТЧОrКХs ШП KКrОХТК. IssЮО 10. PОЭrШгКЯШНsФ. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. P. 194-206. (IЧ RЮssТКЧ). NШrНТЧ, I. 1972. CКХШЩХКМК, sОМЭ. GКsЩКrrТЧТК ТЧ NШrНОЮrШЩК. − TКбШЧШЦТsФК ШМС ОФШХШРТsФК SЭЮНТОr. UЩsКХК, 184 Щ. NШrrХТЧ, J. P. 1871: FХШrК KКrОХТКО ШЧОРОЧsТs. PКrs I. − NШЭТsОr Юr SтХХsФКЩОЭs ЩrШ FКЮЧК ОЭ FХШrК FОЧЧТМК FörСКЧНХТЧРКr. 12: 1–183. NШrrХТЧ, J. P. 1876: FХШrК KКrОХТКО ШЧОРОЧsТs. PКrs II. LТМСОЧОs. − MОННОХКЧНОЧ. SШМТОЭКЭТs FКЮЧК FХШrК FОЧЧТМК (1): 146 PШЩЩТЮs, B. 1899. FörЭОМФЧТЧР öПЯОr RвsФК KКrОХОЧs CШХОШЩЭОrК. − AМЭК SШМТОЭКЭТs ЩrШ FКЮЧК ОЭ FХШrК FОЧЧТМК 34 (9):1-59. RКЦОЧsФКвК, M. L. 1983. . . ДAЧКХвsТs ШП lШrК ШП ЭСО MЮrЦКЧsФ PrШЯТЧМО КЧН KКrОХТКЖ. − LОЧТЧРrКН. 216 Щ. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 15 RКssТ, P., HвЯтrТЧОЧ, E., JЮsХцЧ, A. & MКЧЧОrФШsФТ, I. (ОНs.) 2010. TСО 2010 RОН LТsЭ ШП FТЧЧТsС SЩОМТОs. ВЦЩтrТsЭöЦТЧТsЭОrТö & SЮШЦОЧ вЦЩтrТsЭöФОsФЮs. HОХsТЧФТ. 685 Щ. RОН DКЭК BШШФ ШП EЮrШЩОКЧ BrвШЩСвЭОs. 1995. – TrШЧНСОТЦ. 291 Щ. RОРЮХКЭТШЧ 2014. . 7 2014 № 88- . 6 2007 № 102. . . ДRОРЮХКЭТШЧ ШП ЭСО GШЯОrЧЦОЧЭ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК 07.04.2014, №88-P. OЧ ЭСО МСКЧРОs ЭШ ЭСО RОРЮХКЭТШЧ ШП GШЯОrЧЦОЧЭ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК 06 .07.2007 № 102- . PОЭrШгКЯШНsФЖ. (IЧ RЮssТКЧ). СЭЭЩ://РШЯ.ФКrОХТК.rЮ/LОРТsХКЭТШЧ/ХКаЛКsО.СЭЦХ?ХТН=11393 SМСОЦО (2012). К , 06.07.2007 № 102- . . . ДSМСОЦО ШП SЩКЭТКХ ЩХКЧЧТЧР ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК. 06.07.2007 № 102- . PОЭrШгКЯШНsФЖ. (IЧ RЮssТКЧ). СЭЭЩ://ааа.РШЯ.ФКrОХТК.rЮ/PШаОr/CШЦЦТЭЭОО/BЮТХН/PХКЧ/ SPOK NGO 2013 , « » ДDШМЮЦОЧЭКЭТШЧ ШП ЭСО МШЦЩХОб ОМШХШРТМКХ ТЧЯОЧЭШrв УЮsЭТПвТЧР ОsЭКЛХТsСЦОЧЭ ШП ЭСО ГКШЧОгСsФв sЭКЭО ЧКЭЮrО ЩКrФЖ. − PОЭrШгКЯШНsФ.108Щ. (IЧ RЮssТКЧ). TrЮЭЧОЯ JЮ. P. ОЭ КХ. (ОНs.). 2008. . . . ( .). ( ). ДRОН DКЭК BШШФ ШП RЮssТКЧ FОНОrКЭТШЧ (ЩХКЧЭs КЧН ПЮЧРТ)Ж. − AsЭrОХ. MШsМШа. 855 Щ. (IЧ RЮssТКЧ). СЭЭЩ://ЛТШНКЭ.rЮ/НЛ/rЛЩ/ТЧНОб.СЭЦ ГСЮrКЯХОЯ, A. I. & OriЧsФв, S. N. 1993. ., . . . ДГКШЧОгСвОЖ. − KТгСsФв VОsЭЧТФ 2. PОЭrШгКЯШНsФ. 217 Щ. (IЧ RЮssТКЧ). 16 Reports of the Finnish Environment Institute 40 | 2014 1 Geology and physical geography of Zaonezhye Peninsula area 1.1 Geological description of Zaonezhye Peninsula Anatoly I. Golubev*, Dmitry V. Rychanchik*, Alexander E. Romashkin* and Alexander K. Polin* *Institute of Geology of Karelian Research Center of Russian Academy of Sciences, 11 Pushkinskaya St., 185610 Petrozavodsk, Karelia, Russia Corresponding author: Alexander E. Romashkin E-mail: roma@krc.karelia.ru Introduction Geologically, Zaonezhye Peninsula is located in the centre of the synclinorial Paleoproterozoic1 Onega structure, which is referred to by some authors as the Onega trough. It is conined to southeastern Fennoscandian Shield and rests on an Archean2 granite gneiss basement. The basement rocks on the peninsula are not exposed. Most of the igneous (effusive and intrusive) and sedimentary rocks (sandstone, siltstone, argillite and carbonate) of the bedrock were formed between 2300–1800 Ma. In the regional Paleoproterozoic stratigraphy these rocks are situated in the Jatulian (2300 – 2100 Ma), Ludicovian (2100 – 1920 Ma) and Kalevian (1920 – 1800 Ma) superhorizons. The positions of the Zaonezhye Peninsula bedrocks in the stratigraphic column of Karelia are shown in Figure 1. The relief of Zaonezhye Peninsula is affected by a system of predominantly NW-trending faults. (Lake Onega bays are also elongated NW.) The area is formed of a series of gently dipping synclines3, separated by narrow anticlines4 with steeply dipping limbs. These have resulted in seven different zones of folding and faulting zones on the Peninsula (Bulavin 1999), also described as linear anticlinal uplifts with longitudinal folds and faults (Fig. 2). The Paleoproterozoic geological and tectonic structure of the area as well as the types and chemical and mineral composition of its bedrocks are described in detail in literature (Glushanin et al. 2011, Reading… 2013) and are discussed briely below. 1 Paleoproterozoic – a period in the Earth’s evolution 2.5 to 1.6 Ga; rocks that formed at that time 2 Archean – a period in the Earth’s evolution older than 2.5 Ga; rocks that formed at that time 3 Syncline – a fold of which the core contains stratigraphically younger rocks; generally concave upward 4 Anticline – a fold, generally convex upward, whose core contains stratigraphically older rocks Reports of the Finnish Environment Institute 40 | 2014 17 Thickness, m Horizon Superhorizon Eonothema Acrothem Absolute age, Ma Sandstone, quartzitic sandstone, siltstone, schist, conglomerates, conglobreccia. Basic sills and lava. 1500 Vepsian 1650 Interbedding of graywacke sandstone, siltstone and carbonaceous argillite with ine-pebble conglomerate interbeds. 1000 Kalevian 1800 700 Suisarian Tuffs, tufites and lava of basalt, picrobasalt and metabasalt composition. Feldspar-quartz sandstone, siltstone, krivozerite, shungite-bearing siltstone and argillite with dolomite, limestone and lydite interbeds. Basic lava and sills. 1200 TransOnega Lower (Karelian) 2100 Dolomite, marbled limestone, quartz sanstone with dolomite matrix, siltstone, schist, basalt. Onega 500 Jatulian Proterozoic Ludicovian 1920 1100 Segozerian Sandstone, quartzitic sandstone, schist, tufite, scarce carbonate rock interbeds, conglomerates and basalt. 2500 500 2400 1000 Sumian Sariolian 2300 Polymictic and granite conglomerates, arkose, graywacke, lava of andesite-basalt composition. Conglomerates, tuff conglomerates, gravelstone, arkose, quartz porphyry of dacite-rhyolite composition. Intermediate and felsic volcanic tuffs, schist, iron formations, carbonaceous and carbonate rocks, conglomerates, basalt, komatiite and andesite. 2000 Upper (Lopian) 3200 >3000 Archean Lithological composition Biotite- and epidote-biotite gneiss, amphibole and kyanite-bearing gneiss and granite gneiss. Fig. 1. General stratigraphic column of Karelia (black line indicates the position of Zaonezhye Peninsula rocks in the column). 18 Reports of the Finnish Environment Institute 40 | 2014 Sedimentary rocks. Jatulian superhorizon, Tulomozero suite. The rocks of the Jatulian superhorizon are the oldest on the Zaonezhye Peninsula.They are only exposed in the centre of the anticlines, which are aligned SE–NW. TСОв ШММЮr КХШЧР ЭСО ЧШrЭСОКsЭ sСШrО ШП ЭСО ЩОЧТЧsЮХК КЧН КrО ШММКsТШЧКХХв ОЧМШЮЧЭОrОН Кs ОХШЧРКЭОН sЭrЮМЭЮrОs КХШЧР ЭСО TКЦЛТЭsв ЯТХХКРО-LКФО PКНЦШгОrШ ХТЧО КЧН ТЧ ЭСО КrОК ЛОЭаООЧ LКФО ВКЧНШЦШгОrШ КЧН ЭСО ЯТХХКРО ШП VОХТФКвК GЮЛК. TСОsО rШМФs СКЯО КХsШ ЛООЧ rОЩШrЭОН ПrШЦ ВЮгСЧв OХОЧв IsХКЧН КЧН ЧШrЭСОrЧ ЩКrЭs ШП SЯвКЭЮФСК BКв (FТР. 2). Fig. 2. Diagram of the geological structure of Zaonezhye Peninsula (made using the maps of Sevzapgeologia (Mikhailyuk et al. 1988), and by USSR Ministry of Geology, PGO Nevskgeologia (Bulavin 1999). Reports of the Finnish Environment Institute 40 | 2014 19 20 Reports of the Finnish Environment Institute 40 | 2014 Fig. 3. Mode of occurrence of carbonate rocks, Tulomozero suite, Yuzhny Oleny Island (Photo Vladimir Makarikhin). Reports of the Finnish Environment Institute 40 | 2014 21 Fig. 4. Diagram of the geological structure of South Oleny Island (6): 1 = Quaternary sediments; 2 = red bed- dolomite unit; 3 = limestone-dolomite unit; 4 = stratigraphic boundaries; 5 = fault lines; 6 = quarry contours; 7 = mode of occurrence; 8-15 = organic residue: 8 = Klimetia, 9 = Butinella, 10 = Calevia olenica (Rjab), 11 = Stratifera ordinata Mak., 12 = oncolites, 13 = Kareliana zonata Korde, 14 = nodular stromatolites, 15 = Olenia rasus But. 22 Reports of the Finnish Environment Institute 40 | 2014 Fig. 5. Limestone kilning furnace, South Oleny Island (Photo Vladimir Makarikhin). Fig. 6. Carbonate pseudomorphs after gypsum, core sample from the Onega Parametric Borehole. The sample is about 8 cm wide. At this level the rocks are dominated by partly marbled dolomite interbedded with limestone, sandstone, phyllite and carbonate breccia. Carbonate rocks contain relics of biogenic stromatolites produced by the vital activity of lower organisms, mainly cyanobacteria, and occur now as carbonate or, occasionally, secondarily siliciied deposits with different forms of internal layering. A distinctive feature of the rocks that occur in this part of the geological column is the anomalously heavy isotope composition of carbonate carbon δ13 (+10 – +18‰, while the isotope composition of carbon in both old and modern carbonates is commonly about 0‰). It should be noted that this anomaly is considered global and carbonates of similar age, displaying the same anomalous isotope composition of carbon, have been reported from several regions of the earth (Melezhik et al. 2005, Melezhik et al. 2010, Reading…2013). The largest exposures of Tulomozero carbonate rock can be found on South Oleny Island (with the area of 0.7x2.5 km), which lies 12 km east of Kizhi Island. It is a unique area of geological and archaeological signiicance (Makarikhin 1992) where quarries and other land use have exposed calcareous-dolomitic rocks that contain an abundance of organic fossils (stromatolites and microphytolites) dating back circa 2 Ga. The carbonate rock deposits are up to 70 m thick, dipping SW and making up the Reports of the Finnish Environment Institute 40 | 2014 23 limb of the NW-trending anticline. In the limb, rocks exhibit small-scale dome-shaped folding. Limestone is commonly conined to the cores of the dome-shaped folds, whereas dolomite constitutes the fold arches. In addition, accumulated dolomite displays small-scale plication (Fig. 3). These rocks have been described in detail in several publications and geological guidebooks (Sokolov & Butin 1961). V.V. Makarikhin and G. . Kononova (1983) provide the most complete and detailed description of the organic fossils. Bedding patterns and spatial relationships of rocks and organic fossils (old algae) can be seen in the rock exposures on the northeast shore of the island and in the quarry walls in the northern and central parts of the island (Fig. 4). On the southwest shore of the island, one can learn more about limestone kilning carried out before 1956 near the Main Quarry where fragments of two furnaces, illed with raw material for kilning, and other traces of past activities have been preserved (Fig. 5). The extensive evidence obtained in the last few years shows that the rocks of the Tulomozero suite were formed in an evaporative environment (in a hot, dry climate). Examples include carbonate pseudomorphs, lesser talc and quartz pseudomorphs after gypsum, nodular and cloud-like (chicken-wire) deposits typical of gypsum aggregates (Fig. 6), carbonate beds after gypsum deformed locally by the volumetric effects of gypsum-anhydrite transitions and scarce pseudomorphs5 after cubic and skeletal halite (rock salt) crystals. Carbonate breccia, which often occurs in this layer, has some features indicating that they have been produced as a result of collapsed salt karst (Melezhik et al. 2005). Fig. 7. Rock salt (halite) with anhydrite inclusions (light and grey). Core sample from the Onega Parametric Borehole. The sample is about 5 cm wide. Fig. 8. Brecciated krivozerites. Lower Zaonezhye subsuite, Svyatukha Bay of Lake Onega (Photo Vladimir Makarikhin). 5 PsОЮНШЦШrЩС Тs К ЦТЧОrКХ аСШsО ШЮЭаКrН МrвsЭКХ ПШrЦ Тs ЭСКЭ ШП КЧШЭСОr ЦТЧОrКХ sЩОМТОs; К ЩsОЮНШЦШrЩС Тs НОsМrТЛОН Кs ЛОТЧР КПЭОr ЭСО ЦТЧОrКХ аСШsО ШЮЭаКrН ПШrЦ ТЭ СКs, О.Р. ХТЦШЧТЭО КПЭОr ЩвrТЭО, qЮКrЭг КПЭОr lЮШrТЭО, etc.). 24 Reports of the Finnish Environment Institute 40 | 2014 Fig. 9. Krivozerite of the Lower Zaonezhye subsuite, core sample from the Onega Parametric Borehole. The sample is about 8 cm wide. Fig. 10. Brecciated maksovite, Berezovets Island (Photo Vladimir Makarikhin). Fig. 11. Maksovite pebble beach, Berezovets Island (Photo Vladimir Makarikhin). Reports of the Finnish Environment Institute 40 | 2014 25 Fig. 12. Anthraxolite, village of Shunga. The sample is about 6 cm long. Geomorphology and Quaternary deposits of Zaonezhye At this level the rocks are dominated by partly marbled dolomite interbedded with limestone, sandstone, phyllite and carbonate breccia. Carbonate rocks contain relics of biogenic stromatolites produced by the vital activity of lower organisms, mainly cyanobacteria, and occur now as carbonate or, occasionally, secondarily siliciied deposits with different forms of internal layering. A distinctive feature of the rocks that occur in this part of the geological column is the anomalously heavy isotope composition of carbonate carbon δ13C (+10 – +18‰, while the isotope composition of carbon in both old and modern carbonates is commonly about 0‰). It should be noted that this anomaly is considered global and carbonates of similar age, displaying the same anomalous isotope composition of carbon, have been reported from several regions of the earth (Melezhik et al. 2005, Melezhik et al. 2010, Reading…2013). The largest exposures of Tulomozero carbonate rock can be found on South Oleny Island (with the area of 0.7x2.5 km), which lies 12 km east of Kizhi Island. It is a unique area of geological and archaeological signiicance (Makarikhin 1992) where quarries and other land use have exposed calcareous-dolomitic rocks that contain an abundance of organic fossils (stromatolites and microphytolites) dating back circa 2 Ga. The carbonate rock deposits are up to 70 m thick, dipping SW and making up the limb of the NW-trending anticline. In the limb, rocks exhibit small-scale dome-shaped folding. Limestone is commonly conined to the cores of the dome-shaped folds, whereas dolomite constitutes the fold arches. In addition, accumulated dolomite displays small-scale plication (Fig. 3). These rocks have been described in detail in several publications and geological guidebooks (Sokolov & Butin 1961). V.V. Makarikhin and G.M. Kononova (1983) provide the most complete and detailed description of the organic fossils. Bedding patterns and spatial relationships of rocks and organic fossils (old algae) can be seen in the rock exposures on the northeast shore of the island and in the quarry walls in the northern and central parts of the island (Fig. 4). On the southwest shore of the island, one can learn more about limestone kilning carried out before 1956 near the Main Quarry where fragments of two furnaces, illed with raw material for kilning, and other traces of past activities have been preserved (Fig. 5). 26 Reports of the Finnish Environment Institute 40 | 2014 The extensive evidence obtained in the last few years shows that the rocks of the Tulomozero suite were formed in an evaporative environment (in a hot, dry climate). Examples include carbonate pseudomorphs, lesser talc and quartz pseudomorphs after gypsum, nodular and cloud-like (chicken-wire) deposits typical of gypsum aggregates (Fig. 6), carbonate beds after gypsum deformed locally by the volumetric effects of gypsum-anhydrite transitions and scarce pseudomorphs6 after cubic and skeletal halite (rock salt) crystals. Carbonate breccia, which often occurs in this layer, has some features indicating that they have been produced as a result of collapsed salt karst (Melezhik et al. 2005). The presence of salt-bearing and sulphate beds in this part of the column is indicated by the so-called “grandfather’s salt pits”, located two kilometres north of Velikaya Guba. Salt-rich water accumulates in these man-made pits, which are about 2x2 m in size. Slightly altered sulphate and salt rock beds have been found also at a depth of 2.5-3 km during the drilling of the Onega parametric hole near Ulitina Novinka, Kondopoga District, west of the Onega Peninsula (Fig. 7). Ludicovian superhorizon, Trans-Onega suite. On the Zaonezhye Peninsula the Trans-Onega suite consists of exposed sedimentary, volcanic-sedimentary and volcanogenic rocks. A characteristic feature of these rocks is the presence, from several percent to dozens of percent, of organic matter (shungite) (Filippov et al. 2007). These exposures are conined to the limbs of the anticlines. The Trans-Onega suite falls into two subsuites, lower and upper, that differ in their mineralogical composition. Rocks of the lower subsuite occur as narrow bands in the northern and southern parts of the peninsula. These bands consist of sandstone, siltstone and argillite interbedded with arenaceous dolomite. In the lower subsuite horizontal bedding is predominant. Occasionally, siltstone and argillite interbeds contain up to 3% (mass) of organic matter. The lower subsuite is characterized by the presence of clay-carbonate and carbonate-clay (marl) rocks with distinctive microrhythmic lamination often referred to in literature as krivozerite (Fig. 8, 9). They occur in all known examples of the lower subsuite of the Zaonezhye suite and can be used as a good marker horizon. In Zaonezhye, he upper subsuite rocks are far more common than the lower subsuite rocks. However, they are also conined to the limbs of NW-trending anticlines. All the rocks in this subsuite are enriched in various amounts of organic matter (shungite) and are therefore dark gray or black. Their organic matter content varies from less than 1 per cent to 70% (mass). The subsuite consists of dark-gray and black tuffaceous-sedimentary and sedimentary rocks bearing sand-, silt- and pelite-sized shungite with carbonate interbeds and predominantly dolomite lenses, often including disseminated sulphide. Also, lenticular, dome-shaped structures with elevated carbon concentrations (at least 20% mass) are encountered in this part of the geological column (Melezhik et al. 2004). This type of rock, often referred to in literature as maksovite (Fig. 10, 11), is now being querried near the Tolvuya in northeastern Zaonezhye Peninsula. It is used predominantly as a substitute for metallurgic coke but is also commonly used in medicine and as an absorbent in water-puriication ilters (Filippov et al. 2007). The rock horizon, referred to in literature as the shungite-lydite-dolomite complex, is well deined in this part of the column of the Paleoproterozoic Onega structure (Melezhik et al. 2009). It is formed of alternating dolomite, lydite and shungite-bearing rock beds (lenses). Dolomite commonly contains organic matter between crystals and within the cores of rhomboid grains. Lydite is a hard dark-gray to black cherty 6 Pseudomorph is a mineral whose outward crystal form is that of another mineral species; a pseudomorph is described as being after the mineral whose outward form it has, e.g. limonite after pyrite, quartz after luorite, etc.). Reports of the Finnish Environment Institute 40 | 2014 27 rock that contains 1-5% (mass) organic matter. There have been attempts to use these rocks as touchstone7, but they have been found too fractured and brecciated. The shungite-lydite-dolomite complex also contains veins of metamorphosed natural bitumens known as anthraxolite (Fig. 12, 13). Practically all the lithotypes of sedimentary rocks in this layer of the column contain fossiled organic remnants such as carbonate rocks – Litophyta (stromatolites and microphytolites); terrigenous, mainly pelite-sized rocks known as acrotarchs; cherty rocks such as styriolite and microfossils; and shungite-bearing rocks termed chemofossils (Makarikhin & Kononova 1983). Kalevian superhorizon, Kondopoga suite. These bedrock exposures cover a large area of up to 10 km wide bands of synclines with gently dipping limbs, extending from southeast to northwest. The column of the Kondopoga suite is a lyschoid sequence in which terrigenous rocks of different particle sizes and mineral compositions (conglomerates, gravelstone, sandstone, siltstone and argillite) are interbedded monotonically to form rhythms, varying from several centimetres to tens of metres in thickness, that are dominated by sedimentary rocks of different particle sizes. Occationally, also thin carbonate intercalations, lenses and concretions are encountered. Conglomerates are conined to the base of the elementary rhythms and occur more in the lower part and less in the upper part of the Kondopoga suite. Sandstones are divided into greywacke and polymictic types, depending on their composition. These stones are light gray to dark gray in colour and display parallel, horizontal and minor undulating cross-bedding. Siltstones are predominantly dark gray to black. The incorporated clasts consist of quartz, feldspar, ine-grained chlorite aggregates and lesser carbonates. Argillites are dark gray to black in colour, with a brownish shade, and they are commonly interbedded with siltstone. Like siltstones, argillites display well-deined horizontal and parallel bedding. Also diastems8, current folds and intrastratal faults are occasionally encountered. Rocks of the Kondopoga suite are characterized by the presence of organic matter (several per cent), which imparts a dark colour to the terrigenous sedimentary rocks (Fig. 14). The suite also contains lens-shaped (oblate) anthraxolite9 aggregates up to dozens of centimeters in diameter and up to 5 cm in thickness. Cyanobacterial (Cyathotes nigoserica Mak.) buildups in terrigenous rocks have been found in the carbonaceous siltstone of the Kondopoga suite. These buildups are morphologically similar to mud cracks and current ripple marks, although different in other features (Makarikhin & Kononova 1983). Kalevian superhorizon, Munozero suite. In the central part of the study area, near Lake Munozero, the bedrock of the Munozero suite is exposed. This is the core of the Munozero syncline. The lower part of the suite consists of dark-gray clastic limestone with thin siltstone and argillite intercalations. The calcite content of these rocks varies from 30 to 80%. The upper portion of the suite contains gray arenaceous dolomite with chert intercalations, siltstone, quartz-feldspathic sandstone with carbonate matrix and arkose. Dolomite commonly displays ine undulation and oblique lamination. Microphytolites of the genus Glebosites (Reitl.) have been found in limestone and oncolites of the genus Osagia (Twenh.) have been reported from dolomite (Makarikhin & Kononova 1983). 7 Touchstone – a black, linty stone, such as a siliciied shale or slate, whose smooth surface was formerly used in testing the purity or ineness of alloys of gold and silver by comparing the streaks left on the stone by rubbing with the metal with the streaks left by an alloy of predetermined composition. 8 Diastem – a relatively short interruption in sedimentation, with little or no erosion before deposition is resumed 9 Anthraxolite – natural bitumen at the metaanthracite stage of coaliication 28 Reports of the Finnish Environment Institute 40 | 2014 Igneous rocks, mineralogeny and commercial minerals of Zaonezhye Peninsula On Zaonezhye Peninsula volcanic rocks can be found in numerous basaltic lava lows and sheets. These dark-gray rocks were produced by volcanic activity (Fig. 15, 16). As a result of paleovolcanological studies of Zaonezhye, areas subjected to the most active volcanism have been identiied and described. Lava lows, varying from 5–7 m to 35–40 m in thickness, are divided into ine-grained varieties at the base, medium- and coarse-grained varieties at the centre and ine-to medium-grained amygdaloidal varieties at the top. Rocks in these lava lows are fairly homogeneous in their petrographic composition, texture and structure. Predominantly, basalts consist of ine plagioclase laths and isomorphic tabular pyroxene in strongly chloritized matrix. Commonly the amygdales are illed with chlorite, lesser quartzite and quartz. Flow bedding at the top of lava lows is characterized by an abundance of chlorite and chlorite-calcite amygdales, extending as “layers” for dozens of metres along the strike. Ore minerals are represented by pyrite and leucoxenized titanomagnetite and lesser chalcopyrite. Brecciation is occasionally observed at the top of the lava low; hydrothermal quartz-calcite veins and veinlets evolve in these zones. Due to the highly hematized (oxidized) lava in the area, the colour of its rocks is often brown. Gabbro-dolerite sills represent sub-volcanic rocks. In composition these rocks are identical to lava deposits but differ in their degree of recrystallization and, hence, structure (Golubev & Svetov 1983). Gabbro-dolerite sills form at least 40–45 m thick structures with distinct crystallization, from ine-grained varieties at the margins to coarse-grained and occasionally pegmatoid varieties at the centre of the structure. The rocks are dark gray to brown in colour and fairly dense, often forming a conspicuous relief of high scarps or ridges. They are easily traceable for dozens of kilometres along the strike, folding together with host rocks. The volcanic breccia on Radkolye Point in the Zaonezhye Peninsula is fairly exotic. The relics of the Radkolye volcanic ediice were mapped in 1972 during paleovolcanological studies on the southwestern shore of Bolshoi Lelikovsky Island (Svetov & Golubev 1978). Due to erosion, only a small portion of the volcanic neck is preserved. Eruptive channel rocks can be found in rocky scarps at its northeastern and southern endocontacts, while its entire western and northern parts are under the Lake Onega water level. The preserved part of the volcanic neck is described as a rocky, two-peaked roches moutonnée created by the glacier. It is 8–10 m higher than the surrounding rocks (Fig. 17). Morphologically, the volcanic neck is a round body, presumably about 200 m in diameter. The base of the volcanic structure on Radkolye Point consists of volcanogenic sedimentary-effusive rocks of the Zaonezhye volcanic complex. It forms a gently dipping syncline with a well-exposed northeastern limb that extends along the southwestern shore of the island. On the island the volcanogenic structure forms a series of narrow and gently dipping anticlines and synclines elongated towards northwest. In southeastern parts of the island, effusive rocks are crosscut by coarse- to medium-grained gabbro-dolorite sill that forms a sheeted body, folded with host rocks. The fold axes generally plunge northwest. Direct contacts between the neck and the host rocks of the Zaonezhye suite have only been reported from its southern parts, while in the rest of the area the contact zone is buried under deluvial piles of rocks and unconsolidated Quaternary sediments. Near the water’s edge, in the steep scarp located in the southern endocontact zone, vertically dipping eruptive breccia cuts gently dipping basaltic lava. The rough contact surface can be traced for over several metres. In both cases, the contact plane dips steeply north to northwest at about 80–85º. Reports of the Finnish Environment Institute 40 | 2014 29 Coarse clastic rocks, morphologically similar to the eruptive breccia described above, have been encountered 3.5 km northwest of Point Radkolye, on one of nameless islands of the Lambinskie Islands. The various rocks of the peninsula are a treasure trove for nature lovers. Semi-quantitative and quantitative spectral analyses were carried out to study minor elements and their concentrations in the mineralogical composition of the rocks. In addition these analyses determined the genesis, conditions of formation and the position of horizons where nonferrous metals may occur. All the above rock varieties contain low concentrations of ore-bearing elements, carbonate and cherty (lydite-like) rocks containing the lowest concentrations. However, certain elements are conined to certain rock varieties in certain structures, indicating geochemical specialization (Golubev et al. 1984). Ore-bearing elements of nonferrous metals are present in carbonaceous rocks mainly as sulides. Although all the rocks of the Zaonezhye suite are contaminated with sulides, ore matter is conined to second-member rocks, i.e. shungitic tufites. Depending on the metamorphic grade, ore mineralization is of the pyrite type and ore matter is either pyrite or pyrrhotite. Formation of pyrite with smaller quantities of chalcopyrite, sphalerite and pyrrhotite is characteristic of greenschist facies. Sulides occur as beds, lit-par-lit intrusions, pockets, concretions, globules, coating around rock and mineral fragments, veins and veinlets. Conditions during their formation determine the mineralization of primary sedimentary and metamorphogenetic-hydrothermal ore in mineralized schist. Spectral and chemical analyses have shown that the ores contain Zn, Ni, Co and Cu as well as smaller quantities of Ag, Mo, Pb and Au. Nonferrous metal concentrations are at least one order of magnitude higher in concretions than in host tufites with lit-par-lit ore injections. Studies of sulphide mineralization have shown that Cu, Co, Ni, Zn, Pb, Ag and Au are concentrated in secondary sulphide redistribution during epigenesis and metamorphism. Pyrrhotite mineralization is not characteristic of the carbonaceous rocks in the Onega trough. Pyrrhotite is formed when ine-grained pyrite is recrystallized into massive pyrite interbeds. It also occurs in tectonically active zones where graphite is formed instead of shungite and pyrite is replaced by pyrrhotite. Volcanic emanations during the three phases of Zaonezhye volcanism are the source of ore matter in Karelian carbonaceous rocks. The hydrothermal ield of the most active second phase of Zaonezhye volcanism has been identiied by facies and paleovolcanological reconstructions in the active submarine volcanic area of the Onega trough. In the Zaonezhye suite column, this zone consists of shungite rocks as well as overlying shungite tuffs that are most likely to contain nonferrous metals. Among other evidence, correlation between ore-forming processes and volcanic events, sheeted shapes of ore bodies, preserved primary structures of rocks and ores as well as the pattern of sulphide mineralization suggest that ore-forming processes were similar in the black shales of the Zaonezhye complex and the Baltic Shield (Golubev et al. 1984). Clearly the geochemical characteristics of the study area are affected by structural dislocation and faulting zones, to which complex Cu-U-Mo-V ore deposits are conined. These zones contain from elevated to anomalous concentrations of Cu, Co, Ni, Cr, Zn, Mo, Bi, Au, Ag, Se, Pt, Pd as well as other elements. Ore-forming processes are indicated mainly by near-fault sodium metasomatism, micatization and the above spectrum of anomalous element concentrations. Ore-forming processes are determined by axial fauls and shear zones, as well as alternating dolomite, siltstone, schist, basalt and gabbro-dolerite deposits of considerably different physical, mechanical and geochemical properties. Structural dislocation and fault zones are described in detail in A.V. Bulavin’s monograph “Metallogeny of Karelia” (Bulavin 1999). 30 Reports of the Finnish Environment Institute 40 | 2014 For commercial mining, most promising are the ore-bearing deposits associated with the formation of uranium, noble metal and vanadium in structural dislocation and faulting zones. Such deposits occur in the Kosmozero, Padma and Shulginovskoe ore ields in the Onega Ore Province of the Onega-Belozero mineralogenic zone. During the past few decades Nevskgeologia GGP has discovered vanadium-rich deposits in Srednyaya Padma, Tsarevskoe, Vesenneye, Verkhnyaya Padma and Kosmozero as well as other deposits in metasomatised rocks - the carbonaceous siltstone and schist occurring at the base of the Zaonezhye suite of the Ludicovian superhorizon. The total reserves of vanadium pentoxide in the Onega Ore Province, including prospective reserves of all deposits and occurrences, are estimated at 556 000 tons. Most of these deposits (C1+C2 resources of 332 500 tons), are concentrated in the active reserves of the Padma and Kosmozero ore ields (Bulavin 1999). Fig. 13. Anthraxolite, village of Shunga. Fig. 14. Mode of occurrence of Kondopoga suite rocks, Nigozero quarry (Photo Vladimir Makarikhin). Reports of the Finnish Environment Institute 40 | 2014 31 Fig. 15. Contact between globular-pillow lava (above) and silty sandstone (below). Lambas-Ruchei (Photo Vladimir Makarikhin). Fig. 16. Globular-pillow unit in lava, Lambas-Ruchei (Photo Vladimir Makarikhin). 32 Reports of the Finnish Environment Institute 40 | 2014 Fig. 17. Diagram of the geological structure of the Radkoila volcanic ediice (14): 1 = plagioclase-pyroxene basalt dykes; 2 = eruptive breccia; 3 = globular-pillow basalt lava; 4 = basalt lava-breccia; 5 = amygdaloidal basalt; 6 = massive chilled basalt; 7 = cluster of amygdales in basalt lows; 8 = tuff siltstone and tuffaceous siliceous schist; 9 = tuffaceous sandstone; 10 = low direction; 11 = mode of occurrence (a – bedding, b – jointing); 12 = dominant exposure contours; 13 = geologic boundaries (a – assumed, b – traced); 14 = cliff scarps; 15 = sulphide mineralization zones. Reports of the Finnish Environment Institute 40 | 2014 33 REFERENCES BЮХКЯТЧ, .V. 1999. . . . CШЦЩХОб МШЩЩОr-ЮrКЧТЮЦ-ЦШХвЛНОЧЮЦ-ЯКЧКНТЮЦ ШrО ПШrЦКЭТШЧ ТЧ ЭСО ПШХНТЧР-КЧН-ПКЮХЭТЧР гШЧОs ШП ЭСО OЧОРК sЭrЮМЭЮrОЖ. − MОЭКХХШРОЧв ШП KКrОХТК. PОЭrШгКЯШНsФ. Щ. 246–261. (IЧ RЮssТКЧ). GХЮsСКЧТЧ, L.V., SСКrШЯ, N.V. & SСМСТЩЭsШЯ, V.V. (ОНs.), 2011. . ., . ., . . ( . ). ( , , ) ДPКХОШЩrШЭОrШгШТМ OЧОРК sЭrЮМЭЮrО (РОШХШРв, ЭОМЭШЧТМs, НООЩ sЭrЮМЭЮrО КЧН ЦТЧОrКХШРОЧвЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 431 Щ. (IЧ RЮssТКЧ). GШХЮЛОЯ, .I., AФСЦОНШЯ, . ., & GКХНШЛТЧК, L.P. 1984. . ., . ., . . . ДGОШМСОЦТsЭrв ШП ЭСО LШаОr PrШЭОrШгШТМ ЛХКМФ sСКХО МШЦЩХОбОs ТЧ ЭСО KКrОХТК-KШХК rОРТШЧЖ. – LОЧТЧРrКН. 192 Щ. (IЧ RЮssТКЧ). GШХЮЛОЯ, .I. & SЯОЭШЯ, A.P. 1983. . ., . . . ДGОШМСОЦТsЭrв ШП ЛКsКХЭs ЩrШНЮМОН Лв ЩХКЭПШrЦ ЯШХМКЧТsЦ ТЧ KКrОХТКЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 191 Щ. (IЧ RЮssТКЧ). FТХТЩЩШЯ, M.M. ОЭ КХ. (ОНs.), 2007. . . . ( .). ). ДAЭХКs ШП ЭСО sСЮЧРТЭО-ЛОКrТЧР rШМФ ЭОбЭЮrОs КЧН sЭrЮМЭЮrОs ШП ЭСО OЧОРК sвЧМХТЧШrТЮЦЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 80 Щ. (IЧ RЮssТКЧ). MКФКrТФСТЧ, V.V. 1992. . . . ДSТЭОs ШП РОШХШРТМКХ sТРЧТiМКЧМОЖ. – IЧ: GОШХШРв КЧН ЩrШЭОМЭТШЧ ШП ЦТЧОrКХ rОsШЮrМОs ТЧ KКrОХТК. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ, Щ. 60–98. (IЧ RЮssТКЧ). MКФКrТФСТЧ, V.V. & KШЧШЧШЯК, G. . 1979. . ., . . . ДLШаОr PrШЭОrШгШТМ ЩСвЭШХТЭОs ШП KКrОХТК. –LОЧТЧРrКН. 208 Щ. (IЧ RЮssТКЧ). MОХОгСТФ, V. A., FТХТЩЩШЯ, M. M. & RШЦКsСФТЧ A. E. 2004. A РТКЧЭ PКХКОШЩrШЭОrШгШТМ НОЩШsТЭ ШП sСЮЧРТЭО ТЧ NА RЮssТК. − OrО РОШХШРв rОЯТОаs 24: 135–154. MОХОгСТФ,V.A., FКХХТМФ, A.E., FТХТЩЩШЯ, M.M., LОЩХКЧН, A., RвМСКЧМСТФ, D.V., DОТЧОs, ВЮ.E., MОНЯОНОЯ, P.V., RШЦКsСФТЧ, A.E. & SЭrКЮss, H. 2009. PОЭrШХОЮЦ sЮrПКМО ШТХ sООЩs ПrШЦ К PКХКОШЩrШЭОrШгШТМ ЩОЭrТiОН РТКЧЭ ШТХiОХН. − TОrrК NШЯК 21: 119–126. MОХОгСТФ, V.A., FКХХТМФ, A.E., RвМСКЧМСТФ, D.V. & KЮгЧОЭsШЯ, A.B. 2005. PКХКОШЩrШЭОrШгШТМ ОЯКЩШrТЭОs ТЧ FОЧЧШsМКЧНТК: ТЦЩХТМКЭТШЧs ПШr sОКаКЭОr sЮХЩСКЭО, ЭСО rТsО ШП КЭЦШsЩСОrТМ ШбвРОЧ КЧН ХШМКХ КЦЩХТiМКЭТШЧ ШП ЭСО δ13C ОбМЮrsТШЧ . − TОrrК NШЯК 17 (2): 141–148. MОХОгСТФ, V.A., HЮСЦК, H., CШЧНШЧ, D.J., FКХХТМФ, A.E. & АСТЭОСШЮsО, M.J. 2007. TОЦЩШrКХ МШЧsЭrКТЧЭs ШЧ ЭСО PКХОШЩrШЭОrШгШТМ LШЦКРЮЧНТ-JКЭЮХТ МКrЛШЧ ТsШЭШЩТМ ОЯОЧЭ. − GОШХШРв 35: 655–658. MОХОгСТФ, V., LОЩХКЧН, A., RШЦКsСФТ,Ч A., RвМСКЧМСТФ, D., MОsХТ, M., FТЧЧО, T. E. & CШЧгО, R. 2010. TСО GrОКЭ OбТНКЭТШЧ EЯОЧЭ RОМШrНОН ТЧ PКХОШЩrШЭОrШгШТМ RШМФs ПrШЦ FОЧЧШsМКЧНТК. − SМТОЧЭТiМ DrТХХТЧР 9: 23–29. MТФСКТХвЮФ, . . ОЭ КХ. 1988. 1:200 000 МШЦЩШsТЭО ЦКЩ ШП ЭСО OЧОРК sЭrЮМЭЮrО. − 1984–1987 rОЩШrЭ ШЧ PrШУОМЭ -12–48. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ, SСКrШЯ, N.V. & SСМСТЩЭsШЯ, V.V. (ОНs.), KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. – PОЭrШгКЯШНsФ 431 Щ. (IЧ RЮssТКЧ). RОКНТЧР ЭСО ArМСТЯО ШП EКrЭС’s OбвРОЧКЭТШЧ. 2013. VШХЮЦО 3: GХШЛКХ ОЯОЧЭs КЧН ЭСО FОЧЧШsМКЧНТКЧ ArМЭТМ RЮssТК – DrТХХТЧР EКrХв EКrЭС PrШУОМЭ. – IЧ: MОХОгСТФ, V.A., KЮЦЩ, L.R., FКХХТМФ, A.E., SЭrКЮss, H. HКЧsФТ, E.J., PrКЯО, A.R. & LОЩХКЧН, A. (ОНs.), SОrТОs: FrШЧЭТОrs ТЧ EКrЭС SМТОЧМОs. SЩrТЧРОr, HОТНОХЛОrР. Щ. 1049–1552. SЯОЭШЯ, .P. КЧН GШХЮЛОЯ, .I. 1978. RКНФШТХК ЯШХМКЧТМ ОНТiМО. – IЧ: PrШЭОrШгШТМ ЯШХМКЧТМ ОНТiМОs ШП KКrОХТК. LОЧТЧРrКН. Щ. 128–132. SШФШХШЯ, V. . & BЮЭТЧ, R.V. 1961. . ., . . . ДGОШХШРТМКХ iОХН ЭrТЩ ЭШ SШЮЭС OХОЧв IsХКЧН КЧН VШХФШsЭrШЯЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ, 58 Щ. (IЧ RЮssТКЧ). 34 Reports of the Finnish Environment Institute 40 | 2014 1.2 Geomorphology and Quaternary deposits of Zaonezhye Tatyana S. Shelekhova Institute of Geology of Karelian Research Center of Russian Academy of Sciences, 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia E-mail: shelek@krc.karelia.ru Introduction The geomorphology and Quaternary deposits of Zaonezhye Peninsula have been described extensively in literature (Biske et al. 1971, Lukashov et al. 1993, Demidov & Lavrova 2000, Lukashov 2000, Demidov 2005 a,b,c, Demidov 2006, Shelekhova 2013). Zaonezhye is a unique area that has no equivalent in Karelia, or Russia. The mosaic structure of its crystalline basement and the diverse composition of its bedrock are responsible for its highly rugged topography. The unique tectonic structure of Zaonezhye, together with the multiple advances of glaciers and the distinctive evolution of the area after ice retreat gave rise to genetically and compositionally diverse Quaternary rock complexes and unique landforms – the basis for the biologically diverse landscapes of today. Precambrian crystalline rocks are covered by thin Quaternary deposits, formed from rocks carried by the last Scandinavian ice sheet during the Late Valdai glaciation (Fig. 1.). Holocene peat, lake, seismogravitational aeolian and alluvial sediments occur locally. Considerable variations in altitude (up to 100 m) are due to the alternation of narrow NW-trending selkä ridges and interridge depressions occupied by lakes, deep bays and bogs. Older Quaternary deposits may have been preserved in these depressions and, if found, should be further studied. Glacial deposits, consisting of moraine covering highly weathered and fractured Precambrian rocks, are widespread in the area. The most common glacial deposits are gabbro-dolerites, crosscut by at least 3–5 m deep fractures. Since fractured gabbro-dolerites are less resistant to glacial erosion, the resulting moraine consists of coarse local clasts. There are two types of moraine in Zaonezhye. Type I is formed of bedrocks poorly resistant to glacial exaration, such as gabbro-dolerite or slightly fractured and mildly weathered schist, occurring in a rugged relief. Coarse clasts make up 85–90% of this local moraine, produced by the destruction and short-distance redeposition of local bedrocks. The distance of glacial transport varies from hundreds of metres to several kilometers. Coarse clastic fractions (> 1 cm) account for at least 40–50%. Type II is schistose moraine, containing 25–40% of coarse clasts, composed of granite, granite-gneiss and other rock clasts. It has been transported by the glacier from the Onega-Segozero watershed and it rests on either bedrock or local coarse clastic moraine. In sand fractions, quartz dominates over feldspar. These deposits are better Reports of the Finnish Environment Institute 40 | 2014 35 sorted than the moraines of Type I. Up to 25–30% of clasts have been transported for over dozens of kilometres. The petrographic, mineralogical and chemical composition of the moraine depends completely on the mineralogical composition of the basement rock. It varies in thickness from dozens of centimeters on top of selkä ridges to 3–10 m in depressions between the selkäs. In spite of its sandy and sandy loam composition, the moraine displays poor iltrating properties. As a result, such areas are paludiied. Fluvioglacial deposits consist of well-sorted sand, gravel, pebble and sand. These deposits form esker ridges, luvioglacial deltas and debris cones that indicate the locations of major glacial meltwater systems and periglacial lakes resulting from the deglaciation of the area. Fluvioglacial deposits include 10–15 m thick deposits resting on moraine and bedrock, displaced and folded by the movements of the ice margin. Also esker ridges and abraded luvioglacial deltas occur. The mineral and petrographic composition of the luvioglacial deposits relects the bedrock and moraine from which they have been derived. Lacustrine-glacial deposits are widespread in Zaonezhye and consist of periglacial Lake Onega sediments, including seasonally accumulated varved clay and sandy-silty sediments. As a result of the melting ice sheet as well as the irregular glacial isostatic adjustment of the earth’s crust, most of Zaonezhye Peninsula was looded by the periglacial Lake Onega. During this time, water levels reached altitudes of 100–110 m in northern parts and about 80–90 m in southern parts of the peninsula. Varved clay, unaffected by the washout caused by the stadial drop in the Lake Onega water level in late and post-glacial times, is encountered in topographic lows at altitudes below 50–60 m. In some lakes, e.g. Lake Isaevo, the top of the varved clay lies at an absolute altitude of 80 m. Clay, varying from dozens of centimeters to 7–10 m in thickness, rests on moraine and is often conined to distal portions of luvioglacial deltas (Glinyanoe bog near the village of Bor Pudantsev). Continuous varved clay beds, covering an area of more than 1–2 km2, are known from southeastern shores of Lake Kosmozero, south of the village of Lambasruchei, and from the bottoms of all large lakes of Zaonezhye Peninsula. Due to its poor iltration properties and water resistance, clay contributes to the paludiicationc of the area. The mineral and chemical composition of varved clay depends on the composition of the bedrock and the overlying moraine (Demidov 2000, 2005). Lacustrine deposits, consisting of sand, loamy sand and pebble, occur on the shores of Lake Onega at an absolute altitude of 50–60 m. Lacustrine deposits form short beaches, aggradation terraces (Peski special landscape area on the southwest shore of Lake Padmozero) and beach barriers (Lambasruchei). There are also small beaches, composed of older luvioglacial sand and gravel deposits on the shores of Ladmozero, Vanchozero, Padmozero and other lakes. Sediments are accumulated at the bottom of numerous lakes and bays where glacial lacustrine varved clay is covered by a ca. 3-m-thick layer of homogeneous gray silt, followed by sapropel and sometimes diatomites. Organic deposits can be up to 7 m thick (Nizhneye Myagrozero). Also bog iron ore (limonite) has been encountered at the bottom of some lakes. Bottom sediments in lakes located near large-scale paleoseismic dislocations in bedrocks, such as Lake Putkozero and Svyatukha Bay, display folding caused by post-glacial earthquakes. Post-glacial earthquakes have also produced seismocolluvial deposits, consisting of coarse clastic talus and collapse. Seismocolluvial deposits occur on a limited scale and are conined to big cliffs of tectonic origin. Some seismic collapses are up to 100 km wide and 10 m thick, extending 2 km. Peat-bog deposits ill up paludiied interridge depressions of tectonic origin, which in the past would have formed 2–4 km long and 200–400 m wide lakes or bays with their shores. Peat-bog deposists consist of woody-grass and grass lowland peat that 36 Reports of the Finnish Environment Institute 40 | 2014 varies from several metres to over 8 m in thickness. In some lakes, grass and grassmoss bogs occur as loating mats. Aeolian deposits consist of well-sorted ine-to medium-grained sand and occur as small, narrow strips on lakeshores. As the river network is young and poorly developed, alluvial deposits consist of coarse clastic sand-pebble streambed alluvium. Geomorphology Zaonezhye has a highly diverse relief. Denudation, tectonic, glacial and luvioglacial landforms are common. Folding and faulting of crystalline rocks as well as intense neotectonic movements have affected the present-day relief of Zaonezhye. Old structural forms are responsible for the morphology and orientation of elementary surfaces. Elevated surfaces are elongated and exposed, with an orientation parallel to fold and fault structures. Multiple tectonic movements have formed a distinctive, obsequent relief in Zaonezhye. The obsequent relief is a result of the geological structure of Zaonezhye caused by wide-open synclines and narrow, heavily deformed anticlines that are interrupted by longitudinal faults. Synclines form elevated ridges and mountain massifs with relatively high plateaus, while anticlines form valleys occupied by rivers or lakes. Conined to some of the anticlines are structurally complex folding and faulting zones that host uranium-vanadium-rare metal deposits and occurrences (Bilibina et al. 1991). In parts of Zaonezhye Peninsula, individual crustal blocks have been scattered vertically along the faults as a result of neotectonic movements. Therefore, the Zaonezhye relief can be divided into three tiers: upper tier with an absolute altitude of 107–147 m; middle tier with an altitude of 60–100 m; and lower tier with an altitude of 33–60 m (Lukashov 2000). Topographically Zaonezhye can be subdivided into western and eastern parts as well as the elevated Svyatukha Bay – Lake Putkozero watershed. Western Zaonezhye is an elevated massif with a highly rugged surface. Its highest surfaces are narrow, elongated ridges. These linear ridges are 1.6–14 km long and 0.6– 1.4 km wide with 5–40 m high scarp-like slopes. Lake basins occupy piedmonts and lowlands. There is a distinctive pattern of topographic tiers: The upper tier occupies the largest area with altitudes of up to 147 m, while the middle and lower tiers form narrow strips at the rims of the elevated massif. Boundaries between these tiers consist of a series of step-like scarps and steep slopes. Western Zaonezhye is characterized by high vertical (67–101 m) and horizontal ruggedness due to the rugged shoreline of Lake Onega basins and bays. There are few river valleys, although lake basins are common. Crystalline rocks occur over a large area. There are no unconsolidated Quaternary sediments, therefore crystalline rocks are covered by a 1–2 cm layer of modern eluvium. In topographic depressions, such as the Lake Kosmozero – Unitsa Bay basin, crystalline rocks are covered by a 1.5–3 m layer of moraine. There is an esker ridge here with a delta extending northwest. Eastern parts of Zaonezhye Peninsula differ substantially from its western parts. There is no upper tier in the relief, while its middle and lower tiers form extensive structures, rather than narrow strips. In southeastern parts of the peninsula, the middle tier occupies an area of about 380 km2. Its highest surfaces are located at an absolute altitude of 60–100 m. Vertical ruggedness varies from 44 to 60 m. The middle tier consists of a plain with gently sloping lat-topped ridges without a well-deined foot of the hill. These ridges are 2.8–16.4 km long, 0.8–2.0 km wide and up to 5–15 m high. They are separated by large 1.5–2.5 km wide and 5–10 km long depressions with a lat bottom and indistinct boundaries. The lower and middle tiers cover roughly equal areas, while the lower tier is conined to the coastal zones of the peninsula. Reports of the Finnish Environment Institute 40 | 2014 37 This type of relief is most common in the northern parts of Zaonezhye Peninsula, near Padmozero and Tolvuya villages. In southern parts of Zaonezhye Peninsula, the lower tier is found near Lake Yandomozero. In general, Southern Zaonezhye is characterized by gently undulating plains with gently sloping, poorly deined ridges and bars. Watersheds are located at an absolute altitude of 60 m and vertical ruggedness is 6–18 m. The hydrographic network of eastern Zaonezhye is markedly different from western Zaonezhye. There are only two large lakes here, Putkozero and Padmozero, but river systems are more developed. Crystalline rocks of eastern Zaonezhye, unlike those of western Zaonezhye, are almost completely covered by a 6–10 m thick layer of Quaternary rocks. The middle tier is dominated by moraine, formed of boulder and loamy sand, as well as luvioglacial esker ridges and deltas, formed of sand, gravel and pebble. In the lower tier, sand, silt and clay form lacustrine-glacial and lacustrine plains. The elevated Svyatukha Bay − Lake Putkozero watershed represents a typical tectonic-denudation selkä landscape, completely lacking Quaternary deposits or covered by up to 1-m-thick moraine. The thickness of the moraine increases to at least 10 m in depressions between selkäs, where it is often covered by varved clay, glacial lacustrine loamy sand or inequigranular sand. Tectonic scarps and seismocolluvial debris cones surround western and eastern parts of the watershed. These cones are up to 2 km long chaotic piles of sharply angular blocks, which vary in size from dozens of centimeters to 5 m along the long axis (e.g. Mount Zimnyaya, Mount Gorodok, Mount Sypun and the Paltega area). Near Unitsa Bay, towards Kazhma-Velikaya Guba, the area is traversed by luvioglacial systems of esker ridges and deltas, composed of a circa 20–30 m thick layer of sand and gravel, that extend from northwest to southeast and from north to south near Padmozero-Tipinitsy and Gankovskoe-Kuzaranda. Glacial lacustrine sediments such as varved clay, loamy sand and sand occur along the shores of large lakes and in topographic depressions at absolute altitudes below 70 m. In Velikaya Guba, Yandomozero and Glinyanoe Mire near the village of Bor Pudantsev, varved clay is 6–7 m thick. Beaches, consisting of pre-Holocene luvioglacial sand and gravel deposits, stretch along the shores of Lakes Ladmozero and Vanchozero. REFERENCES BТsФО, G.S., LКФ, G.Ts., LЮФКsСШЯ, .D., GШrвЮЧШЯК, N.N. & IХвТЧ V. . 1971. . ., . ., , . ., . ., . . ДSЭrЮМЭЮrО КЧН ОЯШХЮЭТШЧ ШП LКФО OЧОРК ЛКsТЧЖ. – PОЭrШгКЯШНsФ: KКrОХТК.74 Щ. (IЧ RЮssТКЧ). DОЯвКЭШЯК, E. I. 1972. . . . ДPКХвЧШХШРТМКХ НОsМrТЩЭТШЧ ШП ЭСО UЩЩОr QЮКЭОrЧКrв НОЩШsТЭs ШП KКrОХТКЖ. – IЧ: QЮКЭОrЧКrв РОШХШРв КЧН РОШЦШrЩСШХШРв ШП ЭСО ОКsЭОrЧ BКХЭТМ SСТОХН. LОЧТЧРrКН. Щ. 59–96. (IЧ RЮssТКЧ). DОЦТНШЯ, I.N. 1993. . . . Д ЯШХЮЭТШЧ ШП РХКМТКЭТШЧ КЧН ЭСО ПШrЦКЭТШЧ ШП QЮКЭОrЧКrв НОЩШsТЭs ШЧ ЭСО ГКШЧОгСsФв PОЧТЧsЮХКЖ. – KТгСsФв ЯОsЭЧТФ.ГКШЧОгСвО 2: 13–23. (IЧ RЮssТКЧ). DОЦТНШЯ, I.N. & LКЯrШЯК, N.B. 2000. . ., . . . ДCСКrКМЭОrТsЭТМs ШП QЮКЭОrЧКrв НОЩШsТЭs КЧН QЮКЭОrЧКrв РОШХШРТМКХ ОЯШХЮЭТШЧЖ. – IЧ: IЧЯОЧЭШrв КЧН sЭЮНв ШП ЛТШНТЯОrsТЭв ШЧ ЭСО ГКШЧОгСsФв PОЧТЧsЮХК КЧН ТЧ NШrЭСОrЧ PrТХКНШгвО. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 28–40. DОЦТНШЯ, I.N., LКЯrШЯК, N.B., SСОХОФСШЯК, .S. & VКsФШ .V. 2003. . ., . ., . ., . . . ДOЧ ЭСО HШХШМОЧО lЮМЭЮКЭТШЧs ШП LКФО OЧОРКЖ. – IЧ: TСОШrОЭТМКХ КЧН КЩЩХТОН ЩrШЛХОЦs ТЧ ЦШНОrЧ ХТЦЧШХШРв. BОХКrЮs SЭКЭО UЧТЯОrsТЭв. MТЧsФ. Щ. 151–152. DОЦТНШЯ, I.N. 2004. . . . ДBШЭЭШЦ sОНТЦОЧЭs КЧН ЯКrТКЭТШЧs ТЧ LКФО OЧОРК ХОЯОХ ТЧ ЭСО LКЭО GХКМТКХ PОrТШНЖ. –IЧ:GОШХШРв КЧН ЮsОПЮХ ЦТЧОrКХs ШП KКrОХТК. IssЮО 7. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 207–218. (IЧ RЮssТКЧ). 38 Reports of the Finnish Environment Institute 40 | 2014 DОЦТНШЯ, I.N. 2005 К. . . . ДQЮКЭОrЧКrв НОЩШsТЭs ШП ГКШЧОгСвОЖ. – IЧ: EЧЯТrШЧЦОЧЭКХ ЩrШЛХОЦs ТЧ ЭСО ЦТЧТЧР ШП ЭСО SrОНЧвКвК PКНЦК НОЩШsТЭ. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 14–19. (IЧ RЮssТКЧ). DОЦТНШЯ, I.N. 2005 Л. . . . DОРrКНКЭТШЧ ШП ЭСО LКЭО VКХНКТ РХКМТКЭТШЧ ТЧ LКФО OЧОРК ЛКsТЧЖ. – IЧ: GОШХШРв КЧН ЮsОПЮХ ЦТЧОrКХs ШП KКrОХТК. IssЮО 8. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ.134–142. DОЦТНШЯ, I.N. 2005 М. . . . ДDОРrКНКЭТШЧ ШП ЭСО LКЭО VКХНКТ РХКМТКЭТШЧ ТЧ LКФО OЧОРК ЛКsТЧ. – QЮКrЭОr-2005, SвФЭвЯФКr. GОШЩrТЧЭ. Щ. 115–117. (IЧ RЮssТКЧ). DОЦТНШЯ, I.N. 2006. . . , . ДOЧ К ЦКбТЦЮЦ sЭКРО ТЧ ЭСО ОЯШХЮЭТШЧ ШП ЩОrТРХКМТКХ LКФО OЧОРК, ЯКrТКЭТШЧs ТЧ ТЭs аКЭОr ХОЯОХ КЧН РХКМТШТsШsЭКЭТМ sСШrО ЮЩХТПЭ ШП ЭСО sСШrО ТЧ ЭСО LКЭО GХКМТКХ PОrТШНЖ. – GОШХШРв КЧН ЮsОПЮХ ЦТЧОrКХs ШП KКrОХТК. IssЮО 9. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 171–182. (IЧ RЮssТКЧ). EХТЧК, G. ., LЮФКsСШЯ, .D. & ВЮrФШЯsФКвК .K. 2000. . ., . ., . . ( . ДTСО LКЭО GХКМТКХ КЧН HШХШМОЧО ТЧ EКsЭОrЧ FОЧЧШsМКЧНТК (ЩКХОШЯОРОЭКЭТШЧ КЧН ЩКХОШРОШРrКЩСвЖ. – PОЭrШгКЯШНsФ. Karelian Research Center of Russian Academy of Sciences. 242 p. GrТРШrвОЯ, S.V. & GrТЭsОЯsФКвК, G.L. 1959. , . ., . . ДA МКЭКХШРЮО ШП KКrОХТК’s ХКФОsЖ. – .-L. 239 Щ. (IЧ RЮssТКЧ). LЮФКsСШЯ, .D. & IХвТЧ, V. . 1993. . ., . . . ДRОХТОП КЧН QЮКЭОrЧКrв НОЩШsТЭs ШП ЭСО ГКШЧОгСвО PОЧТЧsЮХКЖ. – KТгСsФв ЯОsЭЧТФ. ГКШЧОгСвО. 2:23–34. (IЧ RЮssТКЧ). LЮФКsСШЯ, .D. 2000. . . . ДGОШЦШrЩСШХШРТМКХ МСКrКМЭОrТsЭТМs ШП ЭОrrТЭШrвЖ. – IЧ: IЧЯОЧЭШrв КЧН sЭЮНв ШП ЛТШНТЯОrsТЭв ШЧ ЭСО ГКШЧОгСвО PОЧТЧsЮХК КЧН ТЧ NШrЭСОrЧ PrТХКНШгСвО. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 16–28. (IЧ RЮssТКЧ). SСОХОФСШЯК, .S. 2013. . . . ДGОШЦШrЩСШХШРТМКХ МШЧНТЭТШЧs КЧН QЮКЭОrЧКrв НОЩШsТЭsЖ. – IЧ: SОХФК ХКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ Characteristics, Land Use, Conservation (Gromtsev, A.N, ed.). Karelian Research Center of Russian Academy ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 29–36. (IЧ RЮssТКЧ). SККrЧТsЭШ, M., GröЧХЮЧН, T. & EФЦКЧ, I. 1995. LКЭО GХКМТКХ ШП LКФО OЧОРК - МШЧЭrТЛЮЭТШЧ ЭШ ЭСО СТsЭШrв ШП ЭСО ОКsЭОrЧ BКХЭТМ ЛКsТЧ. – QЮКЭОrЧКrв ТЧЭОrЧКЭТШЧКХ 27:111–120. Reports of the Finnish Environment Institute 40 | 2014 39 Fig. 1. Quartenary deposits of Zaonezhye Peninsula (Demidov 2005, with minor changes). 40 Reports of the Finnish Environment Institute 40 | 2014 1.3 Hydrological characteristics of Zaonezhye Peninsula Alexander V. Litvinenko* and Maria S. Bogdanova* *Institute of Water Problems in the North of the Karelian Research Center of Russian Academy of Sciences, 50 Alexandra Nevskogo St., 185003 Petrozavodsk, Karelia, Russia Corresponding author: Alexander V. Litvinenko E-mail: litvinenko@nwpi.krc.karelia.ru, aleks-litvinenko@mail.ru Introduction The irst fragmentary information about the rivers and lakes of Zaonezhye was obtained in the 1920s and 1940s. In the early 1960s, hydrographic studies of Zaonezhye were carried out by the water problem unit of the Karelian Branch of the USSR Academy of Sciences (now the Institute of Water Problems in the North, Karelian Research Center of Russian Academy of Sciences, KarRC, RAS), including integrated ield studies and the irst cartographic analysis of the area. The results of the studies were published in the “Problems in the hydrology, limnology and water management of Karelia” (1965) and the “Catalogue of Karelia’s Lakes” (Grigoryev & Gritsevskaya 1959) as well as a hand-written catalogue of Karelia’s Rivers. Today most of this data is outdated. Morphometric information about the Zaonechye water bodies has subsequently been presented in the “Catalogue of Karelia’s Lakes and Rivers” (Filatov & Litvinenko 2001). Hydrochemical studies and bottom sediment analyses were carried out as a part of monitoring Zaonezhye lakes and rivers in 1991 and between 1999 and 2001. Nevertheless, there is little information available about water bodies in the region. Due to the lack of hydrometeorological stations on Zaonezhye Peninsula, there are no reliable data on the hydrological regimes of the rivers and lakes. Results Geological structures and the relief of the peninsula deine the distinctive hydrographic network of Zaonezhye. Alternating long, narrow ridges and long, narrow depressions characterize the topography. Nowadays Lakes and Lake Onega bays (Unitsa, Svyatukha, Lizhma, Velikaya and Keften bays) occupy these depressions (Litvinenko 2000). Practically all the basins are elongated from northwest to southeast. Zaonezhye covers an area of 1900 km2. According to inventories conducted in 1950s (Grigoryev & Gritsevskaya 1959), there are 251 lakes in Zaonezhye, covering a total area of 212 km2 (Freindling & Polyakov 1965). The ratio of total lake surface to Reports of the Finnish Environment Institute 40 | 2014 41 drainage area in Zaonezhye is about 12 %. However, recent inventories have shown even greater values. The water bodies of Zaonezhye differ considerably in their morphometric and hydrological indices. Most of them are formed by tectonic subsidence, glacial tectonics or other glacial processes (Freindling & Polyakov 1965). Water area of the water bodies varies from less than 0.01 to 30 km2. Commonly the basins are highly elongated, sometimes dozens of kilometers long and no more than several hundred metres wide. The index of elongation (ratio of length of the lake to width of the lake) can be up to 43.5 (Lake Kosmozero). Extremely elongated lakes are relatively uncommon, occurring only in northern Scotland, northwestern England (Camberland Plateau) and northwestern Central Siberia (Putoran Plateau) (Semyonov 1993). The deepest lakes in the study area are Lakes Ladmozero (52 m) and Putkozero (42 m), which form cryptodepressions, i.e. their maximum depth is below sea level (Semyonov 1993). Because the lake basins in Zaonezhye are typically small, also their watershed values (ratio of basin area to lake area) are low. A speciic watershed value describes the volume of solid, liquid and ionic runoff supplied into the water body as well as the amount of heat supplied by tributaries. Therefore it relects the effects of the watershed on all processes in the water body (Litvinenko 2000). This is a small effect, also indicated by the low water exchange index (ratio of volume of long-term average lake runoff to lake volume), which varies from one year to 10 years (Freindling & Polyakov 1965). Despite the predominantly tectonic origins of the lake basins and the complex structures of the lake bottoms, littoral zones, mainly occupied by solid sand and gravel sediments with clay lenses, are relatively well developed. Ore deposits mixed with mud are conined to deep layers (Vlasova 1965, Belkina 2005). The thermal conditions of water bodies are different. Shallow lakes are warmer during the summer months (up to 25° C) when temperatures in their bottom layers may be only 2–3°Ccolder than the surface layer, whereas deep lakes remain thermally stratiied during the summer months: their surface layer may warm up to 26° C while the bottom layer has temperatures of 8–10° C (Semyonov 1993). Apart from southeastern Zaonezhye, which is dominated by small streams, the hydrographic network is relatively uniform over the entire area. There are only few small rivers on the peninsula. According to inventories in the mid-20th century, there were 56 rivers in Zaonezhye (each over 2 km long) with a combined length of 594 km. Their lake zones were 113 km long. Small rivers and creeks (which are less than 5 km long) make up only 11% of the length and 37% of the number of the rivers. Longitudinally, most streams have a terraced proile, which is most pronounced in the rivers Kuloma, Muna, Putka and Pigmozerka (Nature park…1992). The terraces are formed of rapids, or groups of rapids, separated by deeper slow portions of the rivers. The hydrographic network of the peninsula is characterized by lake and river systems whose linear ratio of lake area length to total length of the system can be as high as 70%. The distribution of river runoff throughout the year is affected considerably by the physical and geographical characteristics of Zaonezhye, especially the high ratio of lake surface area to drainage area of the basins as well as the linear ratio of lake surface area to drainage area of the river and lake systems. As the ratio of river area to drainage area decreases, the amount of spring loods declines and the amount of runoff during low-water periods increases. Spring looding in rivers begins in the second third of April. In rivers with a high ratio of river area to drainage area, spring loods last for 70–100 days, whereas in small rivers looding continues for 50–70 days. Usually there is one peak runoff during the loods. In rivers minimum runoff occurs twice a year: during the summer-autumn and winter low-water periods. On average, the long-term minimum runoff for a 30-day period is 42 Reports of the Finnish Environment Institute 40 | 2014 over 5 l/s*km2 during the summer-autumn low-water period and 2–3 l/s km2 during the winter low-water period. It increases to 4–5 l/s*km2 in rivers with a high ratio of river area to drainage area (Surface water resources… 1972 a). The distinctive hydrochemical characteristics of Zaonezhye include elevated mineralization (occasionally up to several hundred mg/l), alkalinity and nutrient supply. There are also low concentrations of predominantly autochthonous organic substances in lakes, but high concentrations in rivers (Maslova 1965, Kharkevich 1965, Startsev 1993, Present condition…1998; Lozovik et al. 2005). The hydrographic network of Zaonezhye, including the planned Zaonezhsky landscape reserve (zakaznik) is described in more detail in Litvinenko & Bogdanova 2013. In the present paper we discuss the southeastern and southern parts of the area that have not been described previoously. We have divided the study area into four hydrographic regions (Table 1). Lakes form the basis of the hydrographic network. As shown in the 1:50 000 map below, there are 101 water bodies, covering a total area of 1007 km2, located in their entirety in the study area (Fig.1). Table 1. Suggested hydrographic regions. Hydrographic region Total lake area, km2 Ratio of lake area to drainage area, % River network density, m/km2 Number in Fig. 1 Name I Zaonezhye Peninsula 813 7.2 237 II Lel Peninsula 119 0.3 361 III Lizh Peninsula 32 9.9 81 IV Syar Peninsula 43 9.0 356 Total 1007 6.6 252 Fig. 1. Water bodies in the study area (lakes are numbered in Table 2). Reports of the Finnish Environment Institute 40 | 2014 43 Table 2. Major lakes in the study area. Number in Fig. 1 Name of the lake Lake area, km2 Number in Fig. 1 Name of the lake Lake area, km2 I. Zaonezhye Peninsula 1 44 Varezh 0.086 45 No name 0.001 2 Munozero 0.040 46 Podmalinnoye 0.012 3 Korbozero 2.000 47 Podbereznoye 0.008 4 Kalozero 0.021 48 Beloye 0.052 5 Yandomozero 30.654 49 Chernoye 0.014 6 Korytovo 0.005 50 Bolshoye Khmelozero 3.971 7 Limozero 0.625 51 Gagarye 0.007 8 Glukhoye 0.007 52 Gankovskoye 0.526 9 Palevskoye 0.454 53 Kandozero 0.129 10 No mame 0.002 54 No name 0.003 11 No name 0.002 55 Maloye Pertozero 0.029 12 Keratskoye 1.969 56 Posulskoye 0.037 13 Kalye 0.033 57 No name 0.045 14 Gahkozero 0.125 58 Shumyacho 0.005 15 No name 0.004 59 Vilozero 0.714 16 No name 0.016 60 Bolshoye Pertozero 0.870 17 No name 0.003 61 Kovshozero 0.549 18 Palozero 0.261 62 Uzkoye 0.029 19 No name 0.003 63 Podcheremush0.029 noye 20 Matveyevo 0.007 64 Verkhneye Myagozero 0.032 21 No name 0.004 65 Krivoye 0.025 22 Degtozero 0.030 66 Mokhovoye 0.020 23 No name 0.002 67 Glubokoye 0.006 0.173 24 Driskozero 0.038 68 Nizhneye Myagozero 25 No name 0.019 69 Pelekozero 0.259 26 Koryukhozero 3 0.018 70 Gizhozero 0.453 27 Shibrozero 0.232 71 No name 0.002 28 No name 0.077 72 Nikonovo 0.079 29 Kalgozero 0.008 73 No name 0.035 30 Palozero 4 0.034 74 Nizhneye Torozero 0.044 31 Savozero 0.010 75 Sredneye Torozero 0.084 32 No name 0.006 76 No name 0.062 0.156 33 Koryukhozero 2 0.082 77 Verkhneye Torozero 34 Palozero 3 0.060 78 Gahkozero 5.311 35 Maloye Khmelozero 0.250 79 No name 0.008 Reports of the Finnish Environment Institute 40 | 2014 36 Yasakovo 0.040 80 No name 0.007 37 Palozero 2 0.010 81 Chuzhmozero 6.204 38 Munozero 0.044 82 No name 0.006 39 Zimneye 0.052 83 Karasevo 0.016 40 Koryukhozero 1 0.080 84 No name 0.009 41 No name 0.007 85 No name 0.007 42 Palozero 1 0.264 86 No name 0.021 43 Kimozero 0.736 87 No name 0.014 44 No name 0.003 88 Khudoye 0.019 89 Zdvizhenskoye 0.079 II. Lel Peninsula 90 Vozhmozero 0.009 94 Rugozero 0.223 91 No name 0.004 95 Pizhei 0.054 92 Bezdonnoye 0.105 96 No name 0.003 93 No name 0.006 97 No name 0.009 III. Lizh Peninsula 98 Pivgozero 3.163 IV. Syar Peninsula 99 Syargozero 3.388 100 Maloye Syargozero 0.121 101 Tulozero 0.341 In the study area, the ratio of lake surface area to drainage area is 6.6 %, which is much lower than the average for Karelia (12 %) or the estimate for the Onega and Ladoga lake area in Karelia (21 %) (Litvinenko et al. 1998). Most of the water bodies (93%) are small or very small (lambas), covering an area of less than 1 km2. Only seven water bodies are large. The largest lakes are Chuzhmozero (6.2 km2), Gahkozero (5.3 km2), Bolshoye Khmelozero (4.0 km2), Syargozero (2.4 km2), Pivgozero (3.2 km2) and Keratskoye (2.0 km2). Lake Yandomozero is the largest lake on Zaonezhye Peninsula with a surface area of 30.1 km2. It is 11.4 km long. Its maximum width is 4.3 km and its average width is 2.6 km, whereas its maximum depth is 6.0 m and its average depth is 4.3 m. Its shoreline is 47.5 km long. The water volume of the lake is 130 M m3. The Lake Yandomozero basin is of glacial origin. Its slopes are low and gradual and its bottom is smooth. The littoral zone of the lake consists of sand and gravel, whereas brown mud is common in the central part of the bottom. The study area is ajoined by three relatively large lakes: Putkozero (surface area 21.1 km2), Kosmozero (20.6 km2) and Padmozero (10.0 km2). The southern parts of Lake Putkozero border the study area in the northeast. Lake Putkozero has a surface area of 21.1 km2. It is 24.2 km long with a maximum width of 2.1 km and an average width of 0.9 km, as well as a maximum depth of 42.0 m and an average depth of 15.6 m. The water volume of Lake Putkozero is 330 M m3 and the shoreline extends 62.4 km. The lake basin is a deep elongated depression formed by tectonic subsidence. Generally its slopes are steep or moderately steep and up to 20 m high. However, in the western parts of the lake steep slopes can be up to 40–50 m high. The lakeshores are elevated and predominantly stony, or occasionally rocky. There are 16 islands on Lake Putkozero that cover an area of 0.38 km2. The bottom of the lake has a mildly rugged relief. Underwater the slope is mostly steep. In the littoral zone, rocky or rocky and sandy ground is common, while muddy ground with small quantities of clay, sand and ore are common in the deep. Reports of the Finnish Environment Institute 40 | 2014 45 The southern parts of Lake Kosmozero adjoin the western boundary of the study area. Lake Kosmozero has a surface area of 20.6 km2. It is 30.9 km long with a maximum width of 2.1 km and an average width of 0.7 km as well as a maximum depth of 25.0 m and an average depth of 7.8 m. Its shoreline is 76.6 km long. The lake basin is also been formed by tectonic subsidence. Its slopes are 50–80 m high, steep in the west but low (15–20 m) and gradual in the east and southeast. In the north, the slopes are low and paludiied. The shores are predominantly gently sloping and their height varies. There are 10 islands on the lake that cover a total area of 0.56 km2. The bottom of the lake is rugged. A deep groove extends across the entire lake. The bottom is muddy in the deep but argillaceous or rocky in the shallow zone. Bog ore is encountered occasionally. The study area is also adjoined by the eastern shore of Lake Padmozero. The lake has a surface area of 10.0 km2. It is 10.1 km long with a maximum width of 2.0 km and an average width of 1.0 km as well as a maximum depth of 14.9 and an average depth of 4.0 m. The water volume of the lake is 40.0 M m3 and its shoreline is 24.7 km long. Glacial tectonic processes have formed the Lake Padmozero basin. Its slopes are predominantly steep. Most of the slopes are about 10 m high, althought the highest slopes are up to 20 m high. Most of the lakeshores are low and rocky, although some shores are gently sloping. The bottom of Lake Padmozero is an elongated depression with a predominantly muddy ground, apart from the sandy and muddy littoral zone. The lake is deepest in its northern parts. (Surface water resources...1972 b). In the study area, the average density of the river network is 252 m/km2, varying from 81 to 361 m/km2 in parts of the river network (Table 1). It consists of small rivers and creeks as well as short tributaries between lakes. Watersheds of major water systems are shown in Fig. 2 and their basic characteristics are described in Table 3. The largest streams are the rivers Kalei (25.9 km), Padma (24.9 km), Tambitsa (22.1 km) and Putka (21.2 km). Practically all the river basins have been affected by human activities, long-term agricultural development (1960–1980), land reclamation and clear cutting in particular. As a result, there have been changes in their water regimes. The Putka, Padma and Kalei river basins are most heavily affected, while the Tambitsa and Tsarevka river basins are least affected by human activities. 46 Reports of the Finnish Environment Institute 40 | 2014 Fig. 2. Major streams in the study area (Major river watersheds are numbered in Table 3). Table 3. Major rivers in the study area. Name of the river Number of the drainage area in Fig. 2 Limozerka I Blizhnyaya I Name of the drainage area Height of mouth, m asl Stream gradient, m/km (‰) 5.3 119.6 37 15.6 21.2 54.6 33 1.02 16.2 River mouth Lake Limozero Polevskoye 4.3 Putka Mire Polevskoye 5.4 Putka Lake Bolshoye Khmelozero Lake Putkozero Putka Drainage area, km2 Ratio of lake surface area to drainage area, % Height of source, m asl Recognised source River length, km Spirovsky Creek I Putka I Putka Keratskoye Lake Onega No name I Putka Lake Kondozero Lake Putkozero 6.8 No name I Putka Lake Korjuhozero Putka 2.1 Chugmuksa II Chugmuksa Lake Chuzhmozero Lake Onega, Svyatukha Bay 39.7 2.3 56.9 33 10.47 32.3 No name III Lake Vilozero Lake Degtozero Lake Onega, Svyatukha Bay 29.9 16.1 148 33 7.13 9.8 231.7 Reports of the Finnish Environment Institute 40 | 2014 47 Pigmarya IV Padma 2.9 Padma IV Padma Padamokh mire Lake Onega 109.5 24.9 72.4 33 1.58 10.4 Tsarevka V Tsarevka mire Lake Onega, Karguba Bay 46.5 10.2 60 33 2.66 0.00 Sarandzha V Tsarevka Sarandzha mire Tsarevka Kalei VI Kalei Kalei Lake Onega, Tolvuya Bay 92.6 33 2.30 0.8 Kurgilov VII Tambitsa mire Tambitsa 103.2 22.1 72.7 33 1.80 0.00 2.5 85.5 25.9 6.4 Tambitsa VII Tambitsa mire Lake Onega, Rechnaya Bay Nulitsa VIII Nulitsa mire Lake Onega, Tipinitsy Bay 28.4 9.2 61.6 33 3.10 0.00 Korezhruchei IX Korezhruchei mire Lake Onega, Tipinitsy Bay 16.1 4.0 46 33 3.22 0.00 Jandoma X Jandoma Lake Jandomozero Lake Onega 119.9 4.0 42.4 33 2.32 27.3 No name XI Lake Palozero mire Lake Onega, Svyatukha Bay 9.1 6.5 150 30 18.37 4.1 No name XII Lake Kosmozero – Onega Lake Kosmozero Lake Onega, Svyatukha Bay 104.1 1.1 38.4 33 4.75 22.4 Karasozerka (Melnichnyj) XII Lake Kosmozero – Onega Lake Karasozero Lake Kosmozero 7.5 98 38.4 7.95 Sudma XIII Sudma mire Lake Onega, Velikaya Bay 18.8 8.6 45 33 1.40 0.00 Antonovshchina XIV Antonovshchina mire Lake Onega, Velikaya Bay 28.3 4.8 50 33 3.52 1.3 Lelrechka XV Lelrechka Lake Lelikozero Lake Onega, Velikaya Bay 27.5 11.4 86.4 33 4.70 6.0 Chernyj XVI Ust-Reka (Lake Matkozero) Lake Nizhneye Kontozero Ust-Reka (Lake Matkozero) Ust-Reka (Lake Matkozero) XVI Ust-Reka (Lake Matkozero) Lake Matkozero Lake Onega, Vegoruksa Bay 47.5 33 1.74 1.3 Pizhei XVII Pizhei Pizhei Lake Onega, Velikaya Bay No name XVII Vegoruksa Lake Rugozero Lake Onega, Vegoruksa Bay 17.4 8.6 55.5 33 2.62 1.4 No name XIX Lake Vekhkozero Lake Vekhkozero Lake Onega 6.4 5.9 68.7 33 6.07 0.9 XX Vozhmarikha mire Lake Onega, Vozhmarikha Bay 19.0 10.8 105.2 33 6.68 0.05 XXI Lake Pivgozero Lake Pivgozero Lake Onega, Bolshaya Lizhemskaya Bay 26.4 1.8 38.2 33 0.11 12.0 Vozhmariha No name 48 2.6 61.1 8.3 4.6 Reports of the Finnish Environment Institute 40 | 2014 No name XXII Lake Tulozero mire Lake Onega, Tulguba Bay 13.4 5.3 68 33 6.56 2.5 No name XXIII Lake Syargozero Lake Syargozero Lake Onega, Ilemguba Bay 12.1 0.02 34.3 33 68.99 28.1 No name XXIV Lake Maloye Syargozero Lake Maloe Syargozero Lake Onega, Zimnyayya Bay 5.6 2.0 40 33 3.43 2.1 Thus, the hydrographically distinctive Zaonezhye Peninsula is a particularly picturesque area even by Karelian standards. However, due to its high ratio of lake surface area to drainage area, its relatively low drainage density and its diversity of water bodies, the area is particularly sensitive to human impact. Therefore, a strictly protected area is urgently needed on Zaonezhye Peninsula. REFERENCES BОХФТЧК, N. . 2005. К . . К К ДBШЭЭШЦ sОНТЦОЧЭs ШП ЭСО ХКФОs ШЧ ЭСО ГКШЧОгСвО PОЧТЧsЮХК.Ж – IЧ: EЧЯТrШЧЦОЧЭКХ ЩrШЛХОЦs ТЧ ЭСО НОЯОХШЩЦОЧЭ ШП ЭСО SrОНЧвКвК PКНЦК НОЩШsТЭ. PОЭrШгКЯШНsФ. Щ. 65–71. (IЧ RЮssТКЧ). FТХКЭШЯ, N.N. &.LТЭЯТЧОЧФШ, A.V. (ОНs.), 2001. К . ., . . ( .) К К К ДA МКЭКХШРЮО ШП KКrОХТК’s ХКФОs КЧН rТЯОrs.Ж – PОЭrШгКЯШНsФ. 290 Щ. (IЧ RЮssТКЧ). FrОТЧНХТЧР, V. . & PШХвКФШЯ, ВЮ. K. 1965. , . ., . . ДMШrЩСШХШРв КЧН СвНrШХШРв ШП ЭСО ХКФОs.Ж – IЧ: PrШЛХОЦs ТЧ ЭСО СвНrШХШРв, ХТЦЧШХШРв КЧН аКЭОr ЦКЧКРОЦОЧЭ ШП KКrОХТК. IssЮО ББIII. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 61–78. (IЧ RЮssТКЧ). GrТРШrвОЯ, S.V. & GrТЭsОЯsФКвК, G.L. 1959. , . ., К . . К К К ДA МКЭКХШРЮО ШП KКrОХТК’s ХКФОsЖ. – ШsМШа–LОЧТЧРrКН. 239 Щ. (IЧ RЮssТКЧ). KСКrФОЯТМС, N.S. 1965. К . . К ДHвНrШМСОЦТsЭrв ШП ЭСО ХКФОs ТЧ ОКsЭОrЧ ГКШЧОгСвО.Ж – IЧ: PrШЛХОЦs ТЧ ЭСО СвНrШХШРв, ХТЦЧШХШРв КЧН аКЭОr ЦКЧКРОЦОЧЭ ШП KКrОХТК. IssЮО ББIII. PОЭrШгКЯШНsФ. Щ. 110–139. (IЧ RЮssТКЧ). LТЭЯТЧОЧФШ, . V. 2000. . . К ДHвНrШРrКЩСТМ МСКrКМЭОrТsЭТМs ШП ЭСО ЭОrrТЭШrв.Ж – IЧ: IЧЯОЧЭШrв КЧН sЭЮНв ШП ЛТШХШРТМКХ НТЯОrsТЭв ШЧ ЭСО ГКШЧОгСвО PОЧТЧsЮХК КЧН ТЧ NШrЭСОrЧ PrТХКНШгСвО. PОЭrШгКЯШНsФ. Щ. 41–44. (IЧ RЮssТКЧ). LТЭЯТЧОЧФШ, .V. & BШРНКЧШЯК, .S. 2013. . ., К К . . К К ДHвНrШРrКЩСТМ ЧОЭаШrФ.Ж – IЧ: SОХФК ХКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ CСКrКМЭОrТsЭТМs, LКЧН UsО, Conservation (Gromtsev, A.N. (ed.). Karelian Research Center of Russian Academy of Sciences. Petrozavodsk. Щ. 36–46. (IЧ RЮssТКЧ). LТЭЯТЧОЧФШ, .V., FТХКЭШЯ, N.N., LШгШЯТФ, P. . & KКrЩОМСФШ, V. . 1998. . ., К . ., . ., К . . К К : К К К К ДRОРТШЧКХ ОМШХШРв: ОМШХШРТМКХ КЧН ОМШЧШЦТМ ПЮЧНКЦОЧЭКХs ШП ЭСО rКЭТШЧКХ ЮsО ШП KКrОХТК’s аКЭОr rОsШЮrМОs.Ж − IЧгСОЧОrЧКвК ОФШХШРТК 6: 3–13. (IЧ RЮssТКЧ). LШгШЯТФ, P. ., BКsШЯ, . I. & ГШЛФШЯ, . B. 2005. . ., К . ., . . К К. К ДSЮrПКМО аКЭОrs ШП ЭСО ГКШЧОгСвО PОЧТЧsЮХК. CСОЦТМКХ МШЦЩШsТЭТШЧ ШП ЭСО аКЭОr.Ж – IЧ: EЧЯТrШЧЦОЧЭКХ ЩrШЛХОЦs ТЧ ЭСО НОЯОХШЩЦОЧЭ ШП ЭСО SrОНЧвКвК PКНЦК НОЩШsТЭ. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 20–34. (IЧ RЮssТКЧ). MКsХШЯК, N.P. 1965. К К . . К К К ДАКЭОr СвНrШМСОЦТsЭrв ШП аОsЭОrЧ ГКШЧОгСвО.Ж – IЧ: PrШЛХОЦs ТЧ ЭСО СвНrШХШРв, ХТЦЧШХШРв КЧН аКЭОr ЦКЧКРОЦОЧЭ ШП KКrОХТК. IssЮО ББIII. PОЭrШгКЯШНsФ. Щ. 141–154. (IЧ RЮssТКЧ). ДPrОsОЧЭ МШЧНТЭТШЧ ШП ЭСО аКЭОr ЛШНТОs ТЧ ЭСО RОЩЮЛХТМ ШП KКrОХТК.Ж 1998. К . – PОЭrШгКЯШНsФ. 188 Щ. (IЧ RЮssТКЧ). ДRОsШЮrМОs КЧН РОШМСОЦТsЭrв ШП KКrОХТК’s ЮЧНОrРrШЮЧН аКЭОr Ж. 1987. К . KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. – PОЭrШгКЯШНsФ. 151 Щ. (IЧ RЮssТКЧ). SОЦвШЧШЯ, V.N. 1993. . . К ДCХТЦКЭО КЧН sЮrПКМО аКЭОr СвНrШХШРв.Ж – KТгСsФв ЯОsЭЧТФ. ГКШЧОгСвО.2:33–59. (IЧ RЮssТКЧ). SЭКrЭsОЯ, N.S. 1993. К . . К К ДNКЭЮrКХ аКЭОrs ШП ЭСО ГКШЧОгСвО PОЧТЧsЮХК.Ж –KТгСsФв ЯОsЭЧТФ. ГКШЧОгСвО. 2:59–74. PОЭrШгКЯШНsФ. (IЧ RЮssТКЧ). ДSЮrПКМО аКЭОr rОsШЮrМОs ШП ЭСО USSRЖ 1972 К. . VШХ. 2. KКrОХТК КЧН ЧШrЭСаОsЭ RЮssТК. PКrЭ 1. – LОЧТЧРrКН. 528 Щ. (IЧ RЮssТКЧ). ДSЮrПКМО аКЭОr rОsШЮrМОs ШП ЭСО USSRЖ 1972 Л. . VШХ. 2. KКrОХТК КЧН ЧШrЭСаОsЭ RЮssТК. PКrЭ 3. – LОЧТЧРrКН. 960 Щ. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 49 VХКsШЯК, .S. 1965. К К . . К ДBШЭЭШЦ sОНТЦОЧЭs ТЧ ЭСО ХКФОs ШП ГКШЧОгСвО.Ж – IЧ: PrШЛХОЦs ТЧ ЭСО СвНrШХШРв, ХТЦЧШХШРв КЧН аКЭОr ЦКЧКРОЦОЧЭ ШП KКrОХТК. IssЮО ББIII. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 93–103. (IЧ RЮssТКЧ). ДГКШЧОгСвО NКЭЮrО PКrФЖ. 1992. К « К ». – PrОЩrТЧЭ ШП К ЩrОsОЧЭКЭТШЧ КЭ К PrОsТНТЮЦ sОssТШЧ ШП ЭСО KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 35 Щ. (IЧ RЮssТКЧ). Fig. 3. Lake Bolshoe Khmelozero (Photo Maria Bogdanova). Fig. 4. Lake Kovshozero (Photo Maria Bogdanova). 50 Reports of the Finnish Environment Institute 40 | 2014 Fig. 5. Lake Korytovo (Photo Maria Bogdanova). Fig. 6. Putka River (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 51 Fig. 7. Spirovsky Creek (Photo Maria Bogdanova). 52 Reports of the Finnish Environment Institute 40 | 2014 1.4 Soils and their characteristics on Zaonezhye Peninsula Olga N. Bakhmet* and Natalya G. Fedorets* *Forest Research Institute of the Karelian Research Center of Russian Academy of Sciences 11 Pushkinskaya St., 185610 Petrozavodsk, Karelia, Russia E-mail: obahmet@krc.karelia.ru Introduction The soil cover of Zaonezhye Peninsula is very distinctive. It differs considerably from other parts of Karelia due to the unique nature of the region. Soil patterns are mainly determined by a variety of landforms, including high, narrow ridges that alternate with narrow depressions. The macrorelief is also responsible for the climatic conditions in the area: Zaonezhye is protected against northerly winds, which makes its climate milder than in adjacent areas. The unconsolidated Quaternary sediment cover, produced by glacial abrasion, is either thin or completely absent. Soil-forming rocks are represented mainly by basic bedrocks, such as gabbro-diabase and amphibole, overlain by Leptosols and Cambisols (World reference base.. 2006). Due to widespread shungite schist and schist-enriched moraine, the soils are regionally and globally unique. Soil types and their characteristics The irst deinition of soils on shungite-bearing, soil-forming rocks was proposed by the academic F.Yu. Levinson-Lessing (Levinson-Lessing 1889) who named them “Olonets black soil”. Their place in the Russian soil classiication (1997, 2004) as well as in international soil classiications remains a subject of debate. Some researchers consider them as soils with well-developed sod-forming processes, which is inaccurate for several reasons. First, sodden soils develop under meadow plant communities, whereas virgin soils on shungite-bearing soil-forming rocks are formed under forest vegetation with decomposed mull litter. Secondly, in sodden soils humus typically accumulates in the sod horizon and its content in the underlying horizons decreases abruptly. However, in soils formed on shungite-bearing rocks, humus can be traced to a great depth in the proile and occasionally its concentration at the boundary with parent rock can be up to 2%. Thirdly, in the taiga zone, sodden soils are formed in an acid environment, whereas soils resting on shungite-bearing rocks are developed in neutral or subacid environments. Some researchers classify soils formed on shungite Reports of the Finnish Environment Institute 40 | 2014 53 rocks as lithogenic. However, this is also inaccurate since biological processes in these soils are vigorous. Thus, their place in soil classiication remains uncertain. Shungite-bearing rocks include shungite and shungite schist deposits as well as glacial and aqueo-glacial deposits. These deposits have different mechanical compositions but all contain a high percentage of black coaly shale, which gives them their black colour. As a soil-forming rock, shungite differs markedly from other parent rocks in its high carbon and hygroscopic moisture content. It also has a high absorptive capacity due to the presence of ine-grained carbon. The carbon content of shungite rocks varies between 5% and 95%; the higher the carbon content, the more intensely the rocks are eroded and weathered and the higher the mineral nutrient content of the soil. The mechanical compositions of soil-forming rocks are highly diverse, including gravelly sand, loamy sand, loam and ine clay. The silica content (of particles over 1 mm in diameter) can be over 80%. Genuine shungitic soils are common in areas covered by shungite eluvium-deluvium and shungitic moraine. With increasing distance from shungite deposits, the shungite content of moraine decreases and the moraine acquires a composition in which basic and shungite rocks are mixed with silicate rocks in equal proportions. Shungitic soils are common in such areas. These soils are darker and less acidic than Cambisols. They are also enriched with iron and mineral nutrients. Shungitic soils are usually combined with poorly developed Leptosols that are conined to slopes and podzolised Albic Cambisols, occupying low landforms. Soils on shungite-bearing rocks are formed under forest vegetation, dominated by small-leaved forests and a well-developed grass cover. Despite large quantities of plant residues accumulating at the surface, thick forest litter does not form due to the high biological activity of soil animals and microorganisms. Due to the characteristics of the soil-forming rocks as well as the accumulation of plant residues, there is a distinctive pattern of organic soil proile with a high percentage of humus and a homogenous composition of organic matter throughout the soil proile. Despite a high percentage of crushed stone and high water permeability of soils on shungite rocks, humic acids are ixed in the soil proile. This is due to the distinctive chemical composition of the soils, containing low silica and high iron and calcium oxide concentrations. These form strong polymeric complexes with humic acids. The low mobility of organic-mineral complexes in soils formed on shungite-bearing rocks has led to the formation of a texturally undifferentiated proile where organic matter and mineral mass are transformed in situ without the migration of substances beyond the soil boundary. Thus, the main processes that form the above soils are humus formation under neutral or slightly acid environmental conditions and the in situ metamorphism of mineral mass with the release of iron, calcium and other oxides. These soil-forming processes are not characteristic of Karelian soils but their occurrence in Zaonezhye is due to unique natural conditions. Primitive soils, combined with Leptosols, are common where crystalline rocks are either exposed or occur near the earth’s surface. Primitive soils are subdivided into crustal, organic (sodden, humus, peaty) or detrital soils depending on the degree of soil-forming process. In primitive soils, the layer of unconsolidated material is no more than 10 cm thick and consists of crystalline rock eluvium. Diabase eluvium, which is common in Zaonezhye, contains a large amount of iron (up to 20%) and calcium. Because the unconsolidated sedimentary cover is thin, these soils are poorly fertile. Open pine forests with suppressed growth occupy these soils. In parts of their distribution, they also grow juniper brushwood (alvars). Leptosols are formed on lat ridge tops or terraced slopes that provide favourable conditions for the accumulation of crystalline rock eluvium and eluvium-deluvium. 54 Reports of the Finnish Environment Institute 40 | 2014 These soils often grow moderately dense pine stands with grass in the undergrowth. Also juniper brushwood is occasionally encountered. The soil proile consists of A0-AhBfm-BC-M horizons. The AhBfm horizon displays features characteristic of humus-illuvial and metamorphic horizons. It is hard to divide these soils into genetic horizons because they contain large amount of rocks and crushed stone (particle content varies between 50 and 90%). The entire proile of these soils is saturated with humus. Podzols are typical of Karelia but scarce in Zaonezhye, which is due to the polymictic composition of unconsolidated sediments that contain considerable quantities of boulders, crushed stone as well as coarse basic and intermediate rocks. Also the abundance of mixed and deciduous open woodland, with a well-developed grass cover, contributes to the accumulation of humus. The podzolic soils of Zaonezhye are characterized by the poor eluvial-illuvial distribution of silicon, the presence of aluminium and iron oxides along the proile as well as the accumulation of organic elements (phosphorus, calcium, manganese, potassium, magnesium and sulfur) in the forest litter. However, the mineralogical composition of soil-forming rocks has affected the chemical composition of the soils. As a result, almost all of the soils contain much less silica than average in Karelia. These soils are also enriched with iron and often calcium, which has decreased soil acidity. Therefore, podzolic soils with a humus-accumulating horizon (A1) and a low level of podzolization are more common in Zaonezhye than podzols. Histic Podzols are formed on poorly drained plains and in wide depressions, composed of silicate sand and loamy sand, where ground water is near. Normally there is peat-saturated forest litter for at least 10 cm or a 10–30 cm thick peaty horizon. These soils are highly acidic, particularly in the upper part of the proile, and they have a low base saturation. Therefore, the soils are poorly fertile. Peaty soils are formed in deep depressions and lows between ridges under moisture-loving vegetation. In these conditions there is excess moisture and, therefore, the mineralization of plant residues is delayed. Fibric Histosols occupy only a small area in Zaonezhye. They are more common in watershed areas composed of silicate moraine, aqueo-glacial sand and loamy sand. Terric Histosols occur in areas where basic crystalline rocks are widespread. There, they occupy mires in old lake basins without outlow, ravines and at the foot of the slopes. Conclusions Zaonezhye consists of diverse areas. The soil contours are clearly aligned from southeast to northwest throughout the area. The distinctive feature of soil cover in Zaonezhye is its unique dark soils formed on carbonaceous rocks (shungite) or glacial deposits that are not encountered in other parts of the world. Although soils formed on shungite-bearing rocks have attracted the attention of many researchers who have described physical, chemical and biological soil properties in their publications, many issues remain poorly understood. Also, their place in soil classiication is unclear. Considering that shungite-bearing rocks are highly diverse in their chemical composition and abundance in Quaternary deposits, the genesis of these soils is still largely unknown. LITERATURE LОЯТЧsШЧ-LОssТЧР, F.ВЮ. 1889. . . sШТХЖ. − IЧ: OХШЧОЭsФТвО GЮЛОrЧsФвО VОНШЦШsЭТ 33:357–358. PОЭrШгКЯШНsФ. АШrХН rОПОrОЧМО ЛКsО ПШr sШТХ rОsШЮrМОs. 2006. ДOЧ ЭСО OХШЧОЭs ЛХКМФ Reports of the Finnish Environment Institute 40 | 2014 55 Mesic grassland in Zaonezhye Peninsula: Gymnadenia conopsea among Melampyrum nemorosum (Photo Tapio Lindholm). 56 Reports of the Finnish Environment Institute 40 | 2014 1.5 Paleogeography of Zaonezhye Peninsula Lyudmila Filimonova* and Nadezhda Lavrova** *Institute of Biology of Karelian Research Center of Russian Academy of Sciences, Petrozavodsk. 11 Pushkinskaya St, 185910 Petrozavodsk, Karelia, Russia Corresponding author Lyudmila Filimonova E-mail: ilimonovaluda@mail.ru Tel: +79535444890 ** Institute of Geology of Karelian Research Center of Russian Academy of Sciences, 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia E-mail: lavrova@krc.karelia.ru Tel.: +79214545451 Introduction Zaonezhye Peninsula juts out into Lake Onega, occupying central parts of its northern coast. It is a unique area of diverse Quaternary sediments. Diverse in composition and distribution of the complexes of Quaternary deposits are a result of the complex structure of the crystalline basement, the composition of bedrocks as well as the Late Pleistocene and Holocene evolution. The distribution of Quaternary sediments forms the basis of modern landscapes and biodiversity on the peninsula. Major relief-forming factors include glacial activity and denudation of surface horizons in Precambrian crystalline rocks. A combination of these factors has resulted in two genetically different landforms: 1) forms composed of crystalline rocks and 2) forms consisting of Quaternary rocks of different genesis (e.g. glacial and glacioluvial accumulative relief). The topography of Zaonezhye Peninsula can be divided into two parts: eastern and western. The eastern part is a moraine plain with gently sloping hills. It is a relatively lat area 30–60 m above lake level with paludiied depressions separated by gently sloping ridges. The western part of Zaonezhye Peninsula displays a typical selkä relief with a system of NW-trending ridges at an altitude of up to 120 m above lake level. Ridges have steep, stepped slopes and steep scarps. Narrow lake basins and the Lake Onega bays occupy depressions between the ridges. Elevated sites are either covered with thin moraine, or completely devoid of Quaternary sediments. All glacial and aqueoglacial deposits on Zaonezhye Peninsula relect the composition of the bedrock, eroded by glaciers (Lukashov & Ilyin 1993). Local moraines are widespread on shungite schis and rich in carbon, potassium, nitrogen and trace elements such as Cu, V, Ni, Zn and B. These elements are easily assimilated by plants, thus providing substrate for shungitic “black earth (chernozem)”, one of the best soil types for agriculture in Karelia Reports of the Finnish Environment Institute 40 | 2014 57 (Demidov 1993). The topographic characteristics and the composition of Quaternary deposits determine the plant biodiversity of Zaonezhye Peninsula. Vegetation dynamics have been reconstructed from the Allerød period (~11800 BP) to the present based on palynological, macrofossil and radiocarbon data for the lacustrine deposits of the Lake Putkozero cross-section from central Zaonezhye Peninsula (Lavrova 1999, Demidov & Lavrova 2000) as well as from lake-mire deposits of the Zamoshye and Boyarshchina cross-sections from eastern parts of the peninsula (Elina & Filimonova 1999, Elina et al. 1999, 2000, Elina et al. 2010; Fig. 1). Also, data from coeval deposits in central parts of Lake Onega as well as present-day ponds and mires in its basin have been analysed (Elina 1981, Filimonova 1995, 2010, Elina Filimonova 1996, Lavrova 2004, 2005). Vegetation dynamics are shown against variations in geomorphology (Lukashov & Ilyin 1993, Demidov & Lavrova 2000), climate (Klimanov & Elina 1984, Filimonova & Klimanov 2005) as well as the transgressions and regressions of Lake Onega (Devyatova 1986, Demidov 2005, 2006). In addition, surface pollen and spore spectra from the study area and other regions as well as correction coeficients for tree pollen have been examined (Elina & Filimonova 1999, Filimonova 2007 et al.). Ecological and geographic analyses of identiied taxa (after Grichuk et al. 1969) and estimations of pollen concentration in the deposits (after Stokmarr 1972) have been performed to reveal redeposited and remote pollen, which is essential for the study of Late Glacial vegetation. 58 Reports of the Finnish Environment Institute 40 | 2014 Fig. 1. Pollen diagram for the lake-mire deposits of the Zamoshye cross-section. (КЧКХвsОН Лв E. DОЯвКЭШЯК КЧН L. FТХТЦШЧШЯК) ДТЧ: EХТЧК КЧН FТХТЦШЧШЯК 1999Ж LОПЭ – sЭrКЭТРrКЩСТМ МШХЮЦЧ: 1–8 = ПОЧ ЩОКЭ: 1 – ЛТrМС, 2 – аШШНв, 3 – аШШНв-rООН, 4 – аШШНв-РrКss, 5 – rООН, 6 – РrКss, 7 – sОНРО-Sphagnum, 8 – Sphagnum (Sphagnum teres), 9 – ЭrКЧsТЭТШЧКХ Sphagnum (S. centrale); 10 – sКЩrШЩОХ-ХТФО ЩОКЭ; 11 – sКЩrШЩОХ; 12–14 – МХКвs: 12 – ЦКssТЯО, 13 – iЧО sКЧН ХОЧsОs, 14 – ЯКrЯОН. IЧ ЭСО НТКРrКЦ, iХХОН ЩКЭЭОrЧs sСШа ЭСО ЩШХХОЧ КЧН sЩШrО МШЧЭОЧЭ (%) ШП ЭСО ЭКбК ТЧНТМКЭОН; ЮЧiХХОН ЩКЭЭОrЧs sСШа ЭСО МШЧЭОЧЭ (%) ЦКРЧТiОН Лв 10; МШЧМОЧЭrКЭТШЧs ШП ХОss ЭСКЧ 1% КrО sСШаЧ аТЭС НШЭs Reports of the Finnish Environment Institute 40 | 2014 59 Geological Periods Late Glacial period (AL, DR3: 11 800–10 300 BP). Approximately 12 000 years ago, the territory of present-day Lake Onega and its surroundings were occupied by the last glacial ice sheet. During the retreat of the Valdai glaciation, a large periglacial meltwater body formed in the Lake Onega basin and on the adjacent lowlands. Its area and water level varied constantly depending on the position of the ice margin, the glacial isostatic adjustment of the earth’s crust and the erosional activity around the lake’s margins. After reaching the southern shores of Zaonezhye Peninsula, the glacier retreated relatively rapidly. Large, deep periglacial water bodies such as Lake Onega (which was over 100 m deep), Lake Ladoga and the White Sea contributed to the rapid retreat of the glacier. The periglacial Lake Onega basin, over 100 m deep, was dominated by a type of deglaciation which caused the ascent and destruction of the ice lobe periphery. In this case, the ice margin retreated at a speed of no less than 1–1.5 km/year, while upon deglaciation of frontal type it retreated at a speed of no more than 200–250 m/year. However, on reaching the south shore of the Zaonezhye Peninsula, the glacier retreated fairly rapidly Active glacier tongues, moving across deep bays and the rugged relief of the peninsula, contributed to the rapid disintegration of the ice lobes. The deglaciation of the Lake Onega basin began around 12 400 BP. By about 11 600 BP the ice had receded completely from the northern parts of Zaonezhye Peninsula (Demidov 2005, 2006, Filatov 2010) (Fig. 2). Fig. 2. Deglaciation of Zaonezhye Peninsula [After Demidov 2005, Filatov 2010]. 1 – Active ice sheet 2 – Passive ice sheet 3 – Cracks and tunnels in glacier 4 – Old water bodies and icebergs 5 – Large dead ice massifs 6 – Runoff directions 7 – Modern hydrographic network 8 – Absolute altitudes of modern surfaces 9 – Large old deltas 60 Reports of the Finnish Environment Institute 40 | 2014 During deglaciation, the water level of the periglacial Lake Onega changed constantly. The periglacial lake started to developed in the lower River Vytegra, on the southern shores of present-day Lake Onega. It is likely to have formed a part of the Upper Volga lake system where the water level was 120–130 m (Kvasov 1976). As a result of the glacial runoff, cutting through the river valley of Oshta, Tuksha and Oyat into the Baltic Sea about 12 500–12 400 BP, the lake’s water level dropped to 106 m (Demidov 2006). About 12 300 BP the ice margin retreated from the Svir river valley, and the lake was provided with a new, lower, threshold into the Baltic Sea (Saarnisto & Saarinen 2001). Consequently the water level in its southern parts dropped to 75–85 m (Demidov 2006). As a result of glacier retreat, deglaciation of new areas and glacial meltwaters, the periglacial Lake Onega reached its maximum size by the end of the Allerød (about 11 400 BP) when its water level rose to 115–130 m in the northern part. About 11 300 BP the water level dropped by 20–25 m down to 95–100 m due to isostatic uplift of the earth’s crust and the opening of a new threshold into the White Sea. Also another threshold was opened into Lake Ladoga in the northern parts of the Onega-Ladoga watershed and River Vidlitsa before the water level stabilized for a long time. The next large-scale regression of Lake Onega took place at the end of the Late Pleistocene about 10 300 BP due to the renewed runoff into Lake Ladoga though River Svir. At the same time Lake Onega lost its connection with the ice margin, which had retreated to Western Karelia. As a result, its level dropped by about 20 m and large areas were drained (Demidov 2005, 2006). Varved clay accumulated in the periglacial Lake Onega until 10 700 BP. After the ice margin retreated beyond the lake basin, mass deposition of homogeneous clay and silt in Lake Onega began. As deglaciation proceeded, water-and ice-free areas were colonized by vegetation whose distribution and evolution were determined by climatic, geological and geomorphological factors. At the inal stages of the Valdai glaciation, climatic changes were considerable. Quantitive climatic indices have been estimated for the Late Dryas: mean July temperatures were 3–6° lower, mean January temperatures 8–14° lower, annual temperatures 5–9° lower and precipitation 175–250 mm/year lower than at present (Filimonova & Klimanov 2005; Fig. 3). During the earlier Allerød interstadial warm period, negative temperature and precipitation deviations would have been more substantial on Zaonezhye Peninsula without the huge periglacial water body that made the climate slightly less continental. Reports of the Finnish Environment Institute 40 | 2014 61 Fig. 3. Dynamics of the climate, of Lake Onega level and vegetation in the Late Glacial and Holocene periods. Palaeoclimatic characteristics are shown as deviations from present values: toVI = 16o, toI = - 11o, toyear = 2o, total annual precipitation = 550 m. Acronyms: T – tundra, FT – forest-tundra, NT – northern taiga, MT – middle taiga, ST – southern taiga, Qm – broad-leaved species and hazel 62 Reports of the Finnish Environment Institute 40 | 2014 The evolution of the vegetation in Zaonezhye began after the ice receded and plants started to invade suitable areas, free from the melting ice. First almost the entire Zaonezhye was covered by the periglacial Lake Onega, leaving only some islands, elongated in a near-N-S direction, above the water level (Fig. 4). Plant growth was boosted by the presence of small quantities of mineral nutrients in the substrate, supplied by glacial meltwaters. Lower plants, dominated by algae and lichens, were most probably the irst to colonize the study area. These were followed by higher plants (Botrychium boreale, Dryas octopetala, Eurotia ceratoides, Lycopodium alpinum, Thalictrum alpinum, Saxifraga oppositifolia, Cryptogramma crispa, Ephedra and Saxifraga species) growing on crushed stones and rocky ground as well as on substrates with an unstructured, disturbed soil cover (Artemisia species,Chenopodium album, Ch. polyspermum, Ch. rubrum, Kochia lanilora and K. scoparia). These species are not sensitive to environmental change. However, they are resistant to temperature variations and water availability. These species grew on the soil-free islands that later turned into mainland of Zaonezhye Peninsula. First, seeds brought by various agents such as wind and water evolved into seedlings that provided the area with more seeds and formed a pioneer community. Later the pioneer species were joined by new species. As the ice retreated, water level in the periglacial lake dropped. While soils began to form on the islands and in adjacent areas, also the plant cover became more complex. It consisted of forest, tundra and steppe communities, comprised of species conined to different environments. Due to the proximity of the retreating ice cover, the weather was dry and the ground was saturated, which created favourable conditions for the growth of xerophytes, mesoxerophytes, mesophytes and hygrophytes. Late Glacial deposits on Zaonezhye Peninsula contain pollen of geographically diverse arctalpine (Dryas octopetala, Diphasiastrum alpinum, Saxifraga oppositifolia, Thalictrum alpinum, Oxyria digyna, etc.), hypoarctic (Betula czerepanovii, Botrychium boreale, Huperzia appressa, Lycopodium pungens, Rubus chamaemorus, Selaginella selaginoides, etc.), boreal (Alnus incana, Diphasiastrum complanatum, Lycopodium clavatum, etc.) and steppe species (Ephedra, Helianthemum, Eurotia ceratoides, Kochia scoparia, Kochia lanilora, etc.). During the Late Glacial period the plant cover was open, as shown by low pollen concentrations and the occurrence of heliophyte pollen (Hippophae rhamnoides, Helianthemum and Ephedra) in the deposits. Pioneer plant groups and bare ground succeeded each other. One of the critical factors limiting the spread of vegetation was long-term permafrost, which prevented the downward growth of roots. Its existence in the study area is supported by the presence of halophytes (Salsola kali, Salicornia herbacea and Atriplex nudicaulis) that found favourable habitats in saline depressions. Chenopodium album, Ch. rubrum, Eurotia ceratoides and Ephedra are also resistant to moderate salinity. In the dry continental climatic conditions, salts accumulated in the surface soil layer, while permafrost prevented their transfer into the deeper horizons. Permafrost contributed to the saturation of soils, too, by preventing moisture from penetrating into deeper layers, which in turn led to soliluction. Cold winters with little snow and strong winds were typical of periglacial zones and resulted in soil erosion. Thus, soliluction and erosion created suitable habitats for plants growing in disturbed and unstructured soils (taxa are shown above). Relief and the composition of Quaternary sediments were essential for the formation and distribution of plant communities. The succession of plains, ridges and hills created diverse conditions for plant growth on clay, loam and inequigranular sand. Some of the hills were completely devoid of Quaternary cover. Elevated areas and slopes were composed of rock debris, occupied by xerophylous communities (i.e. species of the Chenopodiaceae family and the Artemisia Ephedra and Helianthemum genera, Dryas octopetala, Cryptogramma crispa, Huperzia appressa, etc.). Depressions with accumulated snow protected plants against cold winter winds and provided Reports of the Finnish Environment Institute 40 | 2014 63 favourable habitats for tundra-like dwarf birch-green moss communities, consisting of Selaginella selaginoides, Rubus chamaemorus and Salix, Pedicularis, Cyperaceae and Poaceae species, in addition to Betula nana and Bryales. One of the factors responsible for the distinctive pattern of the Late Glacial vegetation was the permanent exposure of the earth’s surface after the glacier retreat and the lowering of the periglacial lake level. As a result, paleocommunities of unstructured soils existed for a long time. The presence of algae of the genus Pediastrum (Pediastrum boryanym var. boryanum, P. integrum var. integrum, P. kawraiskyi, P. privum) indicates that the periglacial Lake Onega was cold, deep and oligotrophic. Such conditions halted the spread of aquatic and littoral aquatic plants. The growth of woody species in the late glacial period poses a complex and ambiguous question. On one hand the pollen content of the deposits from the late glacial period is high (Fig. 1). On the other, most pollen seems to have been transported by wind and redeposited, as indicated by the low pollen concentration of woody plants. At the same time, favourable habitats provided good conditions for some woody plants, e.g. Betula pubescens, B. czerepanovii, Alnaster fruticosus and Alnus incana. These species differ considerably in their adaptability to low temperatures, cold soils and permafrost. It is likely that there were favourable habitats for open communities of woody plants or individual trees at least at the end of the Allerød. Another signiicant cooling event triggered the advance of the glacier in the Late Dryas (Fig. 3). Due to cold winters and thin snow cover, soliluction, erosion and weathering of the unstable ground increased. As a result, areas covered by crushed stone, rocky ground and plant communities on disturbed soils (Artemisia, Chenopodiaceae species, etc.) expanded. While the contribution of woody communities in the plant cover decreased, the tundra dwarf birch-green moss communities were survived in favorable habitats (Fig. 3, Fig. 4). In general the loristic composition of the Late Glacial vegetation remained practically unchanged. 64 Reports of the Finnish Environment Institute 40 | 2014 Fig. 4. Palaeovegetation maps of Zaonezhye Peninsula (10 500, 8500, 7500, 5500, 3000 and 1000 BP) [After Elina et al. 2010]. 1, 2 – Periglacial palaeocommunities (pc): 1 – Artemisia-Chenopodiaceae, 2 – Artemisia-Chenopodiaceae with herbs; 3 – Tundra pc: Betula nana-Bryales pc; 4 – Forest tundra pc: open Betula woodland; 5–9 – Middle taiga pc: 5 – Betula-herbs, 6 – Betula-Alnus-herbs, 7 – Pinus-Betula with Alnus, 8 – Pinus-Ericales-Bryales-Lichenes, 9 – Picea-Ericales-Bryales; 10–12 – Southern taiga pc: 10 – Pinus-herbs and Pinus-herbs-Bryales, 11 – Alnus glutinosa-Picea-herbs, 12 – Picea-Ulmus-herbs; 13 – Past shoreline; 14 – Shoreline at present; 15 – Shore scarps Reports of the Finnish Environment Institute 40 | 2014 65 The Holocene (10 300 BP – Present) During the Holocene, the greater availability of heat and moisture triggered an irreversible change in plant cover dynamics. As a result, the treeless ecosystems of Late Dryas were succeeded by open birch woodland and, more recently, taiga forests. The Preboreal period (PB: 10 300–9 300 BP) began with a substantial warming of the climate to a temperature maximum ca. 10000 BP when July temperatures were 2°C lower, January temperatures 6°C lower and annual temperatures 4°C lower than at present. Also precipitation was lower by 150 mm/year. Then, in PB-2 (10 000–9 300 BP), the climate became more unstable and colder, especially in the winter months. The deviation of the above parameters was 4–4.5°, 6–9°, 5–7° and 150–200 mm/year, respectively (Filimonova & Klimanov 2005; Fig. 3). The water level of Lake Onega continued to decrease, while transgressions and regressions succeeded one another (Fig. 3). Cross-sections have been studied from the massive clay deposits of Zamoshye and Boyarshchina on Zaonezhye Peninsula (Elina, Filimonova et al. 1999, Elina et al. 1999, 2000, Elina et al. 2010). Consequently, varves of ine sand found in the clay clearly correlate with the regressions: irst varve at the DR3/PB contact, second varve in the middle of PB and third varve at the end of PB (Fig. 1, Fig. 3). As the water level of Lake Onega declined, islands jutted out of the water and merged to form larger islands. Water-free areas were colonized by Artemisia, Chenopodiaceae (including Chenopodium album, Ch. hybridum, Ch. foliosum, Ch. glaucum, Ch. polyspermum, Ch. rubrum, Eurotia ceratoides, Salicornia herbacea, Salsola kali) and other pioneer plants. It looks as if these plant groups followed the retreating lake water and remained widespread until the end of the Preboreal period. At the beginning of the period, a large part of the area was occupied by dwarf birch-green moss tundra with Sphagnum, dwarf birch and willow thickets, occurring along the creeks. Birch continued to spread, although its contribution in the plant cover decreased. The tundra communities conined to fragmented stones and rocks on the tops and slopes of ridges, hight above sea level, persisted longer than other communities. The considerable contribution of wormwood-goosefoot-motley grass (Artemisia-Chenopodiaceae-Varia) paleocommunities during the Preboreal period was due to the cold and dry climate (Fig. 3), the cooling effect of Lake Onega and the formation of new land areas after the lowering of the lake’s water level. In the parts of Karelia, farther from large water bodies these communities were more typical during DR3, whereas in the PB-period their contribution in the plant cover decreased (Elina 1981, Filimonova 1995, 2014, Lavrova 2005, 2006). In the early Preboreal period open birch woodland (Betula czerepanovii, B. pubescens) spread on plains, ridge tops and ridge slopes. The ground cover was composed of Betula nana, Salix, Ericales, Poaceae, Bryales and Lycopodiaceae, presumably with a small percentage of Pinus sylvestris (Fig. 3, Fig. 4). Moist habitats were dominated by tallgrass open birch forests with Alnus incana, while depressions with good water low and ground cover of clay and loam were colonized by birch-alder and alder grassfern communities with Filipendula ulmaria, Geum rivale and Angelica sylvestris. In the late PB-2 (approximately 9 700 BP onwards), birch forests (Betula pubescens) and open pine-birch forests, similar to northern taiga forests, became more abundant (Fig. 3). Alder grew in tall-grass birch forests and formed alder groves. During the Preboreal period the number of xerophytes, halophytes and species typical of unstructured and disturbed grounds decreased, together with arctic, arctalpine, hypoarctic and steppe lora. At the same time boreal species, especially mesophytes and hydrophytes became more abundant. Grasses were represented by Apiaceae, Asteraceae (Aster, Tanacetum type), Brassicaceae, Caryophyllaceae, Ephedra, Fabaceae, Galium, 66 Reports of the Finnish Environment Institute 40 | 2014 Lamiaceae (including Mentha), Myosotis, Polygonaceae (including Bistorta oficinalis, Rumex,), Ranunculaceae (including Thalictrum alpinum), Rosaceae (including Dryas octopetala, Filipendula ulmaria), Scrophulariaceae, Urtica, Cyperaceae, Poaceae and Polypodiaceae (including Polypodium vulgare). Lycopodiaceae included Diphasiastrum alpinum, D. complanatum, Huperzia apressa and Lycopodium pungens. The formation of shallow bays made possible the growth of wetland plants (Myriophyllum spicatum, Sparganium, Parnassia palustris, Phragmites australis, Typha angustifolia, T. latifolia, Cyperaceae, Isoëtes, Equisetum, Bryales and Sphagnum). During the Preboreal period, nature and climate were generally unfavourable for human livelihood, although temporary settlements may have been established on the shores of shallow bays during warmer periods. The Boreal Period (BO: 9300–8000 BP) is characterized by the some climate warming. It began with cold conditions but reached maximum temperatures around 8500 BP when air temperatures were either close to, or above present values in the Lake Onega basin (Elina et al. 1984, Devyatova 1986, Filimonova & Klimanov 2005). In BO-3 (8300–8000 BP) the climate cooled and around 8200 BP July temperatures decreased by 1.5°C, January temperatures by 3.5°C and annual temperatures by 2.5°C. The amount of precipitation were by 25 and 75 mm/year lower than at present, respectively (Fig. 3). Thus, the climate was drier during the Boreal period than at present. In the BO-period, the water level in Lake Onega varied as transgressions were succeeded by regressions (Fig. 3). During the last regression, the water level dropped to 43 m above sea level. As a result, island area increased signiicantly. The vegetation responded to the changes in nature and climate, changing from northern taiga in the irst third of the Boreal period to middle taiga thereafter. Pine, birch-pine-green moss and grass-motley grass forests became predominant in the central parts of the islands (Fig. 4). Birch and alder tall-grass forests with Poaceae, Polypodiaceae (including Dryopteris linnaeana, D. phegopteris and D thelypteris) and motley grasses, e.g. Apiaceae, Fabaceae, Liliaceae, Polygonaceae (including Bistorta oficinalis), Ranunculaceae (including Thalictrum), Rosaceae (including Filipendula ulmaria), Rumex, Urtica grew at lower altitudes in shallow, well-lowing topographic depressions The presence of Artemisia and Chenopodiaceae pollen in the deposits (Fig. 1) indicates that more extensive areas became water-free during the Boreal period. Furthermore, habitats responded to the new environmental conditions. Late Glacial deposits contain pollen of Hippophae rhamnoides and Ephedra as well as Dyphasiastrum alpinum spores. Also the abundance of the Lycopodiaceae spores (Dyphasiastrum complanatum, D. tristachium, D. alpinum, Huperzia selago, Lycopodium pungens, L. annotinum and L. clavatum) is characteristic of the Boreal period. Club mosses are characteristic of open woodlands and open, treeless areas, including exposed, rocky grounds. The increased abundance of pollen and spores of aquatic (Myriophyllum spicatum, Nymphaea, Potamogeton, Sparganium and Iso tes) and coastal-aquatic plants (Alisma, Parnassia palustris, Phragmites australis, Typha angustifolia, T. latifolia and Cyperaceae) indicate an abundance of shallow bays. During the Boreal period Lake Onega retreated, more areas became water-free and the climate became milder. As a result, conditions for human livelihood became more favorable. Around the lake, people picked mushrooms and berries as well as ished and hunted for elk, reindeer, bear, hare and other animals, including waterfowl (geese, ducks, etc.) The Atlantic period (AT: 8000–4700 BP) was a period of a climatic optimum as well as considerable changes in hydrology and vegetation. Air temperature were higher than at present throughout the entire period: 1–2.5°C warmer in July and 1–4°C warmer in Reports of the Finnish Environment Institute 40 | 2014 67 January. In general, mean annual precipitation was higher by 50–75 mm/year. But it decreased in the late AT-3 (especially around 5200 BP) when air temperatures were relatively high (Fig. 3). As the results, the climate became drier in this time. During AT-1 (8000–7000 BP), the natural complexes of the Lake Onega basin were affected by the warm, humid climate as well as the considerable (over 3 m) transgression of Lake Onega (Fig. 3). Also, the water levels in small and medium-sized water bodies rose, as well as the groundwater in mires (Filimonova, 2010 et al.). In the middle of AT-2 (7000–6000 BP), the climate became less humid and the crystalline Baltic Shield continued to ascend. As a consequence, the Lake Onega water level dropped by 5 m. Its subsequent variations were smaller, in accordance with humid and dry periods (Fig. 3). Peat accumulation began here about 6700–6600 BP, during the Mid-Atlantic regression of Lake Onega. The mire has never been looded by lake water since (Elina & Filimonova, 1999). As a result of regression that preceded the AT-period, the depression, occupied now by Zamoshye Mire, separated from Lake Onega, and a shallow, overgrowing water body was formed there. This is supported by the greater occurrence of the pollen and spores of aquatic and mire plants and the formation of 10 cm thick sapropel and sapropel-like peat layers in the central portion of the mire in the late AT-1. Peat accumulation began there about 6700–6600 BP, when the Mid-Atlantic regression of Lake Onega took place. A warmer and more humid climate supported the spread of broad-leaved species (Ulmus laevis, U. glabra, Quercus robur, Tilia cordata, Acer platanoides), Corylus avellana and Alnus glutinosa. These species became most abundant in Zaonezhye during AT-2, as shown by the radiocarbon date 6580±80 BP. During the AT-period, the vegetation acquired southern taiga features. At the beginning of the period, pine and birch-pine forests continued to dominate. However, also grass-green moss spruce forests were spreading (Fig. 3, Fig. 4). These communities became more prevalent since AT-2 (~7000 BP). Depressions with fertile soils, saturated by lowing water, grew birch-black alder and spruce-black alder forests with elm and hazelnut, as well as lush grasses (Angelica sylvestris, Fillipendula ulmaria, Bistorta oficinalis, Fabaceae, Geum rivale, Humulus lupulus, Liliaceae, Urtica, Polypodiaceae, etc.). Also Alnus incana, Sorbus aucuparia, Viburnum opulus, Frangula alnus, Lonicera, Ribes and Salix have been encountered in these forest communities. The birch took part in coniferous forests and formed post-pyrogenic birch forests as well as birch-grass-moss communities, growing on eutrophic mires. Fires affected pine forests especially in dry habitats, as indicated by the Zamoshye pollen diagram (Fig. 1): The percentage of Pinus sylvestris pollen decreased, whereas the percentage of Betula sect. Albae pollen increased. Also pollen of Chamaenerion angustifolium and coal particles is occasionally encountered. Shallow-water zones continued to overgrown by aquatic and mire plants (Hydrocharis Nuphar, Triglochin and Menyanthes trifoliata were added to the taxa identiied earlier). At irst shallow reed and reed-sedge mires were common close to the shoreline; later they were succeeded by grass-Sphagnum fens. Atlantic period was the most favorable time for people’s lives. This contributed to the presence of many kilometers of shoreline with high, dry ridges, as well as an abundance of plant resources, game animals, birds and ish. The Subboreal period (SB: 4900–2500 BP) began with an abrupt cooling event, with a drop in humidity to a minimum around 4500 BP. It determined the course of subsequent environmental change. According to climatic reconstructions from seven pollen diagrams for the Lake Onega basin, July temperatures were 0.5–1° lower, January temperatures 1–2° lower and precipitation 50 mm/year lower than at present (Elina et al., 1984, Filimonova & Klimanov 2005). Since SB-2 (4200 BP) temperatures 68 Reports of the Finnish Environment Institute 40 | 2014 began to rise again, within the same range as during SB-1. However, mean annual precipitation was smaller. Climate was the driest during SB-1 (4700–4200 BP) and after 3900 BP (Fig. 3). The regression of Lake Onega as well as smaller water bodies is consistent with the cooling and decreased precipitation during the early SB-period. At the same time, there was a drop in groundwater levels, including in the mires, where woody communities became common. During the middle-Subboreal transgression, moisture-loving plants reappeared, as indicated by the peat stratigraphy of Zamoshye Mire (Elina & Filimonova 1999, Elina et al. 1999). The overall reduction of water level in the Lake Onega has led to an increase in land area. A signiicant cooling and reducing the humidity of the climate caused the gradual replacement of southern taiga forests on middle-taiga forests. During the Subboreal period, spruce and pine-spruce green moss forests were common (Fig. 3, Fig.4). They occupied lacustrine glacial plains and selkä slopes Broadleaved species were present, although they were more common in moist birch-black alder and spruce-black alder forests. By the end of the period, their contribution to the forest composition had decreased. Corylus avellana, Populus tremula, Sambucus racemosa, Sorbus aucuparia, Viburnum opulus and Ribes occurred in the undergrowth. Pine forests with dwarf shrub, green moss and lichen grew on rocky ridges. Birch took part in coniferous forests, although it formed post-pyrogenic birch forests and played a leading role in the afforestation of mires. Distinguished in the grass cover are several loristic groups characteristic of forests and forest edges with moist and fertile soils (Urtica, Thalictrum and Polypodiaceae), moist communities growing at the periphery of mires (Filipendula ulmaria, Bistorta oficinalis and Geum rivale) and meadow-like moist (Parnassia palustris and Cyperaceae) and dry communities (Chamaenerion angustifolium, Galium, Potentilla, Ranuculaceae, Fabaceae and Liliaceae). Eutrophic grass mires, one of which is 2770±60 years old, succeed coastal aquatic and wetland plant thickets. Mires became common towards the end of the period. The development of meadows and meadow-like communities is indicated by the considerable amount of grass pollen and the pollen content in the pollen diagrams (see Fig. 1). Climate, the formation of new territories and the abundance of various food resources and forests with a variety of useful plants were favorable for living and the establishment of permanent settlements. During the Subatlantic period (SP: 2500 BP – Present) the shoreline of the Zaonezhye Peninsula acquired its modern shape and landscapes. These landscapes have been affected by both natural and anthropogenic factors. During the SA-period the climate became colder than in the two previous periods. In the beginning, July temperatures were 1°C lower, January temperatures 2°C lower and precipitation 50 mm/year lower than at present. Both the temperature and the precipitation luctuated simultaneously (Fig. 3). The most considerable warming event took place during the SA-2 (1800–800 BP) in the Viking epoch, especially around 1800 BP and during the Little Climatic Optimum in the Middle Ages (1100–1000 BP) when July temperatures were 1.5°C higher, January temperatures 2°C higher and precipitation 75 and 50 mm/year higher, respectively. The SA-3 (the past 800 years) began with a global cooling. In their coolest, around 700 BP, July temperatures were 1–1.5° lower, January temperatures 1–2°C lower than at present. Precipitation was as it is today or smaller by 50 mm/ year. Other cooling events occurred around 500 BP, 200 BP and a little more than 100 BP, while warming events took place around 600 BP, 300 BP and 170–150 BP. The lat- Reports of the Finnish Environment Institute 40 | 2014 69 est warming event began towards the middle of the 20th century (Klimanov & Elina, 1984, Filimonova & Klimanov 2005). A rise in atmospheric humidity caused increased of groundwater level, including in the mires. At that time the moisture-loving mire communities became more common, peat accumulation rate increased and the degree of peat decomposition decreased (Elina & Filimonova 1999, Kuznetsov et al. 1999). During the irst part of SA-period, middle taiga spruce forests dominated (Fig. 3), especially those were widespread on the gently sloping moraine plains of selkä Zaonezhye Peninsula (Fig. 4). Pine forests were more common in the western esker area. Black alder and black alder-spruce forests with a lush grass cover grew between selkäs and in topographic depressions with good stream moistening. Birch took part in the above forests. It also formed tall-grass and pyrogenic birch forests as well as played a part in the afforestation of mires. Broad-leaved species (Acer, Ulmus and Tilia) grew on more fertile soils. In the second part of SA-period, especially during the past 1000 years, the amount of coniferous forests has decreased and the amount of small-leaved forests has increased. Especially spruce forests have declined (Fig. 3). This has been largely due to agricultural development. Spruce forests growing on fertile soil were cut and burned for use as farmland. Pine has been used as building material and irewood as well as for charcoal. As a result of intensive human activities, most primeval forests have disappeared and been replaced by settlements, meadows, pastures, arable land and secondary forests. Abandoned agricultural land is now overgrown with birch, aspen and grey alder (Alnus incana). The effects of human activities are relected in the spore and pollen diagrams. There is a decrease in the proportion of pollen from coniferous plants, especially Picea, as well as an increase in the amount and diversity of grass pollen. Also coal particles are present. Pollen of species adapted to secondary habitats (Chenopodium album, Ch. rubrum, Ch. polyspermum, Chamaenerion angustifolium, Potentilla, Ranunculus, Artemisia and Poaceae) has become more common. Pollen of ruderal plants (Rumex, Urtica, Potentilla, Galium, Plantago, Apiaceae, Geraniaceae and Chenopodiaceae), segetal weeds (Asteraceae, Centaurea, Cichoriaceae, Fabaceae, Caryophyllaceae and Lamiaceae) and cereals (Cerealia) also occurs. These changes in the spore and pollen spectra suggest that agricultural activities on Zaonezhye Peninsula began about 1100-900 BP. This conclusion is also supported by the radiocarbon dates 1140±50 BP and 950±110 BP obtained from the Moshguba and Shlyamino Mire deposits (Lavrova et al., 2007). Obtained data are in good agreement with the date 1060±60 BP for the beginning of agriculture in the vicinities of Essoila village, Syamozero Lake, on the Onega-Ladoga isthmus (Ekman & Zhuravlev 1986). According to reconstructions from Alleröd to the present, the dominant vegetation on Zaonezhe Peninsula follows the sequence: periglacial steppe-like (Artemisia, Chenopodiaceae, Poaceae, etc.) and tundra (Betula nana, Salix, Ericales, Dryas, Saxifraga, Carex, Bryales) palaeocommunities (PC) [AL, DR3: 11800–10300 BP] → forest-tundra: open birch woodlands (with some pine and alder) combined with dwarf shrub moss tundra and Artemisia-Chenopodiaceae-Varia PC [ -1,2: 10300–9700 BP] → northern taiga: light birch and pine-birch forests [P -2: 9700–9300 BP] → light birch-pine and pine forests [ -1: 9300–8900 BP] → mid taiga: pine and birch-pine forests ДB -2,3: 8900–8000 BP] → southern taiga: pine, pine-birch and birch-black alder forests with broad-leaved species and hazel (Qm), spruce [ -1: 8000–7000 BP] → spruce, pinespruce, birch- and spruce-black alder forests with Qm [ -2,3: 7000–4700 BP] → spruce, pine-spruce, birch-black alder forests with Qm and spruce forests with black alder and elm [SB: 4700–2500 BP] → mid taiga (with elements of the south taiga): spruce, pine-spruce-pine and spruce-black alder forests with present of Qm [SA-1,2: 70 Reports of the Finnish Environment Institute 40 | 2014 2500–1300 BP] → pine, spruce-pine and spruce-black alder forests with present of elm and lime, as well as secondary forests dominated with birch and grey alder [SA-2,3: 1300 BP – 0 yrs]. The diversity natural patterns of Zaonezhye are a result of its geological evolution and climate history. Its carbonate and shungite rocks, diverse landforms and Quaternary deposits of various grain sizes have provided diverse habitats for species and communities in different light, moisture, heat and mineral conditions. These and other natural features of Zaonezhye contributed preserving individual species and communities (spruce and lime forests, black alder fens, and fens with black alder and spruce) that existed during the period of climatic optimum. Tilia cordata, Ulmus laevis and U. scabra are encountered on mainland Zaonezhye and on the islands of Zaonezhye. Nemoral, herbaceous plant species grow in areas with fertile soils (e.g. Kuznetsov 1993, Kravchenko et al. 1993). Relicts of the cold Late Glacial period include Helianthemum nummularium, which is found on Bolshoi Lelikovsky Island (Kuznetsov 1997). In Karelia, pollen of Helianthemum nummularium occurs in Late Glacial deposits of some sections (Demidov & Lavrova 2001, Lavrova 2011). Nowadays the northern limit of the species’ distribution extends from the Åland Islands to the southwestern coast of Finland. Only ive Helianthemum nummularium habitats are known to the north or east: two in Finland, two in Russian Karelia (northern shore of Janisjärvi Lake and Zaonezhye) and one in Cape Tury, Kola Peninsula (Vasari & Vasari 1999, Kravchenko 2007). REFERENCES DОЦТНШЯ, I.N. 1993. . . ДVКrЯОН МХКв sЭrЮМЭЮrО КЧН НОРХКМТКЭТШЧ ЩКЭЭОrЧ ШП CОЧЭrКХ KКrОХТКЖ. − IЧ: PrШЛХОЦs ТЧ ЭСО PrОМКЦЛrТКЧ РОШХШРв ШП KКrОХТК. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 127–151. (IЧ Russian). DОЦТНШЯ, I.N. 2005. . . ДDОРrКНКЭТШЧ ШП ЭСО ХКsЭ РХКМТКЭТШЧ ТЧ LКФО OЧОРК ЛКsТЧЖ. − IЧ: GОШХШРв КЧН МШЦЦОrМТКХ ЦТЧОrКХs ШП KКrОХТК. IssЮО 8. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 134–142. (IЧ RЮssТКЧ). 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Reports of the Finnish Environment Institute 40 | 2014 73 Black alder swamp in Klimenetsky Island (Photo Tapio Lindholm). 74 Reports of the Finnish Environment Institute 40 | 2014 1.6 Nature protected areas in Zaonezhye Denis Maksimov*, Philip Uchuvatkin*, Ivan Kiprukhin**, and Anna Volkova*** * Directorate for regional protected areas of the Republic of Karelia 66 Rigachin St., 185005, Petrozavodsk, Karelia, Russia E-mail: oopt@karelia.ru ** Ministry of Nature Management and Environment of the Republic of Karelia 2/24 Andropov St., 185035, Petrozavodsk, Karelia, Russia E-mail: ecopetr@karelia.ru ***Petrozavodsk State University 33 Lenin prospect, 185035, Petrozavodsk, Karelia, Russia Introduction At present there are three regional nature reserves and 19 regional nature monuments on Zaonezhye Peninsula with a total area of 2500 ha (Table 1). In addition, the federal Kizhi zoological reserve (zakaznik) covers 50 000 ha in the southeastern part of the peninsula. Within its boundaries lie the Kizhi open-air museum and its buffer zone as well as the regional nature monuments “Yuzhniy Oleniy Island”, “Wetland by the village of Boyarschina”, “Wetland by Petrikov’s Bay” and “Wetland Zamoshye”. Overview of protected areas in Karelia On the whole there are 137 regional protected areas in the Republic of Karelia (as of 1st November 2014). These protected areas cover 391 600 ha, or 2.17% of the republic, and include the Valaam nature park (24 700 ha) as well as 31 nature reserves (zakazniks) and 105 nature monuments. The nature reserves consist of 15 landscape reserves (242 800 ha), one marine reserve (72 900 ha), 11 botanical reserves (2 100 ha) and four hydrological reserves (6 700 ha), while the nature monuments comprise 64 protected mires (31 600 ha), nine hydrological monuments (over 6 000 ha), 10 geological monuments (2 400 ha), three landscape monuments (2 300 ha) and 19 botanical monuments (over 100 ha). Overall nature reserves (75% of which are landscape reserves) constitute 82.86% of the total area of regional protected areas in the Republic of Karelia, whereas nature monuments make up 10.83% and nature parks 6.31%. Buffer zones have been designated around the protected areas. By imposing restrictions to land use, these zones shield protected areas from negative human impact. In the Republic of Karelia, 33 regional protected areas (with a total area of 78 000 ha) are Reports of the Finnish Environment Institute 40 | 2014 75 accompanied by 5 600 ha of buffer zones on land. For 15 protected areas, the extent of the buffer zones has not been speciied. In the Republic of Karelia, regional protected areas are established in accordance with the Regional land-use plan of the Republic of Karelia, approved by the government of the republic (Scheme 2012, Regulation 2014). In justiication materials to this document, there are two lists of new protected areas to be established by 2030: A list of planned protected areas, for which the necessary documents have been prepared (Annex 1), and a list of perspective protected areas (Annex 2). The irst list consists of protected areas to be established in the irst stage. For these protected areas, the necessary ecological and economical impact assessments have been prepared and presented to the regional authorities. These assessments include detailed descriptions of ecological, social and economic impacts of the protected areas as well as their borders, areas and proposed protection regimes. At present there are eight planned protected areas with a combined area of 264 890 ha, or 1.5% of the total area of the Republic of Karelia. These include the nature reserves Chukozero, Gridino (in Loukhi municipality), Maslozero, Varozero, Yangozero, Yupauzhsuo and Zaonezhsky as well as the Vargachnoe-Korbozerskoe nature monument. Two regional protected areas were established in 2013: Gridino landscape reserve (8 400 ha; Kemi municipality) and Kumi-Porog nature monument (3 400 ha; Kalevala municipality). In addition, the Institute of Biology of the Karelian Research Centre of the Russian Academy of Sciences has conducted ield studies on the mire systems of Yupauzhsuo and Kepasuo (Kalevala municipality) and prepared the necessary documents for the establishment of the Yupauzhsuo nature reserve. The second list consists of perspective protected areas. These areas have high conservation value, for example habitats of regionally or nationally red-listed species. However, more detailed information is needed for the establishment of these protected areas. In the Regional land use plan there are altogether 49 perspective protected areas that cover a total area of 1 192 900 ha. With the aim of developing the network of protected areas in Karelia and the Barents Euro-Arctic Region, in 2012 the Karelian Research Centre of the Russian Academy of Sciences conducted ield studies and an ecological impact assessment of the landscapes, lora and fauna on Zaonezhye Peninsula, with funding from the Ministry of Natural Resources and Environment of the Republic of Karelia. Based on these studies as well as existing information, the Karelian Research Centre has prepared the ecological impact assessment of the Zaonezhskiy landscape reserve (zakaznik). Protected areas on Zaonezhye Peninsula and its adjacent islands The Klim-Gora nature monument is the largest existing regional protected area on the peninsula. It is one of the most picturesque parts of Zaonezhye Peninsula where Mount Klim rises 90 m above Lake Onega. The nature monument was established for the preservation of glacioluvial landforms in their natural state, as well as for tourism and recreation. Another geological monument worth mentioning is the Shunga outcrop, which is the only large outcrop of shungite rocks in the world. It is part of the Kizhi Skerries group of geological monuments, 12 km east of the Kizhi Islands, which also includes Yuzhniy Oleniy Island in northwestern Lake Onega. Hydrological nature monuments include two water seeps: Tri Ivana and Solyanaya Yama. The Tri Ivana water seep is irst mentioned in literature in 1861. It is located two kilometres north of the abandoned village of Karasozero, 22 km from the village of Velikaya Guba. The water seep resembles a funnel, 1-1.5 m in diameter and 0.5-0.7 m in depth, from where approximately one litre of water lows out every second. 76 Reports of the Finnish Environment Institute 40 | 2014 It is near a small chapel, fenced with a stone dyke, and it has been covered with a wooden construction. The Solyanaya Yama water seep is unique for Karelia. It is located in the backswamp depression of the river Sudma, two kilometres north of the village of Velikaya Guba. In the past, local people collected water from the seep to make salt. A wooden construction has been built inside the well. However, nowadays the wooden construction is dilapidated and the 6-m-deep well is half full of silt. The water’s salt concentration is 4 g/l at the surface and it increases deeper in the well. Due to the large quantities of hydrogen sulide (32 mg/l), sodium chloride water is used as medicinal mineral water. Nature reserves have been created to preserve unique plantations of broadleaf trees, including the state nature reserve “Highly productive stands of larch and common alder” as well as the nature monuments “Natural stands of small-leaved lime and Scotch elm (Ulmus glabra)”, “Natural stands of Scotch elm (Ulmus scabra)”, “Plantation of Siberian pine – 64” and “Plantation of Siberian pine – 65”. Scotch elm, small-leaved lime and Acer platanoides reach their northern limits in Zaonezhye. Protected areas on the peninsula also include the Anisimovschina botanical reserve, created in 1984. This reserve is a unique natural refugium for the curly (Karelian) birch, which is a calling card of both the peninsula and Karelia as a whole. Wetlands cover only 5% of the total area of forest land on Zaonezhye Peninsula (See Chapter 2.3). However, nearly half of the protected areas in Zaonezhye are wetlands. These nature monuments represent wetlands of different type and genesis. In addition, wetland ecosystems are home to berries as well as rare and red-listed plant species. Planned protected areas on Zaonezhye Peninsula Several regional protected areas are planned to be established on Zaonezhye Peninsula. In 2009 the Karelian Research Centre of the Russian Academy of Sciences carried out a scientiic feasibility study for the development of the protected area network in the Republic of Karelia (Feasibility study 2009). However, its irst priority was the establishment of another planned protected area, the Zaonezhskiy nature reserve, which covers nearly 110 000 ha of unique esker landscapes in the northern part of the peninsula. In 2011 the Karelian Research Centre proposed a preliminary area and borders for the Zaonezhskiy nature reserve, which were included in the inal version of the Land-use plan of the Republic of Karelia (Scheme 2012). The nature conservation NGO “SPOK” is proposing the largest protected area in Zaonezhye, the Zaonezhsky nature park. It covers the entire southeastern part of the Zaonezhye Peninsula as well as parts of the peninsulas Sjar and Lizh – altogether 115 000 ha. An alternative way to protect rare, red-listed and indicator species in the southeastern part of the peninsula is to establish six nature monuments, covering 14 500 ha (Fig. 1). These areas were identiied during a multidisciplinary expedition, arranged by the Barents Protected Area Network (BPAN) project (Lindholm et al. 2014) REFERENCES FОКsТЛТХТЭв sЭЮНв 2009. . . ДFОКsТЛТХТЭв sЭЮНв ШП ЭСО ЩrШЭОМЭОН КrОК ЧОЭаШrФ ТЧ ЭСО RОЩЮЛХТМ ШП KКrОХТК. KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 112Щ.Ж (ТЧ Russian). LТЧНСШХЦ, T., JКФШЯХОЯ, J. & KrКЯМСОЧФШ, A. (ОНs.) 2014. BТШРОШРrКЩСв, ХКЧНsМКЩОs, ОМШsвsЭОЦs КЧН sЩОМТОs ШП ГКШЧОгСвО PОЧТЧsЮХК, ТЧ LКФО OЧОРК, RЮssТКЧ KКrОХТК. RОЩШrЭs ШП ЭСО FТЧЧТsС EЧЯТrШЧЦОЧЭ IЧsЭТЭЮЭО 2014/40:1-360. Reports of the Finnish Environment Institute 40 | 2014 77 RОРЮХКЭТШЧ 2014. . 7 2014 № 88- . 6 2007 № 102- . . . ДRОРЮХКЭТШЧ ШП ЭСО GШЯОrЧЦОЧЭ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК 07.04.2014, №88-P. OЧ ЭСО МСКЧРОs ЭШ ЭСО RОРЮХКЭТШЧ ШП GШЯОrЧЦОЧЭ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК 06 .07.2007 № 102- . PОЭrШгКЯШНsФЖ. (IЧ RЮssТКЧ). СЭЭЩ://РШЯ.ФКrОХТК.rЮ/LОРТsХКЭТШЧ/ХКаЛКsО.СЭЦХ?ХТН=11393 SМСОЦО (2012). К , 06.07.2007 № 102- . . . ДSМСОЦО ШП SЩКЭТКХ ЩХКЧЧТЧР ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК. 06.07.2007 № 102- . PОЭrШгКЯШНsФЖ. (IЧ RЮssТКЧ). СЭЭЩ://ааа.РШЯ.ФКrОХТК.rЮ/PШаОr/CШЦЦТЭЭОО/BЮТХН/PХКЧ/ SPOK 2013. , « » NGO “SPOK”. ДDШМЮЦОЧЭКЭТШЧ ШП ЭСО МШЦЩХОб ОМШХШРТМКХ ТЧЯОЧЭШrв УЮsЭТПвТЧР ОsЭКЛХТsСЦОЧЭ ШП ЭСО ГКШЧОгСsФв SЭКЭО NКЭЮrО PКrФЖ. 2013. PОЭrШгКЯШНsФ.108 Щ. (IЧ Russian). Table 1. Regional protected areas on Zaonezhye Peninsula Category: NR – Nature reserve, NM - Nature monument 78 Date of № Name of protected area Category Proile Area, ha establishment 1 Highly productive larch and common alder stands NR Botanical 110.4 15/06/1976 2 3 4 5 Lake Kovshozero Yuzhniy Oleniy Island NR NR NM Shunga outcrop NM 60 5.4 75 10 20/07/1984 20/07/1984 29/07/1981 29/07/1981 6 Plantation of Siberian pine – 64 NM Botanical Botanical Geological Geological Botanical 2.4 29/07/1981 7 Plantation of Siberian pine – 65 NM Botanical 1.9 29/07/1981 8 Natural stands of smallleaved lime and Scotch elm (Ulmus scabra) NM Botanical 5 29/07/1981 9 Natural stands of Scotch elm (Ulmus scabra) NM Botanical 23 29/07/1981 10 Solyanaya Yama water seep NM Hydrological 11 Tri Ivana water seep NM Hydrological 125 21/10/1993 12 Wetland Konye №402 NM 86.2 24/05/1989 13 Wetland Razlomnoe NM Wetland Wetland 39 24/05/1989 14 15 Wetland Pigma №390 24/05/1989 24/05/1989 Wetland Kalegubskoe №3061 Wetland Wetland Wetland 525 204 16 NM NM NM 168 29/12/1997 17 Wetland by Lake Lelikozero №3063 NM Wetland 200 29/12/1997 18 Wetland by River Lelrechka NM Wetland 95 29/12/1997 19 20 Wetland Zamoshye №483 NM NM Wetland Wetland 178 43 29/12/1997 29/12/1997 21 Wetland by the village of Boyarschina NM Wetland 24 29/12/1997 22 Klim-Gora NM Landscape 617 21/10/1993 Anisimovschina Wetland Pala №400 Wetland by Petrikov’s Bay Reports of the Finnish Environment Institute 40 | 2014 20/07/1984 Fig 1. Location of the existing and planned protected areas of Zaonezhye Peninsula. Reports of the Finnish Environment Institute 40 | 2014 79 80 Reports of the Finnish Environment Institute 40 | 2014 2 Biomes and biogeography of Zaonezhye Peninsula area 2.1 Modern landscapes of Zaonezhye Peninsula Maria S. Bogdanova Institute of Water Problems in the North of the Karelian Research Center of Russian Academy of Sciences. 50 Alexandra Nevskogo St., 185003 Petrozavodsk, Karelia, Russia E-mail: mari-mb@mail.ru Zaonezhye is located on the northern shore of Lake Onega. It includes Zaonezhye Peninsula and the adjacent Kizhi Archipelago. According to the biogeographical classiication of Northwest Russia, Zaonezhye belongs to the Karelian middle taiga region of the Eastern European taiga zone (A. Isachenko 2008). Selkä terrain, plains and drained and cultivated peatland dominate the landscape. The selkäs are elongated ridges of consolidated crystalline rocks, whereas the plains consist of boulder, sandy loam and loam or boulder-free sand and loam. In the course of the history, a succession of human communities with different economic activities, agricultural practices and socioeconomic conditions exerted a considerable inluence on the modern landscapes of the region. I have divided the landscape history of Zaonezhye into eight stages from the Mesolithic period to the present, based on the analysis of available data (Bogdanova 2011). To assess the present landscapes of Zaonezhye, basic features of the landscape are divided based on landscape dynamics into site features (relatively stable properties of relief and underlying rocks) and long-term states (more dynamic characteristics of vegetation and soils). Landscape areas are described using three basic indices: 1) landform or morphological features of the relief, 2) composition of underlying (soil-forming) rocks in the uppermost (1 m) layer and 3) moisture regime (drainage conditions). Natural processes as well as human activities have inluenced the landscape dynamics, which consists of different states of different lengths (G. Isachenko 1998, 2007). The landscapes of Zaonezhye were studied between 2005 and 2013. Basic landscapes were described during ield studies. The resulting 1050 landscape descriptions formed the basis for the database “Landscape structure of the Zaonezhye hydrographic province, Republic of Karelia” (Bogdanova 2014). Large-scale maps show key areas of the most representative landscapes. I have developed a classiication of basic landscapes in Zaonezhye and prepared a 1:200 000 scale landscape map. The map shows 775 contours and 32 different types of landscapes, including 16 landscape combinations. Contrasting landscapes are combined if the map scale is too large to show small-scale differences when landscapes succeeded one another at determined intervals. In addition to natural landscapes Reports of the Finnish Environment Institute 40 | 2014 81 (unaffected by human activities), the map shows 14 types of landscapes modiied by long-term agricultural use and/or drainage as well as three artiicial landscapes. The total area studied is 1964 km2, including the inland water bodies and islands of Zaonezhye Peninsula (but excluding Bolshoi Klimenetsky, Yernitsky and Bolshoi and Maly Lelikovsky Islands). The landscape map provides a reliable tool for describing the spatial distribution of natural complexes in Zaonezhye and assessing their present condition. The spatial distribution of the landscapes and their long-term vegetation and soil types are shown in Table 1. When vegetation and soil cover are fragmented and diverse, only dominant vegetation and soil types are described. Table 1. Landscape classiication in Zaonezhye. Landscape sites Long-term states Dominant vegetation Area Dominant soil types km2 % Combinations of selkä ridges and depressions (The elongated selkä ridges consist of Proterozoic crystalline rocks, such as gabbro-dolerite, shungite shale, tuff schist and tufite, covered by moraine and diluvium. The depressions between the ridges are covered by boulder, sandy loam and loam, or a thin layer of peat.) 1. High selkä ridges (relative height 40–90 m) with lat tops and stepped slopes, covered by a layer of eluvium-deluvium and moraine (up to 1.0–1.5 m) and peat (up to 1 m). Rocky scarps are up to 30 m high and their lower parts are covered by coarse clastic material. Pine- and spruce-dominated Vaccinium myrtillus-Calamagrostis arundinacea forests on the ridge tops and slopes; Spruce-dominated forests with a large proportion of pine, birch and aspen; Aspen-dominated forests with spruce, birch, Vaccinium myrtillus and green moss; Bogs in depressions and on the slopes Primitive 75.0 soils, Leptosols, Cambisols, Peat bog, Soil absent 3.8 2. High, rugged selkä ridges (relative height 30–80 m) with numerous rock exposures and cliffs (relative height 30 m). The ridge tops and slopes are covered by a layer of discontinuous eluvium-deluvium and moraine (up to 0.5 m). Sparse pine forests with Vaccinium vitis-idaea and lichen, as well as rocky wasteland on the ridge tops; Birch- or pine-dominated forests with green moss, Vaccinium myrtillus, V. vitis-idaea and lichen on the slopes; Bogs in depressions Primitive 85.5 soils, Leptosols, Peat bog, Soil absent 4.4 3. Poorly structured selkä ridges (relative height up to 20 m) with few rock exposures and a layer of discontinuous eluvium-deluvium and moraine (up to 0.5 m) Sparse pine forests with green moss, Vaccinium vitis-idaea, dwarf shrubs and lichen, as well as rocky wasteland on the ridge tops; Primitive, 37.5 Leptosols, Soil absent 1.9 Combinations of contrasting landscape sites, dominated by drained slopes with mineral soils, where differences in elevation are more than 10 m 4. Hills and ridges consisting of sandy loam and boulder (relative height up to 20 m), combined with plains formed of sand, clay and boulder and sandy loam, as well as thin peatlands 82 Reports of the Finnish Environment Institute 40 | 2014 Pine-, spruce- or birch-dominated forests with green moss, Vaccinium myrtillus, dwarf shrubs and Calamagrostis arundinacea; Former clearcut areas covered by Calamagrostis arundinacea and secondary mixed forests, developed through natural succession; Different types of mires from bogs to fens in depressions Leptosols, 86.3 Cambisols, Peat bog 4.4 5. Hills and ridges consisting of sandy loam and boulder, often with crystalline rock exposures, combined with undulating plains formed of consolidated boulder, sand and sandy loam, as well as thin peatlands Sparse pine forests with dwarf Leptosols, 46.5 shrubs, green mosses and lichen on Cambisols, tops of eskers; Peat bog Spruce-, aspen- or birch-dominated forests with pine, green mosses, Vaccinium myrtillus, dwarf shrubs and Calamagrostis arundinacea; Clearcut areas covered with Calamagrostis arundinacea, Rubus idaeus and Chamaenerion angustifolium; Secondary mixed forests, developed through natural succession of former clearcut areas on the slopes and in depressions; Transitional and raised bogs in depressions 2.4 6. Elongated hills and ridges consisting of sand and pebble or sand and boulder, combined with peatlands in depressions. Often there are also plains consisting of boulder, pebble and sand. Birch- or pine-dominated forests with dwarf shrubs and green moss; Clearcut areas in different stages, covered with Calamagrostis arundinacea and Chamaenerion angustifolium; Fens and transitional bogs in depressions 0.9 Podzol, Surface podzol, Peat bog 16,9 Combinations of contrasting landscape sites, dominated by drained slopes with cultivated mineral soils, where differences in elevation are more than 10 m 7. Cultivated hills and ridges consisting of sandy loam and boulder (relative height up to 20 m), commonly combined with plains formed of sand and clay or boulder, sand and loam, as well as thin peatlands Grassland (Poaceae and herbaceous meadows), arable land and abandoned meadows, which have become overgrown with trees; Young birch, aspen and pine forests with herbaceous plants and spruce; Fens and transitional bogs in depressions Cambisols- 21.1 old arable soils, Peat bog 1.1 8. Cultivated hills and ridges (eskers) consisting of shungitic and shungite-bearing pebble, boulder and sand, combined with cultivated plains formed of boulder, pebble and sand, as well peatlands in depressions Grass and herbaceous meadows, arable land, overgrown meadows; Young birch, aspen and pine forests with herbaceous plants; Fens and transitional bogs in depressions Shungite cambisolsold arable soils, Peat bog 45.5 2.4 Surface podzol 6.5 0.3 Podzols, Surface podzol, Peat bog 103.43 5.3 Drained plains, dominated by mineral soils 9. Plains formed of boulder-free sand and sandy loam Pine-dominated forests with dwarf shrubs and green moss; Birch-dominated forests with spruce, Vaccinium myrtillus and Calamagrostis arundinacea 10. Plains formed of small boulder, Birch- or pine-dominated forests pebble and sand, often combined with with spruce, Calamagrostis arundinathin peatlands cea, dwarf shrubs and green moss; Fens and transitional bogs 11. Undulating plains and gently sloping ridges on consolidated boulder, sand and sandy loam, often combined with thin peatlands Birch- or aspen-dominated forests Leptosols, 357.2 with pine, spruce, dwarf shrubs, Cambisols, Calamagrostis arundinacea and green Peat bog moss; Young mixed forests with herbaceous plants; Clearcut areas covered with Calamagrostis arundinacea and Chamaenerion angustifolium fens and transitional bogs 18.2 Cultivated drained plains, dominated by mineral soils 12. Cultivated, undulating plains and terraces formed of boulder-free sand and sandy loam (lacustrine-glacial and glacial) Grass and herbaceous meadows, Soddy old 37.7 arable land, overgrown meadows; arable soils Young mixed forests, dominated by birch or aspen, with herbaceous plants and pine 1.9 Reports of the Finnish Environment Institute 40 | 2014 83 13. Cultivated, undulating plains formed of small boulder, pebble and sand (luvioglacial deposits) Grass and herbaceous meadows, Cambisols- 22.4 arable land, overgrown meadows; old arable Mature mixed forests, dominated soils by birch or aspen, with herbaceous plants and pine; Young mixed forests, dominated by spruce, birch or aspen with herbaceous plants and Calamagrostis arundinacea 1.1 14. Cultivated, undulating plains and gently sloping ridges on consolidated boulder, sand and sandy loam (moraine) Grass and herbaceous meadows, arable land, overgrown meadows; Young forests dominated by birch, common alder (Alnus glutinosa) and bird cherry (Padus avium) with herbaceous plants Mature spruce or aspen dominated forests with pine, herbaceous plants and Calamagrostis arundinacea Cambisols- 120.9 old arable soils 6.2 Combinations of plains with different soil moisture contents 15. Permanently saturated plains, covered with boulder-free sand, quite often with a thin layer of peat, with a mildly undulating and gently sloping relief. These landscapes also include small peatlands. Forests dominated by pine, birch and common alder with herbaceous plants, sedges, horsetail and Sphagnum; Fens and transitional bogs Humic gley, Peaty gley, Peat bog 9.9 0.5 16. Permanently saturated plains, covered with boulder-free clay and sandy loam, quite often with a thin layer of peat, with a mildly undulating relief. These landscapes also include small peatlands. Birch-, aspen- or pine-dominated forests with common alder, herbaceous plants and Vaccinium myrtillus; Birch-, pine- or common alder-dominated forests with herbaceous plants, sedges and Sphagnum; Birch forests with meadowsweet (Filipendula) and sedges; Lowland fens and transitional bogs Humic gley , Peaty gley, Peat bog 88.6 4.5 17. Saturated plains, covered with boulder and sandy loam, quite often with a thin layer of peat. These landscapes also include small peatlands and hills, consisting of sand and boulder. Birch, pine and spruce forests with herbaceous plants, Vaccinium myrtillus and Sphagnum; Birch, pine and dwarf shrub forests on the hills; Fens and transitional bogs in depressions Cambisols, 69.6 Gley cambisols, Peaty gley, Peat bog 3.5 18. Drained peatland and artiicially drained plains with a thin layer of peat (up to 0.5 m); often combined with drained plains Birch and pine forests or birch, pine and spruce forests with dwarf shrubs, Sphagnum and herbaceous plants of moist soils Peaty gley, Humic gley, Cambisols 10.3 0.5 Combinations of cultivated sites with different soil moisture contents (plains and low hills) 84 19. Predominantly cultivated, saturated plains, covered with boulder-free clay and sandy loam, quite often with a thin layer of peat. These landscapes include small peatlands and cultivated hills of sand and boulder. Meadowsweet (Filipendula) and sedge-meadowsweet meadows, including those overgrown with willow and birch; Meadows with herbaceous plants, sedges and Sphagnum; Young deciduous forests with herbaceous plants and pine; Grass and herbaceous meadows and deciduous forests with pine growing on the hills; Fens and transitional bogs in depressions Humic 14.2 gley, Peaty gley, Peat bog, Cambisolsold arable soils 0.7 20. Cultivated plains and gently sloping ridges, covered with boulder, shungite-bearing and shungitic sandy loam, often combined with shallow peatlands Arable land, grass and herbaceous meadows, overgrown meadows; Young grey alder and birch forests; Birch-or aspen-dominated forests with pine or spruce, herbaceous plants, Vaccinium myrtillus and green moss; Fens and transitional bogs Shungite cambisolsold arable soils, Peat bog 11.6 Reports of the Finnish Environment Institute 40 | 2014 227.4 21. Cultivated, drained plains and gently sloping ridges covered with boulder and shungitic sandy loam, with crystalline rock exposures. These are often combined with plains formed of boulder-free, sandy loam. Grass and herbaceous meadows, arable land, overgrown meadows; Young small-leaved forests with herbaceous plants; Birch and aspen forests with herbaceous plants, pine and spruce; Meadows of herbaceous plants and sedges, mixed with birch forests with herbaceous plants and sedges of moist soils Cambisols- 34.3 old arable soils, Humic gley 1.7 22. Cultivated, artiicially drained plains, covered with boulder-free clay and sandy loam, as well as paludiied plains with a thin layer of peat. Occasionally there are also cultivated hills of sand and boulder. Grass, tall grass and herbaceous meadows, including overgrown meadows; Meadows with sedges and Sphagnum; Small-leaved forests with herbaceous plants and pine; Fens and transitional bogs Soddy hu- 30.8 mic gley, Peaty gley, Peat bog, Cambisolsold arable soils 1.6 Peatland with a peat layer of more than 0.5 m 23. Oligotrophic raised bogs (peat over 1.5 m thick) Pine-covered Sphagnum-cottongrass-dwarf shrub bogs Raised bog 24.8 soils 1.3 24. Drained oligotrophic raised bogs Pine-covered Sphagnum-cottongrass-dwarf shrub bogs Drained raised bog soils 3.3 0.2 25. Meso-oligotrophic and mesHerb-sedge-Sphagnum bogs, often otrophic peatland (varying thicknesses covered with birch and pine; of peat) Moist birch- or pine-dominated forests with herbaceous plants, sedges and Sphagnum Mesotrophic bog soils 40.3 2.0 26. Drained meso-oligotrophic and mesotrophic peatland Herb-sedge-Sphagnum bogs, often covered with birch and pine; Moist birch- or pine-dominated forests with herbaceous plants, sedges and Sphagnum Drained mesotrophic bog soils 5.00 0.3 27. Drained, cultivated meso-oligotrophic and mesotrophic peatland Grass and herbaceous meadows; Moist meadows with herbaceous plants and sedges following the cessation of agriculture; Moist meadows with herbaceous plants and sedges, including those with birch undergrowth; Birch forests with moist herbaceous plants Drained mesotrophic bog soils and cultivated bog soils 16.0 0.8 28. Mesoeutrophic and eutrophic peatland in lotic depressions; varying thicknesses of highly mineralized peat Sedge and herb-sedge bogs with willow, birch and black alder; Black alder and birch forests with moist herbaceous plants; Reed thicket Boggy fen peat and bog-gley soils 5.5 0.3 Drained and cultivated boggy fen peat and bog-gley soils 122.1 6.2 29. Drained, cultivated mesoeutrophic Grass and herbaceous meadows; and eutrophic peatland Meadows with moist herbaceous plants and sedges following the cessation of agriculture; Birch scrub forests; Birch forests with moist herbaceous plants Sites with relief and grounds transformed by human activities 30. Former peat production areas Peat wasteland in areas affected by ires; Burned moorland with heather Young birch forests Soil absent 3.6 0.2 31. Sand- and gravel-pits Only sparse vegetation during Soil quarrying; absent Young pine and small-leaved forests after the cessation of quarrying 0.5 <0.1 Reports of the Finnish Environment Institute 40 | 2014 85 32. Shungite rock quarries Only sparse vegetation during quarrying; Young small-leaved forests after the cessation of quarrying Soil absent Inland water bodies on the peninsula, excluding Lake Onega bays Total 0.3 <0.1 194.3 10.3 1964 100 Fig.1. Landscape areas of Zaonezhye Peninsula. Numbers indicate l andscape areas: 1. Kosmozero-Putkozero; 2. Dianogorsko-Mizhostrov; 3. Pigmozero; 4. Myagrozero-Lelikovo; 5. Shunga-Kuzaranda; 6. Limozero-Gankovo; 7. Velikaya Guba-Tambitsy; 8. Kizhi Due to the characteristics of the geological structure, the landscape pattern of Zaonezhye is fragmented, including a mosaic of small-scale landscapes. Its landscape contours are typically elongated from northwest to southeast. In Zaonezhye, a total of eight landscape areas are identiied based on recurrent combinations of landscapes (Fig. 1): 1. Kosmozero-Putkozero area, dominated by selkä ridges, cultivated plains and hills 2. Dianogorsko-Mizhostrov area, dominated by selkä ridges 3. Pigmozero area, dominated by luvioglacial sand plains and peatland 4. Myagrozero-Lelikovo area, dominated by moraine plains and peatland 5. Shunga-Kuzaranda area, dominated by cultivated land on shungite and shungite-bearing rocks, as well as drained and cultivated plains and peatland 6. Limozero-Gankovo area, dominated by moraine plains, covered with a thin layer of peat, as well as peatland and drained peatland 7. Velikaya Guba-Tambitsa area, dominated by cultivated plains on moraine, and peatland 8. Kizhi area, dominated by cultivated land on shungite and shungite-bearing rocks. 86 Reports of the Finnish Environment Institute 40 | 2014 Cultivated land makes up a large proportion of the landscapes in Zaonezhye. In the past, it has been one of the most agriculturally developed areas in Karelia. Agricultural development in Zaonezhye began in the 9th and 10th centuries, although natural complexes were most signiicantly transformed in the 19th century. By the end of the 19th century, agricultural development had reached its peak with about 30% of the peninsula cultivated for arable crops or hay. Old arable land is characterized by a well-deined soil horizon, even if the land is no longer cultivated. Normally the horizon is over 15 cm thick. On old arable land, speckled alder, birdcherry and mountain ash dominate the forest cover, whereas the ground cover is characterised by meadow species. The agricultural development of Zaonezhye is characterized by the cultivation of bouldery (moraine and luvioglacial) plains, ridges and hills as well as gently sloping selkäs and relatively steep slopes of (up to 50–70%) crushed stone. Boulders were removed and stored for future use. Local people called these piles rovnitsas. Rovnitsas are a part of the cultural landscape of Zaonezhye, reminding of its agricultural history. It was not until the late 20th century that people began draining bogs here. Until then only small parts of paludiied plains and lowland bogs had been used for cultivating hay. During the past centuries unique cultural landscapes have formed in Zaonezhye where plains, selkä ridges, coniferous and small-leaved forests, dry valley forests, arable land and lakes coexits. Wooden architecture is an inseparable part of the region’s landscape. There are several well-preserved old wooden buildings in Zaonezhye, including 96 architectural monuments (including the famous churches of Kizhi Island), of which 65 are listed buildings. The best example of wooden architecture in Zaonezhye is the Kizhi Pogost with the Church of the Intercession and the Church of the Transiguration. Kizhi Pogost is included in the UNESCO list of World Heritage Sites. Zaonezhye landscapes are transforming: Coniferous and small-leaved forests are maturing. Agricultural land has become overgrown. Cutting areas and abandoned quarries grow scrub forests. Over 20 different dynamic processes have been identiied in different types of landscapes. The following trends are most typical for the region: • The composition and growing stock of pine and spruce forests on selkä ridges have stabilized. • The phytomass and growing stock of young and middle-aged small-leaved coniferous forests in cutting areas have increased. • The phytomass and growing stock of young and middle-aged small-leaved forests and small-leaved coniferous forests on former agricultural land have increased. • Secondary paludiication of reclaimed land is accompanied by the appearance of mesohygrophytes and hygrophytes in the vegetation cover. Vegetation cover is actively overgrow by scrub forests. • Meadows are declining and secondary small-leaved forests are increasing as former agricultural land becomes overgrown with speckled alder, birch, aspen and pine. • Grass and herb-grass communities are succeeded by tall grass-chervil (Anthriscus sylvestris) and tall grass-raspberry (Rubus idaeus) communities. If Zaonezhye landscapes are left without human intervention, the area of both young and mature mixed small-leaved forests as well as small-leaved coniferous for- Reports of the Finnish Environment Institute 40 | 2014 87 ests will increase in the next 50 years. Also the portion of young small-leaved forests on overgrown meadows is expected to increase. A wide range of landscapes on Zaonezhye Peninsula needs protection, including the rapidly disappearing cultural landscapes. Protected areas with different protection regimes should be established to promote nature conservation and environmental tourism in the area. REFERENCES BШРНКЧШЯК, . S. 2011. . . : . ДTСО НОЯОХШЩЦОЧЭ СТsЭШrв КЧН ЭСО ЩrОsОЧЭ МШЧНТЭТШЧ ШП ГКШЧОгСвО’s ХКЧНsМКЩОs: ХКЧНsМКЩО-НвЧКЦТМ sЭЮНвЖ.− IгЯОsЭТвК ШП RЮssТКЧ GОШРrКЩСв SШМТОЭв 143 (2): 23–31. (IЧ Russian). BШРНКЧШЯК, . S. 2014. . . ( ). – ДLКЧНsМКЩО sЭrЮМЭЮrО ШП ЭСО ГКШЧОгСвО СвНrШРrКЩСТМ ЩrШЯТЧМО, RОЩЮЛХТМ ШП KКrОХТКЖ CОrЭТiМКЭО ШП ЭСО ШПiМТКХ rОРТsЭrКЭТШЧ ШП ЭСО НКЭКЛКsО ЧШ. 2014620226 ШП 5.02.2014. (IЧ RЮssТКЧ). IsКМСОЧФШ, . G. 2008. . . , , . ДTСО EКrЭС’s ХКЧНsМКЩО sЭrЮМЭЮrО, sОЭЭХТЧР КЧН ЭСО ЮsО ШП ЧКЭЮrКХ rОsШЮrМОsЖ. – SЭ. PОЭОrsЛЮrР. 320 Щ. (IЧ RЮssТКЧ). IsКМСОЧФШ, G. . 1998. . . ДMОЭСШНs ПШr iОХН ХКЧНsМКЩО sЭЮНв КЧН ХКЧНsМКЩО-ОЧЯТrШЧЦОЧЭКХ ЦКЩЩТЧРЖ. – SЭ. PОЭОrsЛЮrР. 112 Щ. (IЧ RЮssТКЧ). IsКМСОЧФШ, G. A. 2007. LШЧР-ЭОrЦ МШЧНТЭТШЧs ШП ЭКТРК ХКЧНsМКЩОs ШП EЮrШЩОКЧ RЮssТК. – IЧ: LКЧНsМКЩО AЧКХвsТs ПШr SЮsЭКТЧКЛХО DОЯОХШЩЦОЧЭ. TСОШrв КЧН AЩЩХТМКЭТШЧs ШП LКЧНsМКЩО SМТОЧМО ТЧ RЮssТК. MШsМШа, AХОб PЮЛХТsСОr Щ. 144–155. Fig. 2. Flat top of the selkä ridge (Landscape sites 1, Table 1) (Photo Maria Bogdanova). 88 Reports of the Finnish Environment Institute 40 | 2014 Fig. 3. Stepped slope of the selkä ridge (Landscape sites 1, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 89 Fig. 4. Rugged top of the selkä ridge (Landscape sites 2, Table 1) (Photo Maria Bogdanova). 90 Reports of the Finnish Environment Institute 40 | 2014 Fig. 5. Slope of the selkä ridge (Landscape sites 2, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 91 Fig. 6. Cliff of the selkä ridge (Landscape sites 1 and 2, Table 1) (Photo Maria Bogdanova). 92 Reports of the Finnish Environment Institute 40 | 2014 Fig. 7. Poorly structured low selkä ridge (Landscape sites 3, Table 1) (Photo Maria Bogdanova). Fig. 8. Cultivated ridge (esker) consisting of pebble, boulder and sand (Landscape sites 8, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 93 Fig. 9. Arable land on esker, consisting of shungitic pebble and sand (Landscape sites 8, Table 1) (Photo Maria Bogdanova). Fig. 10. Plain formed of boulder-free sand (Landscape sites 9, Table 1) (Photo Maria Bogdanova). 94 Reports of the Finnish Environment Institute 40 | 2014 Fig. 11. Plain on consolidated boulder, sand and sandy loam (moraine) (Landscape sites 11, Table 1) (Photo Maria Bogdanova). Fig. 12. Cultivated plain formed of boulder-free sand (Landscape sites 12, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 95 Fig. 13. Plain formed of small boulder, pebble and sand (luvioglacial deposits) (Landscape sites 13, Table 1) (Photo Maria Bogdanova). Fig. 14. Cultivated plain on consolidated boulder, sand and sandy loam (moraine) (Landscape sites 14, Table 1) (Photo Maria Bogdanova). 96 Reports of the Finnish Environment Institute 40 | 2014 Fig. 15. Overgrown arable land on consolidated boulder, sand and sandy loam (moraine) (Landscape sites 14, Table 1) (Photo Maria Bogdanova). Fig. 16. Plain covered with boulder-free clay and sandy loam (Landscape sites 16, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 97 Fig. 17. Cultivated, artiicially drained plain, covered with boulder-free clay and sandy loam (Landscape sites 22, Table 1) (Photo Maria Bogdanova). Fig. 18. Oligotrophic raised bog (Landscape sites 23, Table 1) (Photo Maria Bogdanova). 98 Reports of the Finnish Environment Institute 40 | 2014 Fig. 19. Mesotrophic peatland (Landscape sites 25, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 99 Fig. 20. Eutrophic peatland (Landscape sites 28, Table 1) (Photo Maria Bogdanova). Fig. 21. Former peat excavations (Landscape sites 30, Table 1) (Photo Maria Bogdanova). 100 Reports of the Finnish Environment Institute 40 | 2014 Fig. 22. Sand- and gravel-pit (Landscape sites 31, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 101 Fig. 23. Shungite rock quarry (Landscape sites 32, Table 1) (Photo Maria Bogdanova). 102 Reports of the Finnish Environment Institute 40 | 2014 2.2 Landscape structure of Zaonezhye Peninsula Vladimir Karpin Forest Research Institute of the Karelian Research Center of Russian Academy of Sciences 11 Pushkinskaya St., 185610 Petrozavodsk, Karelia, Russia E-mail: landscapeexplorer@gmail.com Introduction Zaonezhye Peninsula is characterised by a complex landscape structure as well as a diverse forest cover. According toVolkov et al. (1990), Gromtsev (2008) and Gromtsev (2013), there are two contrasting types of geographical landscapes on Zaonezhye Peninsula (Fig.1): (1) Paludiied lacustrine and lacustrine-glacial plains occur in the east, where forests are dominated by spruce (II in Fig 1), while (2) paludiiedtectonic-denudation ridge (selkä) landscapes occur in the west,where forets are dominated by pine (I in Fig.1). The landscape structure of Zaonezhye consists of large geomorphological areas, or geographical terrains. These geomorphologically uniform areas cover approximately 10 000 hectares (or over 90 % of the area). The geographical terrains have a homogeneous composition of Quaternary sediments as well as uniform hydrographic and soil conditions. As a consewuenve, they show a constant succession of forest and mire complexes on the mesoscale, covering areas of 10–100 ha (Gromtsev 2000, 2008). Fig. 1. Geographical terrains of Zaonezhye Peninsula.Image and fax viewing software. Reports of the Finnish Environment Institute 40 | 2014 103 Results The tectonic-denudation landscape of Zaonezhyevaries at the sub-landscape level (Selkä landscapes2013). Three types of geographical terrains have been identiied: Moderately paludiiedtectonic-denudation ridge terrain, dominated by pine habitats (No. 1 in Fig. 1) This dominant terrain type covers 40 % of the area (Fig. 2). Its relief is a result of multiple tectonic movements that have created a system of northwest-trending subparallel folds, comprising ridges (selkäs), steep slopes and steplike scarps. The long and rocky ridges correspond to synclines, whereas the straight, narrow and shallow basins and bays of Lake Onega are consistent with the anticlines. Thefold structure is broken by a system of stepped strike-slip faults.Quaternary sediments are represented by a thin moraine cover. On the ridge tops, moraine is either dozens of centimeters thick or completely absent, while on the slopes and in the depressions between the ridges moraine can be up to 2 m thick. Altitudes range from 33 m to 202 m, while altitudes of adjacent landforms vary between 20 m and 50 m above sea level. Overall, mires cover less than 20% of the terrain. Open mires account for 5%. Mires are predominantly mesotrophic or oligotrophic. Hydrographically, the percentage of lakes is relatively high (28%). The network of rivers and lakes shows a pattern of small streams and small lakes, which contributes to the fragmentation of the forest cover. The soil cover is dominated by two soil types: Primitive, poorly developed soils cover bedrock exposures on ridgetops and rocky shores. These soils are infertile and susceptible to erosion. More fertile, humus-rich soils known as Leptosol are common on ridge slopes. The dissected topography, disrupted with tectonic dislocations, is responsible for a distinctive microclimate. Conditions are favourable for more southern lora and fauna on south-facing slopes, which receive more sunlight and are protected against cold, northerly winds. More northern higher vascular plant and moss species occur on north-facing slopes and in narrow crevasses. Considerable variations in altitude (up to 200 m) at this latitude (62–63°N) have resulted in altitudinal zoning. As a consequence, frosts occur 10–30 days earlier in the elevated areas. Also the numerous lakes have a substantial effect on the microclimate. The forest cover has been considerably transformed by selective and clear cutting. However, most of the forest communities have survived or recovered due to the relatively small number of trees removed as well as the natural dynamics of the forests.In contrast with the rest of Zaonezhye, there is practically no agricultural development in this terrain. In this geographical terrain (No. 1 in Fig. 1), the forest cover consists mainly of pine forests, growing on rocky ground, and pine-dominated forests of Myrtillus type, growing on tectonic blocks that are covered by a thin layer of unconsolidated sediments. Other predominant forest types include mesic, pine- or spruce-dominated stands of Myrtillus type on the slopes and in the depressions between the ridges. These forests are characterized by diverse ground vegetation and complex plant communities. Birch-dominated stands make up less than 5% of the area covered by forests of Myrtillus type. However, their ground vegetation is diverse, including combinations of herbaceous species, motley grass and Myrtillus patches. On average, these plant communities are restricted to relatively small areas. Paludiied glacial terrain of hills and ridges, dominated by pine habitats (No. 2 in Fig. 1) This terrain type covers 30% of the tectonic-denudation landscapes (Fig.3). Its glacial relief comprises of plains, intersected by gently sloping, lat-topped ridges 104 Reports of the Finnish Environment Institute 40 | 2014 without a well-deined foot of the hill. Altitudes vary between 60 and 120 m above sea level and vertical ruggedness is 30–40 m. Quaternary sediments consist mainly of moraine that forms a 4–7 m layer, covering 70–80% of the crystalline basement and evening out the rugged bedrock. In parts of the terrain, also moraine drumlins contribute to the ridge pattern.Overall, mires cover approximately 20% of the terrain and open mires 8%. These eutrophic and mesotrophic mires contain a diverse lora and a variety of plant communities. The hydrographic network is well developedand uniform. The largest rivers are between 10 km and 30 km long. Lakes account for approximately 7% of the terrain. The soil cover is dominated by acidic, sandy loam and loamy burozems (Cambisols). These highly fertile soils areazonal and provide good conditionsfor a relatively high biological diversity for Karelia. With the exception of the western parts of the terrain, the gently sloping landscape and the minor vatiations in altitude have created a uniform microclimate. In the western parts, Lake Onega evens out considerable variations in temperature. Vegetation has been markedly transformed by long-term slash-and-burn farming of fertile land as well as continuous selective and clear cutting. However, forest regeneration has been successful over most of the area and plant communities have largely been restored to their original state. Nowadays, the forest cover is characterised by a mosaic of fresh pine and spruce forests of Myrtillus type with nemoral elements in the ground vegetation.Other common vegetation types include birch forests of Myrtillus type as well as herbaceous birch forests, growing on abandoned agricultural land. Also these forests have nemoral elements in the ground vegetation. Grey alder (Alnus incana) forests with a large proportion of mountain ash (Sorbusaucuparia) and European birdcherry (Padus racemosa) often grow on the most fertile sites. Spruce is absent in these stands. Some Sphagnum habitats are occupied by low-productive secondary spruce and birch stands. The average contour of the plant communities is 120 m long. Paludiied lacustrine-glacial hill terrain, dominated by pine stands (No.3 in Fig. 1) The relief of this terrain has been affected by the regression of Lake Onega (Fig.4). It makes up 30% of the tectonic-denudation landscapes. Its gently sloping, undulating plain is formed through accumulation and abrasion (of former lake bottom). Active movement along crystalline faults has produced small ridges, although they are not characteristic of this terrain. Absolute altitudes of watersheds are no more than 60 m above sea level and vertical ruggedness is 5–20 m. Overall, mires make up 20% of the terrain. Open mires account for 6% of the terrain. Due to their lacustrine origin, mires are predominantly mesotrophic or eutrophic. Usually peat is underlain by sapropel, lake clay and silt. These features have resulted in diverse plant communities and a rich lora. Long and narrow lakes, conined to faul zones, determine the hydrographic conditions of the terrain. Lakes cover no more than 10 % of the area (excludingUnitsa Bay and a small portion of Lizhma Bay). Small streams that are less than 5 km long are distributed evenly throughout the area. The diverse soil cover consists of dark, acidic sandy loam and loam burozemson shungite, marshland humus gley and lowland peat soils. These fertile soils provide good conditions for a variety of species and plant communities. In addition, the microclimate is uniform across the terrain. However, the area has been heavily affacted by human activities, including forest cutting and agriculture. There is an increasing amount of highly fertile soils (on land formerly used for agriculture), covered by secondary forests or secondary forest and meadow communitites. The forest cover is a mosaic of fresh pine and birch forests with a diverse ground cover (motley grass, motley grass-bilberry, grass-bilberry, etc.). Also pine forestswith Sphagnum are widespread. Spruce forests make up only a Reports of the Finnish Environment Institute 40 | 2014 105 small percentage of the area, but their ground cover is diverse. Birch communities are mostly conined to abandoned agricultural land.All these forest types host a variety of woody and shrub species, including nemoral species such as lime, elm and currant. The average contour of the plant communities is 120 m long. Normally paludiied lacustrine and lacustrine-glacial plains, dominated by spruce, have indistinct boundaries, although their core areas are well deined. This landscape type comprises the following geographical terrains: Paludiied terrain of moraine plains, dominated by spruce habitats (No. 4 in Fig. 1) This is the dominant terrain type, covering 50% of the paludiied landscapes of lacustrine and lacustrine-glacial plains (Fig. 5). Its glacial relief consists of a plain with gently sloping hills and lat-topped ridges that lack a well-deined foot of the hill. Altitudes vary between 50 and 90 m above sea level and vertical ruggedness is 10–30 m. Quaternary deposits consist of a 4–7 m thick layer of moraine, which covers 90–100% of the crystalline basement and smoothes the ruggedness of the bedrock. In parts of the terrain, a ridge relief is formed by moraine drumlins. Mires make up about 50% and open mires 15% of the terrain. These eutrophic and mesotrophic mires contain a diverse lora and a variety of plant communities. The hydrographic network is well developedand uniform. Rivers are between 10 km and 30 km long and there are practically no lakes. The soil cover is dominated by acidic, sandy loam and loamy burozems. The gently sloping landscape and the minor vatiations in altitude have created a uniform microclimate. However, Lake Onega evens out considerable variations in temperature in its vicinity. Vegetation has been considerably transformed by long-term slash-and-burn cultivation of fertile land as well as continuous selective and clear cutting. However, forest regeneration has been successful over most of the area and plant communities have largely been restored to their original state. Nowadays, the forest cover is characterised by a mosaic of fresh bilberry spruce forests that grow on the enriched ground. Other common vegetation types include bilberry, bilberry-grass and wide-grass aspen and birch forests. The most fertile soils host plant communities, consisting of speckled alder as well as extensive mountain ash and European birdcherry stands. In these communities, spruce is absent in the undegrowth. Some Sphagnum habitats are occupied by low-productive secondary spruce and birch stands. The average contour of the plant communities is 120 m long. Moderately paludiied, topographically complex aqueo-glacial terrain, dominated by pine stands (No.5 in Fig 1) This terrain type makes up approximately 20 % of the landscape area (Fig. 6). Fluvioglacial landforms include radial ridges (eskers), associated with luvioglacial deltas. The terrain extends for over 30 km from northwest to southeast. Altitudes vary between 5 m and 15 m. Absolute altitudes of watersheds are no more than 80 m above sea level. Overall, mires cover up to 20% of the terrain, while open mires account for 5% of the terrain. Raised bogs with low mineral consentrations are common. There are no lakes in the terrain, and streams are less than 5 km long creeks. Microclimatic conditions remain more or less the same throughout the terrain. The soil cover consists of podzols and leptosols. More fertile sites include clasts of local basic and shungite-bearing rocks. Ridges and wide delta-like areas are used for agriculture. The forest cover is considerably transformed. It shows a mosaic pattern (Fig.) of pine, aspen and birch stands, growing in fresh bilberry habitats with diverse ground 106 Reports of the Finnish Environment Institute 40 | 2014 vegetation (motley grass, motley grass-bilberry, grass-bilberry, etc.). Often speckled alder grows on abandoned agricultural land. Wet habitats are occupied by Sphagnum. Spruce stands are few. The undergrowth consists of currant, lime, buckthorn and birdcherry. The average contour of the plant communities is 70 m. Highly paludiied lacustrine-glacial terrain of plains, dominated by spruce habitats (No. 6 in Fig. 1) This terrain type makes up 30% of the landscapes (Fig. 7). Its relief consists of a plain with gently sloping hills. Absolute altitudes are estimated at no more than 80 m above sea level and vertical ruggedness is 5–20 m. Structural denudation landforms are completely covered by unconsolidated sediments, which are dominated by a 6–7 m thick layer of varved clay. Overall, mires make up 70% of the area, while open mires account for 30% of the area. Mires are predominantly eutrophic and mesoeutrophic and their lora consist of both marshland and forest species. Streams are less than 5 km long and lakes cover no more than 5 % of the terrain.The microclimate is uniform across the terrain. Well-drained eluvial, surface and gley loam soils support highly productive forests. However, the forest cover has been totally transformed by selective and clear cutting as well as agriculture. Nowadays, secondary forests dominate most of the area, including abandoned agricultural land. The most common forests are aspen, birch and speckled alder stands of bilberry and horsetail types. These forests have succeeded spruce stands,which are characteristic of the terrain. Black alder communities are encountered on stream-irrigated sites. Paludiied sites are dominated by pine stands with sedge and Sphagnum. The average contour of the plant communities is 150 m. REFERENCES GrШЦЭsОЯ, .N. 2000. . . : ДLКЧНsМКЩО ОМШХШРв ШП ЭКТРК ПШrОsЭs: ЭСОШrОЭТМКХ КЧН КЩЩХТОН КsЩОМЭsЖ. – PОЭrШгКЯШНsФ. KКrОХТКЧ RОsearch Center of Russian Academy of Sciences. 144 p. (in Russian). GrШЦЭsОЯ, .N. 2008. . . ДBКsТМ ХКЧНsМКЩО ОМШХШРв ШП RЮssТК’s EЮrШЩОКЧ ЭКТРК ПШrОsЭsЖ. PОЭrШгКЯШНsФ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП Russian Academy of Sciences. 226 p. (in Russian). GrШЦЭsОЯ, A.N. (ОН.) 2013. . . ( .). : , , ДSОХФК ХКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ МСКrКМЭОrТsЭТМs, LКЧН UsО, CШЧsОrЯКЭТШЧЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 179 Щ. (IЧ RЮssТКЧ). VШХФШЯ, .D., GrШЦЭsОЯ, .N., ErЮФШЯ, G.V., KКrКЯКОЯ, V.N., KШХШЦвЭsОЯ, V. ., KЮrСТЧОЧ, В.P., LКФ, G.T., PвгСТЧ,. .F., SКгШЧШЯ, S.V. &SСОХОФСШЯ, . . 1990. . ., . ., . ., . ., . ., . ., . ., . . ., . ., . . ( ) ДLКЧНsМКЩО ОМШsвsЭОЦs ШП аОsЭОrЧ ЦТН-ЭКТРК: sЭrЮМЭЮrО КЧН НвЧКЦТМs. PОЭrШгКЯШНsФЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. 284 Щ. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 107 Fig .2 Forest structure in a mildly paludiied denudation-tectonic ridge terrain dominated by pine habitats (fragment). Fig. 3 Forest structure in glacial hilly-ridge mid-paludiied terrain dominated by pine habitats (fragment). 108 Reports of the Finnish Environment Institute 40 | 2014 Fig. 4 Forest structure in lacustrine-glacial hilly mid-paludiied terrain dominated by pine stands (fragment). Fig. 5 Forest structure in mid-paludiied morainic plain terrain dominated by spruce habitats (fragment). Reports of the Finnish Environment Institute 40 | 2014 109 Fig. 6. Forest structure in aqueo-glacial topographically complex mildly paludiied terrain dominated by pine stands (fragment). Fig. 7 Forest structure in highly paludiied lacustrine-glacial plain terrain dominated by spruce habitats (fragment). 110 Reports of the Finnish Environment Institute 40 | 2014 2.3 The structure of forest land and forest stands in Zaonezhye Peninsula Boris Raevsky* and Nikolay Puteshov** * Directorate for Regional protected areas of the Republic of Karelia, 66 Rigachin St. 185005, Petrozavodsk, Karelia, Russia. Corresponding author Boris Raevsky. E-mail: oopt@karelia.ru ** Ministry of Nature Management and Environment of the Republic of Karelia, 2/24 Andropov St. 185035, Petrozavodsk, Karelia, Russia. E-mail: ecopetr@karelia.ru Introduction Zaonezhye Peninsula (Zaonezhye) is known both inside and outside of Russia as an exceptionally valuable natural and cultural territory. Currently there is a clear trend towards the intensiication of the exploitation of forest and mineral resources as well as increased recreational pressure in Karelia, particularly in Zaonezhye. Therefore, the creation of a protected area network, aiming at preserving the most valuable objects under different threats, becomes of paramount importance. At present there are 22 regional protected areas in the peninsula, covering 2500 ha. The largest among them is the Klim-gora landscape nature monument (approximately 600 ha). Kizhi federal zoological reserve (zakaznik), which covers 50 000 ha, is located southeast of the peninsula. The main objectives of this reserve are to preserve natural values of the Kizhi skerries and to protect nesting places of waterfowl (Figure 1). The Kizhi open-air museum and its buffer zone are within the boundaries of the reserve and they cover a large proportion of it. The open-air museum is characterized by landscapes that have been under a heavy human inluence. Results Forest ecosystems are the most dynamic components of natural landscapes due to their biological and ecological characteristics as well as their economic value. Therefore, forests require special protection. The establishment of a large-scale protected area on Zaonezhye is crucial for the conservation of forest communities; primarily pine forests, which are most valuable from ecological, biological and recreational point of view. In 2013, Karelian Research Center published a monograph which summarized research data concerning esker landscapes situated in the middle part of Zaonezhye Peninsula (Gromtsev 2013). The authors have used the results of the publication as scientiic arguments for the establishment of the Zaonezhye landscape reserve. In 2013 the NGO “SPOK” also developed arguments for the establishment of the Zaonezhye nature park (Documentations... 2013; see Figure 1). Reports of the Finnish Environment Institute 40 | 2014 111 According to modern knowledge, Zaonezhye is located within the Fennoscandian middle taiga subzone. Its area is divided into western and eastern parts that differ clearly in their landscape features. The transition zone between them divides two contrasting types of geographical landscapes in line with the villages of Velikaya Guba, Velikaya Niva and Shunga. Areas to the west of these villages are dominated by moderately paludiied denudation-tectonic esker landscapes; whereas areas to the east are dominated by moderately waterlogged lacustrine and lacustrine-glacial lowland landscapes. Pine habitats prevail in the west, while spruce habitats dominate in the east (Gromtsev 2013). The landscape reserve (LR), proposed by the Karelian Research Centre, covers a total area of 106 373 ha. It is located in its entirety within the boundaries of the former landscape type. On the contrary, the nature park (NP) proposed by the NGO “SPOK”, which covers 107 862 ha, lies mostly within the boundaries of the latter landscape type. Together these planned protected areas cover roughly two thirds of Zaonezhye Peninsula. According to the Ministry of nature management and environment of the Republic of Karelia (1/1/2012), forests cover 81,9% and 87,5% of the protected areas respectively. The planned landscape reserve and nature park share 25% of their territories and 22% of their forest areas. Comparative analysis of the structure of forest land (lesnoi fond in Russian) shows the level of anthropogenic transformation in the two protected areas. It also suggests that characteristics of intact forest communities are preserved mainly in pine stands. Analysis of the land categories of forest land in LR and NP (Table 1) shows that the proportion of forest areas is relatively high: 79,4% and 86,9% respectively. In the Karelian context, this suggests, irst and foremost, moderate or low paludiication of the territory. Wetlands cover no more than 5% of the area. Practically all of the forest areas are covered by forests (99,0% in LR and 96,4% in NP). At the same time, the proportion of forest plantations is higher in LR (19,7%) than in NP (13,4%). This suggests that artiicial reforestation has been widely used on the peninsula at least since the middle of the 20th century. Fig. 1. Protected areas of Zaonezhye peninsula. 112 Reports of the Finnish Environment Institute 40 | 2014 Table. 1. Distribution of different land categories of forest land (lesnoi fond) in the planned protected areas*. Land category Landscape reserve Nature park Area, ha Structure, % Area, ha Structure, % Total area of forest land (lesnoi fond) 87138 100 94422 100 Total forest area, including: 69227 79.4 (100) 82025 86.9 (100) Forest-covered areas 68520 78.6 (99.0) 79067 83.7 (96.4) Forest plantations 13518 15.5 (19.7) 10998 11.6 (13.4) Total of bare forest land, including: 705 0.8 (100) 2956 3.1 (100) Open plantations 147 0.2 (20.9) 964 1.0 (32.6) Forest nurseries and seed orchards 99 0.1 (14.0) – – Open stands – – – – Fire sites 3 – 7 – Dead plantations 9 – 30 0.03 (1.0) Felling areas 447 0.5(63.4) 1955 2.1 (66.1) Forest clearings and waste- – land – – – Total of non-forest areas, including: 17912 20.6 (100) 12397 13.1 (100) Arable land – – – – Hay meadows 88 0.1 (0.5) 270 0.3 (2.2) Pastures – – – – Water area 12873 14.8 (71.9) 8246 8.7 (66.5) Gardens and berry ields – – – – Roads and clearings 243 0.3 (1.4) 281 0.3 (2.3) Buildings – – 43 – Wetlands 4355 5.0 (24.3) 3295 3.5 (26.6) Sand – – – – Other non-forest areas 353 0.4 (2.0) 264 0.3 (2.1) * The proportion of sub-categories within the land categories of forest land is shown in parentheses. Felling areas predominate the structure of bare forest land in both territories (63,4 and 66,1%) but their area is four times larger in NP than in LR. Felling areas also occupy a considerable proportion of bare forest land within the total forest land. The proportion of non-forest areas is less than 21% of the total forest land in the examined protected areas. Water areas and wetlands dominate their structure. The proportion of water objects in the total structure of the forest land roughly corresponds to the average igure in Karelia (approximately 10%), whereas the proportion of mires is considerably lower than average for the paludiied forest land of Karelia (23,7%). In general, structural analysis of the forest area indicates relatively extensive exploitation and anthropogenic transformation of the nature park in comparison with the landscape reserve. Reports of the Finnish Environment Institute 40 | 2014 113 Forests dominated by coniferous species cover 68,4% and 59,3% of forest-covered areas in LR and NP respectively (Table 2). Table 2. Distribution of forest-covered areas, based on the dominant species. Landscape reserve Nature park Dominant species Area, ha % Area, ha % Pine (Pinus sylvestris) 28693 41.9 21188 26.8 Spruce (Picea x fennica) 18105 26.4 25678 32.5 Larch (Larix sibirica) 33 0.05 41 0.1 Birch (Betula spp.) 18308 26.7 23962 30.3 Speckled alder (Alnus incana) 1264 1.8 3427 4.3 Black alder (Alnus glutinosa) – – 66 0.1 Aspen (Populus tremula) 2117 3.1 4705 6.0 Total 68520 100.0 79067 100.0 A high proportion (90% or more) of forests, dominated by coniferous species, is typical for intact taiga forests. A higher proportion of deciduous stands, dominated by birch, alder and aspen, indicate both moderate human inluence and relatively high soil fertility in the area. Pine dominates in the landscape reserve while spruce dominates in the nature park, which relects the characteristics of the aforementioned landscapes. Siberian larch is present in forest plantations. Next, we will use a set of parameters to examine the distribution of forest stands in the main coniferous structures. Coniferous stands show a particular age class distribution (Table 3). For coniferous species, each age class equals 20 years. Approximately 68% of coniferous stands in LR and 51% of pine and spruce stands in NP fall into age classes I-V. For intact taiga forests, the opposite is true. In these forests, more than 70% of forest stands belong to age classes VIII-XII. In the planned protected areas, the proportion of stands in these age classes is no more than 17%. Thus, the distribution of age classes is a certain sign of considerable anthropogenic transformation of Zaonezhye forests. Table 3. Age class distribution of coniferous forests. 114 Age class Landscape reserve Nature park Pine, ha % Spruce, ha % Pine, ha % Spruce, ha % 1 925.7 3.2 1240.9 6.8 411.6 2.1 4389.8 18.6 2 3950.2 13.9 5493.6 30.0 842.7 4.3 4334.9 18.3 3 4903.5 17.2 1220.5 6.7 2065.2 10.6 184.2 0.8 4 4749.3 16.7 2311.5 12.6 2442.8 12.5 628.7 2.7 5 4740.8 16.6 2203.4 12.0 3828 19.6 2868.6 12.1 6 2671.7 9.4 1887.9 10.3 3731.5 19.1 3839.1 16.2 7 2349.6 8.2 1637.8 8.9 2965.8 15.2 3944.9 16.7 8 2104.3 7.4 1293.2 7.1 1807.7 9.2 2138.8 9.0 9 1678.9 5.9 952 5.2 1035.7 5.3 1276.8 5.4 10 313.8 1.1 96.9 0.5 387.5 2.0 44.6 0.2 11 76.1 0.3 – – 34.6 0.2 – – Reports of the Finnish Environment Institute 40 | 2014 12 41.6 0.1 – – – – – – TOTAL 28505.5 100.0 18337.7 100 19553.1 100.0 23650.4 100.0 According to species or group of species dominating either within the ground cover layer or in the undergrowth, different forest types are being distinguished (Table 4). Forest type is a site in the forest which is characterized by uniform forest-growing conditions, similar species composition and ground cover and which demands the same silvicultural methods (Sukachev & Zonn 1961). Table 4. Forest types that are common in pine dominated forests of Zaonezhye peninsula. Forest type Indicatory species Cladonia lichens of genus Cladonia spp. Rocky Cladoniaceae spp. and mosses on outcrops of cliffs Vaccinium Vaccinium vitis-idaea Myrtillus Vaccinium myrtillus Oxalis Oxalis acetosella Long mosses Polytrichum spp. Herbal on bogs Various herbs in waterlogged forests Meadowsweet Filipendula ulmaria Sedge-Sphagnum Cyperaceae spp. and Sphagnum spp. Sphagnum Sphagnum spp. Ledum Ledum palustre The ecological spectrum of coniferous forests in Zaonezhye seems relatively normal. Here, coniferous forests are represented by seven main forest types, as well as a separate type of drained stands (Table 5.) Table 5. Distribution of coniferous forests by forest type. Forest type Landscape reserve Nature park Pine, ha % Spruce, ha Cladonia 676 2.4 – – 379 1.8 – – Vaccinium 3576 12.5 4 0.02 2608 12.3 46 0.2 Myrtillus 16700 58.2 12036 66.5 7147 33.7 16420 63.9 Oxalis 2888 10.1 4598 25.4 3376 15.9 5820 22.7 Long mosseses 1142 4.0 1324 7.3 746 3.5 2002 7.8 Herbal on bogs 35 0.1 47 0.3 80 0.4 178 0.7 Sphagnum 3507 12.2 81 0.4 6220 29.4 1212 4.7 Drained stands 170 0.6 14 0.1 633 3.0 2 0.01 TOTAL 28694 100 18104 100 21189 100 25680 100 % Pine, ha % Spruce, ha % Normally spruce forests are dominated by the Myrtillus type. In forest inventories, these types are referred to as mixed-herb Myrtillus, Myrtillus and moist Myrtillus forests. It is commonly known that during natural reforestation spruce is a more demanding species. Therefore, it occupies relatively homogenous habitats with the most favourable conditions. Meanwhile, pine is ecologically more lexible and dominates less favourable habitats with more diverse habitat conditions. The characteristics of Reports of the Finnish Environment Institute 40 | 2014 115 Zaonezhye forests include the relatively unvaried typological spectrum of pine and spruce. Also, the proportion of Myrtillus pine forests in denudation-tectonic landscapes is high – nearly as high as the proportion of spruce forests - indicating that there are relatively highly fertile mineral soils in the landscape reserve. The proportion of waterlogged forests (49.4%) within the nature park is twice as large as within the landscape reserve (25.0%), which is typical for lacustrine-glacial lowland landscapes. The forests of the peninsula show a distinctive distribution pattern of site quality classes (Table 5). The productivity of coniferous stands varies from classes I to Va and Vb, which is relatively common in Karelia. Characteristically, a particularly high proportion of pine stands belong to class III. These stands constitute nearly half of all pine forests in the landscape reserve. Pine stands cover 1.7 times larger area than spruce stands. Table 6. Distribution of coniferous forests by site quality class (bonitet). Site class Landscape reserve Nature park Pine, ha % Spruce, ha I 58 0.2 – – 114 0.5 3 0.01 II 3422 11.9 491 2.7 1579 7.5 763 3.0 III 13229 46.1 7902 43.7 8637 40.8 12085 47.1 IV 6167 21.5 7432 41.1 3244 15.3 8081 31.5 V 4425 15.4 2280 12.6 4006 18.9 4507 17.6 Va 1392 4.9 – – 3520 16.6 231 0.9 Vb – – – – 89 0.4 8 0.03 TOTAL 28693 100 18105 100 21189 100 25678 100 Average index III.5 – III.6 – IV.0 – III.7 – % Pine, ha % Spruce, ha % Uneven-aged forest stands are a typical feature of primeval forests in the taiga zone of the European part of Russia. Normally these forest stands dominate coniferous stand structures of intact forests. In general, uneven-aged forest stands provide a dynamic balance between growth and dieback processes. Forest inventory data is crucial for detecting primeval forests in existing and planned protected areas as well as calculating certain parameters of their natural age structure. We have used the classiication of S. Zyabchenko (1984) as the methodical basis for analyzing the pine forests of Zaonezhye. We have only analyzed pine-dominated stands in age classes VII and higher. A forest stand is considered absolutely uneven-aged when the following conditions are met: a) there is a minimum of two generations of pine; b) the growing volume of the structure is no more than 40%; c) the oldest generation is at least 180 years old; d) there should be a difference of more than three age classes between generations. In younger age classes, as well as when the proportion of growing volume in one generation is at least 50%, forests are considered relatively uneven-aged. If there has been only one generation of pine, the stand is considered potentially even-aged. The results of the classiication of pine stands in the landscape reserve and the nature park are presented in Tables 6, 7 and 8. We have used the following abbreviations: P – pine; S – spruce; L – larch; B – birch; As – aspen; Ali – speckled alder (Alnus incana); Alg – black alder (Alnus glutinosa). The ages of the elements are described in subscript. 116 Reports of the Finnish Environment Institute 40 | 2014 Table 7. Distribution of pine stands in the Zaonezhye landscape reserve by age structure, forest type and site quality class. № Forest type Site class Composition and structure (in tenth parts of growing volume) Growing volume, m3/ha Total area, ha % Absolutely uneven-aged 1 Myrtillus III 3P190 2P 90 3S170 1B901As90 270 53.0 80.5 2 Sedge-Sphagnum V 3,7P190 2,7P100 1,3S140 2,3B70 84 5.7 8.7 11 Long mosses V 4СP190 2P 90 2S170 2B 80 120 3.2 4.9 12 Ledum V 4P190 3P 90 1S170 2B70 111 3.9 5.9 65.8 100.0 TOTAL Relatively uneven-aged 1 Myrtillus II 4P130 3P110 2B 80 1As80 330 2.1 0.1 2 Myrtillus III 5,3P170 2,2P 90 1S130 1,5B90/As90 253 332.8 18.4 3 Myrtillus IV 5,7P170 2P70 2S70 2B701As70 183 234.8 13.0 4 Myrtillus V 3P130 2,9P100 0,5S90 0,9B90/As90 155 35.0 1.9 3 Vaccinium IV 5,7P150 3,1P 90 0,8S120 0,4B 80/As80 194 142.5 7.9 4 Vaccinium V 5,8P160 3,7P100 0,5B90/As90/S90 133 154.5 8.6 5 Rocky V 6,5P170 2,8P 90 0,7S90/B 80/As80 72,4 126 7.0 6 Rocky Va 6,4P160 2,9P 90 0,7S150/B90 67 27.5 1.5 7 Sedge-Sphagnum V 6,5P170 3P100 0,3S130 0,2B70 113 227.6 12.6 8 Sedge-Sphagnum Vа 4,3P170 5,3P110 0,4B 80/S70 83 179.1 9.9 9 Long mosses IV 5P150 4P 90 1B 40 111 10.1 0.6 10 Ledum V 6,3P170 3,2P110 0,4S170 0,1B 80 121 66.6 3.7 11 Ledum Vа 5P150 5P70 42 3.7 0.2 12 Sphagnum V 6,8P170 2,6P 90 0,6S110/B70 77 87.5 4.8 13 Sphagnum Vа 6,9P160 3P110 0,1S110/B 80 76 143 7.9 1805.8 100.0 TOTAL Potentially even-aged 1 Herbal on bogs II 4P130 1,5S110 4,5B90/As90 345 17.1 0.4 2 Herbal on bogs III 5,4P1301,5S120 3,1B90/As90 320 210.5 5.2 3 Oxalis II 5P130 3S130 1,5B90/As90 0,5S60 331 5.5 0.1 4 Oxalis III 5,1P130 2,5S110 2,3B90/As90 0,8S90 318 63 1.6 5 Oxalis IV 5,7P130 2P110 2,3B90/As90 264 70.6 1.7 6 Myrtillus II 3P130 3S110 2As902B90 362 4.7 0.1 7 Myrtillus III 5,9P140 2,3S130 1,8B90/As90 278 951.4 23.5 8 Myrtillus IV 6,2P140 2,1S110 1,7B90/As90 190 370 9.2 9 Vaccinium III 7P130 1S90 2B90/As90 185 13.9 0.3 10 Vaccinium IV 8,1P130 1S90 1B70/As70 178 397 9.8 11 Vaccinium V 8,6P140 1S90 0,4B 80/As80 141 319 7.9 12 Rocky V 9,5P140 0,5S140/B 80 99 81.9 2.0 13 Rocky Va 9P140 1S150/B60 71 23.5 0.6 14 Meadowsweet IV 5P140 2S130 3B90 186 8.7 0.2 15 Meadowsweet V 5,5P1401,5S140 2,5B70 128 7 0.2 Reports of the Finnish Environment Institute 40 | 2014 117 16 Sedge-Sphagnum V 6,7P160 2S150 1,3B 80 131 482 11.9 17 Sedge-Sphagnum Va 8,3P150 1S130 0,7B90 65 34.7 0.9 18 Long mosses IV 5,8P140 2,6S140 1,6B 80 142 123 3.0 19 Long mosses V 5P150 2,7S140 2,3B90 121 148 3.7 20 Ledum V 9,5P150 0,4S150 0,1B90 143 124 3.1 21 Ledum Va 9P1401S110 +B90 95 31 0.8 22 Sphagnum V 9,2P140 0,5S150 0,3B90 94 167 4.1 23 Sphagnum Va 7,5P140 1,5S140 1B90 65 390 9.6 4043.5 100.0 TOTAL Table 8. Distribution of pine stands in the Zaonezhye nature reserve by age structure, forest type and site quality class. № Forest type Site class Composition and structure (in tenth parts of growing volume) Growing volume m3/ ha Total area, ha % Absolutely uneven-aged 1 Myrtillus III 3P190 2P 90 3S170 1B901As90 270 53.0 73.8 4 Vaccinium V 4P 200 2P130 2S190 2As110 129 6.8 9.5 8 Sedge-Sphagnum Va 4P190 4P 90 2B60+S150 71 12 16.7 71.8 100 TOTAL Relatively uneven-aged 1 Myrtillus III 5,7P180 2,3P100 2B90/As90 237 100.9 6.9 2 Myrtillus IV 5,8P170 2,8P120 1,4B90 226 135.5 9.3 3 Vaccinium IV 5,9P160 2,3P120 1S90 0,8B90/As90 204 259.1 17.7 4 Vaccinium V 6,5P190 2,5P120 1B100 156 84.7 5.8 5 Rocky V 8P150 1,3S140 0,7B90 133 61.3 4.2 6 Rocky Va 9P130 1S130+B 80 133 12 0.8 Oxalis III 3P170 2P120 2,5S1302,5B90 215 31.0 2.1 7 Oxalis IV 5,8P180 2,6P100 1,6S100/B90 218 34.1 14.1 8 Herbal on bogs III 6P130 2P180 1B90 1As90 244 14 1.0 9 Meadowsweet V 5P150 2P 210 3B100 168 6.2 0.4 10 Sedge-Sphagnum V 5,7P160 3P 90 1,3B 80 +S130 99 166.1 11.3 11 Sedge-Sphagnum Va 5,7P1503,5P 90 0,7B 80 0,1S150 71 269.4 18.4 12 Long mosses IV 3P170 2 P120 2,5S1302B90 0,5Ali100 169 12.7 0.9 13 Ledum V 7P190 3P105 94 6.8 0.5 13 Sphagnum V 5,7P160 2,7P130 1,6S130/B 80 85 31.7 2.2 14 Sphagnum Va 6P140 4P 90 +S130 53 66.4 4.5 1464.3 100 TOTAL Potentially even-aged 1 Herbal on bogs III 6P130 2,1S120 1,9B90/As90 268 165.6 3.2 2 Oxalis II 3P130 3S130 3As90 1B90 336 2.6 0.1 3 Oxalis III 5,5P150 2S140 2,5B90/As90 257 144.9 2.8 4 Oxalis IV 6,5P160 2,2S100 1,3B90 236 277.9 5.4 5 Myrtillus II 3P130 3S110 2As90 2B90 362 4.7 0.1 118 Reports of the Finnish Environment Institute 40 | 2014 6 Myrtillus III 5,4P140 2,3S130 2,3B90/As90 266 1088.3 21.0 7 Myrtillus IV 6,7P150 2,1S140 1,2B90/As90 213 97.7 1.9 8 Vaccinium III 7,3P160 1,5S130 1,2B90 264 23.6 0.5 9 Vaccinium IV 8,3P130 1,1S120 0,6S 80/B 80 201 297 5.7 10 Vaccinium V 9,1P140 0,7S110 0,3B 80/As80 176 608.4 11.7 11 Rocky V 8P150 1,3S140 0,7B90 133 61.3 1.2 12 Rocky Va 9P130 1S130+B 80 133 12 0.2 13 Meadowsweet IV 4,7P140 1,7S130 3B90 0,6As90/Ali90 183 16.3 0.3 14 Sedge-Sphagnum V 6,1P140 2,2S130 1,6B 80 0,1Alg80 122 522.4 10.1 15 Sedge-Sphagnum Va 6,4P140 2,1S130 1,5B 80 79,4 1306.6 25.2 16 Long mosses IV 6P140 2,5S140 1,1B 80 0,4As90/Ali90 183 43.9 0.8 17 Long mosses V 6,4P150 2,2S140 1,3B90 0,1As75/Alg60 150 151.5 2.9 18 Ledum V 8,9P150 1,1S150/B90 113 41.8 0.8 19 Ledum Va 10P130 95 14 0.3 20 Sphagnum V 7,9P150 0,9S140 1,2B 80 93 79.5 1.5 21 Sphagnum Va 7,6P140 1,4S140 0,9B90 0,1Alg100 72 229.6 4.4 5189.6 100 TOTAL Table 9. The composition and structure of Zaonezhye pine stands, based on the type of age structure. Composition and structure (in tenth parts of growing volume) Average age class Growing volume, m3/ha Total area, ha % Potentially even-aged 6,7P140 1,8S110 1,5B 80/As80 7.5 184 4043.5 68.4 Absolutely uneven-aged 3,2P190 2,1P 90 2,7S170 2B90 10 237 65.8 1.1 Relatively uneven-aged 6P160 3,3P100 0,7S110/B90/As90 8 145 1805.8 30.5 5915.1 100 Type of age structure Landscape reserve TOTAL Nature park Potentially even-aged 6,4P140 2S110 1,6B90/As90/Ali90/ Alg90 7.7 168 5189.6 77.2 Absolutely uneven-aged 3,3P190 2,3P 90 2,7S150 1,7Ali110 10 223 71.8 1.1 Relatively uneven-aged 5,8P160 3P110 0,5S130 0,7B 80 8.5 158 1464.3 21.7 6725.7 100 TOTAL After analysing Tables 7, 8 and 9, we have come to the following conclusion: Absolutely uneven-aged stands represent the smallest share, amounting to only 1,1% of all types of age structures in both the landscape reserve and the nature park. Consequently, these forest-covered areas are least preserved from anthropogenic transformation. The absolutely uneven-aged Myrtillus pine stands of III site quality class indicated in Tables 6 and 7 are located in the forest compartment (kvartal) 117 of the Velikaya Guba forest district (lesnichestvo). The proportion of relatively uneven-aged stands is Reports of the Finnish Environment Institute 40 | 2014 119 30,5% in the landscape reserve and 21.7% in the nature park. Potentially even-aged pine stands dominate both planned protected areas, totaling 68.4% of the landscape reserve and 77.2% of the nature park. The formation of potentially even-aged pine stands depends on a set of natural and anthropogenic factors. Natural factors include large ires and vast windfalls. The natural reforestation of potentially even-aged pine stands is expected within 20–40 years after these catastrophic events. The main anthropogenic factor is intensive felling, namely clear cutting, followed by natural or artiicial reforestation. In the two planned protected areas, anthropogenic factors play a bigger part due to the long history of agriculture and high population density in Zaonezhye. According to Zyabchenko (1984), relatively uneven-aged pine stands appear after 60–80 years of natural afforestation of pine stands in open areas, namely ire sites. Alternatively, they can be formed under the inluence of intensive selective logging. The latter is true for Zaonezhye. On the whole, anthropogenic transformation is more pronounced in the planned nature park than in the landscape reserve. After analyzing Tables 6 and 7, we have come to the conclusion that the proportion of pine in the stand structure increases when the site quality class decreases. The biggest proportions of spruce are typical for highly productive, potentially even-aged pine stands of the Oxalis and Myrtillus types. Even though the two planned protected areas are located in different geographical landscapes their pine stands are characterized by similar structures (Table 9). According to our analyses, the pine-dominated boreal forests of Zaonezhye Peninsula have been highly productive in the past. These forests have supplied quality construction material for the outstanding monuments of wooden architecture, for which Zaonezhye is famous. Despite the extent of anthropogenic transformation of ecosystems, there are still small areas of old-growth pine stands of high conservation and recreational value. As shown in Figures 2 and 3, nearly all of these areas are already located within protective forests. Average indicators for the planned landscape reserve and nature park are shown in Table 10. At present, a signiicant proportion of coniferous forests in the planned protected areas (LR – 50.5% and NP – 39.7%) are located in protective forests where clear cutting is prohibited. In general, the average indicators for these forests are higher than for commercial forests. There is a special interest in the forest compartments (kvartal) of the Tolvuya and Velikaya Niva forest districts (lesnichestvo), which are included in both the landscape reserve and the nature park. Table 10. Average indicators for coniferous forests in the planned landscape reserve and nature park, based on inventories. Area, ha Average Relative Growing Average composition age, Site class stand volume, and structure years density m3/ha Pine 15443.2 96 III.5 0.67 181 6P2B1S1As+L,Ali,Alg Spruce 8184.8 93 III.7 0.70 173 5P2P2B1As+Ali,Alg Larch 16.1 36 III.9 0.81 109 5B3L1S1P TOTAL 23644.1 95 III.6 0.68 178 5P2S2B1As+L,Ali,Alg 13249.8 72 III.5 0.66 131 5P3B1S1As+Ali,Alg Dominant species Landscape reserve Protective forests Commercial forests Pine 120 Reports of the Finnish Environment Institute 40 | 2014 Spruce 9919.8 63 III.6 0.70 135 5S2B1P1As1Ali+Alg Larch 16.4 47 III.0 0.74 144 4L3P2B1S TOTAL 23186.0 68 III.6 0.68 133 4P3S2B1As+L, Ali,Alg Pine 10860.0 106 III.5 0.69 198 6P2B1S1As+Ali,Alg Spruce 7772.2 110 III.4 0.72 217 6S2B1P1As+Ali,Alg Larch 1.0 46 II.0 0.70 170 5B3L1P1S TOTAL 18633.2 108 III.5 0.70 206 4P3S2B1As+L,Ali,Alg Pine 10328.3 96 IV.4 0.61 128 6P2B1S1As+Ali,Alg Spruce 17906.0 76 III.8 0.67 147 6S2B1P1As+Ali,Alg Larch 40.0 42 II.5 0.80 141 4B3L1S1P1As TOTAL 28274.3 83 IV.0 0.65 140 4S3P2B1As+L,Ali,Alg Nature park Protective forests Commercial forests On the whole, when it comes to protecting forest ecosystems, the two proposed protected areas complement each other to some extent. However, the denudation-tectonic landscape of the landscape reserve seems more promising in terms of structure. Following the creation of a strict protected area (where cutting of dead and damaged stands is allowed only under exceptional circumstances), we would expect over 120-year-old pine stands to acquire features of intact pine forests within the next 50 years. REFERENCES ДDШМЮЦОЧЭКЭТШЧ ШП ЭСО МШЦЩХОб ОМШХШРТМКХ ТЧЯОЧЭШrв УЮsЭТПвТЧР ОsЭКЛХТsСЦОЧЭ ШП ЭСО ГКШЧОгСsФв sЭКЭО ЧКЭЮrО ЩКrФЖ 2013. , « » NGO “SPOK”. – PОЭrШгКЯШНsФ.108 Щ. (IЧ RЮssТКЧ). GrШЦЭsОЯ, A.N. (ОН.) 2013. . . (Щ .). : , .ДSОХФК ХКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ МСКrКМЭОrТsЭТМs, LКЧН UsО, CШЧsОrЯКЭТШЧЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 179 Щ. (IЧ RЮssТКЧ). SЮФКМСОЯ, V.N., ГШЧЧ, S.V. 1961. . ., . . . ДMОЭСШНТМКХ ТЧsЭrЮМЭТШЧs ПШr sЭЮНвТЧР ШП ПШrОsЭ ЭвЩОsЖ. – USSR AМКНОЦв ШП SМТОЧМОs PЮЛХТМКЭТШЧs. MШsМШа. 144 Щ. ГвКЛМСОЧФШ, S. S. 1984. . . . PТЧО ПШrОsЭs ШП ЭСО EЮrШЩОКЧ NШrЭС. – LОЧТЧРrКН, “NКЮФК” LОЧТЧРrКН ЛrКЧМС 248 Щ. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 121 Fig. 2. Spatial distribution of old-growth (older than 120 years) pine-dominated forests in planned Zaonezhye Nature (landscape) Reserve, northern part of Zaonezhye Peninsula. 122 Reports of the Finnish Environment Institute 40 | 2014 Fig. 3. Spatial distribution of old-growth (older than 120 years) pine-dominated forests in planned Zaonezhye Nature Park, southeastern part of Zaonezhye Peninsula. Reports of the Finnish Environment Institute 40 | 2014 123 Old growth spruce-dominated forest in Zaonezhye (Photo Boris Rayevsky). 124 Reports of the Finnish Environment Institute 40 | 2014 2.4 Forest structures and human impact on Zaonezhye Peninsula: a classiication and case studies Timo Kuuluvainen* and Olli-Pekka Tikkanen** * Department of Forest Sciences, University of Helsinki, PO Box 27, 00014 Helsingin yliopisto, Finland. ** School of Forest Sciences, University of Eastern Finland, PO Box 111, 80101 Joensuu, Finland Corresponding authors Timo Kuuluvainen & Olli-Pekka Tikkanen E-mail: Timo.Kuuluvainen@helsinki.i Tel: + 358504486146 E-mail: Olli-Pekka.Tikkanen@uef.i Tel: +358469210746 Introduction Human population history and past land use has a profound and diverse effect on current forest landscapes and forest structures within them (Brumelis et al. 2011). In eastern Fennoscandia, transformation of forests to agricultural land and use of wood for construction and heating has created open cultural landscapes in surroundings of villages (Huttunen 1980, Tikkanen et al. 2014). In Karelia, the landscapes around the old villages are now, after their abandonment, recovering towards more natural stage (Tikkanen et al. 2014, Tikkanen & Chernyakova 2014). Further away from the villages, slash and burn agriculture and other human activities have increased ire frequency, which has favored presence of pine and deciduous trees in forest landscapes and suppressed spruce (Huttunen 1980, Tikkanen & Chernyakova 2014). As a result, we can ind a gradient of human impact with increasing naturalness as a function of increasing distance from villages (Tikkanen et al. 2014). Zaonezhye peninsula has a long population history and it is has historically been more densely populated than many other areas in the Karelian Republic. In addition, industrial forestry has changed forest structure in many parts of the peninsula (see 2.3. in this volume). High intensity in forest use is known to lead to declining naturalness of forest structures including the amount and diversity of dead wood (Rouvinen et al. 2002). This is detrimental to many rare forest species, which are found in pristine forests and require abundance, diversity and long continuum of dead wood (Martikainen et al. 2000, Similä et al. 2003, Penttilä et al. 2004, Junninen et al. 2006). From the point of view of conservation of biodiversity and planning of conservation area networks it is critically important to ask 1) what effect has past human impact on modern day forest Reports of the Finnish Environment Institute 40 | 2014 125 structures and, especially, 2) can we still found primeval forests, which are potential habitats of rare species in Zaonezhye peninsula. Methods For this study, ield inventories and forest structure measurements were carried out in August 2013 using the circular plot method. Each inventory plot had a radius of 15 m (0.07 ha). Plots were chosen subjectively to be representative of the studied forests area (see map, Fig. 1). All living and dead trees with a diameter of more than 10 cm were measured. A vertex device was used to examine trees along the plot borders to accurately deine the plot size. Results and discussion According to the ield observations and inventories, forests of Zaonezhye Peninsula can be roughly divided into three classes: (A) high-quality primeval forests with negligible human impact, (B) forests with high conservation potential, which are no longer utilized and which are rapidly developing natural values and (C) successional, mostly deciduous, forests growing on abandoned ields or forests pastures. These forests retain important natural values as well due to a large amount of living and dead deciduous trees, as well as the natural succession that has occurred here for dozens of years. Examples of structure, tree volume and species composition in the three classes of forests are given in Tables 1–3 and in Figures 2–5. However, we would like to emphasize that although we made an effort to select representative examples, there is considerable variation in forest structures and composition within these broad classes, which is not fully relected in these examples. Map 1 Fig. 1. Locations of the sample plots in Table 1. A1 A2 C3 Lipovitsa B1 B2 Map 2 A3 C1 B3 C2 Tambitsa 126 Reports of the Finnish Environment Institute 40 | 2014 The irst group (class A) is high-quality primeval forests. These forests exhibit all the qualities of old, intact natural forests, including diverse tree species composition, big trees and complex stand structure as well as a large amount, diversity and continuity of dead wood. There are very few signs of human inluence, if any. Examples of structural features of these forests of the highest conservation priority are given in Table 1 and in Figures 2 and 3. At these sites the amount of dead wood ranged from 94 to 248 m3/ha and living tree volumes from 113 to 539 m3/ha. Not surprisingly, these forests were found from the most remote sites, which were visited; several kilometers from the closest larger settlements. Table 1. Examples of tree volumes (m3/ha) in three plots of the class A primeval forests. Tree volumes are presented for different tree species as well as living and dead trees separately. Coordinates for the plots are given in parenthesis (latitude/longitude). See Figure 1 for plot locations. Plot Pinus Picea Betula Populus Sorbus Alnus Total 110.5 - 54.2 - 59.8 225.9 A1(62°10’33.11”,35°3’39.88”) - Living 1.4 - Dead 24.7 66.4 7.4 13.1 - 15.7 127.3 - Total 26.1 176.9 7.4 67.4 - 75.6 353.2 A2 (62°10’15.85”, 35° 3’32.15”) - Living 8.7 103.8 - - - - 112.6 - Dead - 222.8 24.7 - - - 247.5 - Total 8.7 327.6 24.7 - - - 360.1 150.5 52.6 335.5 - - 538.5 A3 (62°17’17.93”, 35°33’53.45”) - Living - - Dead - 79.7 - 14.0 - - 93.7 -Total - 230.2 52.6 349.5 - - 632.3 Fig. 2. Primeval forest with a signiicant amount of large aspens in plot A1 (see Table 1) (Photo Timo Kuuluvainen). Reports of the Finnish Environment Institute 40 | 2014 127 Fig. 3. Primeval forests in plot A2 (see Table 1). In this plot we found the rare fungi species Pycnoporellus alboluteus (Photo Timo Kuuluvainen). The second group (class B) is forests that have been utilized in the past for selective cutting, slash-and-burn cultivation or forest pastures. However, after the cessation of human activities, these forests have developed for dozens of years under natural processes. Therefore, they are rapidly regaining natural structures and they already contain important features of natural forests, such as large trees, layered canopies and a rapidly increasing amount of coarse dead wood. These forests, although still showing signs of past human utilization, can still be considered as forests of high conservation potential. This is the case especially when they are located close to class A forests of the highest conservation priority. Together class A and B forests can form more representative and functional conservation areas. Examples of the composition of forests with high conservation potential are given in Table 2 and in Figure 4. In the study plots, the amount of dead wood ranged from 71 to 193 m3/ha and living tree volumes from 180 to 395 m3/ha. In Finland, these quantities of coarse woody debris has been found suficient to support very high number of species depended on dead wood (Martikainen et al. 2000, Similä et al. 2003, Penttilä et al. 2004, Junninen et al. 2006). Table 2. Examples of tree volumes (m3/ha) in three plots of the class B forests with high conservation potential. Tree volumes are presented for different tree species as well as living and dead trees separately. Coordinates for the plots are given in parenthesis (latitude/longitude). See Figure 1 for plot locations. Plot Pinus Picea Betula Populus Sorbus Alnus Total 109.3 13.6 - - - 180.9 B1 (62° 6'20.58", 35° 3'19.98") - Living 57.9 - Dead 25.8 167.7 - - - - 193.4 - Total 83.7 277.0 13.6 - - - 374.3 B2 (62° 6'15.45", 35° 2'11.61") - Living 10.6 152.9 20.9 - - - 184.4 - Dead - 80.0 - - - - 80.0 - Total 10.6 232.8 20.9 - - - 264.4 259.6 7.5 127.6 - - 394.7 B2 (62°15'15.91", 35°35'48.08") - Living 128 - - Dead - 47.1 20.2 2.9 0.8 - 71.0 - Total - 306.7 27.7 130.5 0.8 - 465.7 Reports of the Finnish Environment Institute 40 | 2014 Fig. 4. An example of forest with high conservation potential that has clear signs of past human use but also rapidly developing natural values, such as coarse woody debris (Photo Timo Kuuluvainen). The forests of the third group (class C) are typically located near old, abandoned villages. These forests have been under intensive human inluence but are now, after the cessation of human activities, in the early or middle stages of natural forest succession. These are former ields, slash-and-burn sites or pastures near abandoned villages. These forests vary greatly in structure and composition, relecting different histories of land use as well as the length of time since the area has last been affected by human activities. These successional forests include dense self-thinning alder stands and mixed deciduous stands with alder, birch and (often large) aspen, sometimes spruce in the undergrowth. There are also spruce-dominated stands among the successional forests. These forests provide important habitats for species thriving on living and dead deciduous trees. Examples of the structure and composition of forests with high conservation potential are given in Table 3 and in Figure 5. Even in these secondary forests, the amount of dead wood was relatively high compared to that of intensively managed forests of western Fennoscandia (Fridman & Walheim 2000, Ihalainen & Mäkelä 2009). Table 3. Examples of tree volumes (m3/ha) in three plots of the class C forests, characterized by intensive human inluence in the past. Tree volumes are presented for different tree species as well as living and dead trees separately. Coordinates for the plots are given in parenthesis (latitude/longitude). See Figure 1 for plot locations. Plot Pinus Picea Betula Populus Sorbus Alnus Total 175.0 82.8 - - 1.0 258.8 C1 (62°14'59.28", 35°27'22.18") - Living 12.1 - Dead - 42.0 23.3 - - - 65.3 - Total 12.1 217.0 106.1 - - 1.0 324.1 C2 (62°14'38.37", 35°29'35.54") - Living - 132.4 95.9 78.4 0.3 - 306.9 - Dead - 35.6 3.6 94.2 1.2 - 134.7 - Total - 168.0 99.5 172.5 1.6 - 441.6 137.4 99.8 20.4 0.3 - 359.6 C3 (62° 8'24.90", 34°56'29.94") - Living 101.5 - Dead - 2.6 10.0 - - - 12.6 - Total 101.5 140.0 109.8 20.4 0–3 - 372.2 Reports of the Finnish Environment Institute 40 | 2014 129 Fig. 5. An example of a successional, deciduous (class C) forest, developing on an abandoned ield (Photo Timo Kuuluvainen). Overall, we conclude that the past human impact on the current forest structures on the Zaonezhye peninsula can be clearly seen, but also primeval forests of negligible human impact can be found in more remote locations. The cessation of major human inluence some dozens of years ago have led to large scale recovery and restoration of natural forest features in many areas. This together with the occurrence of primeval forests of highest conservation priority and culturally modiied habitats, opens up promising prospects for designing eficient forest conservation area networks for protection of biodiversity on the Zaonezhye peninsula. REFERENCES BrЮЦОХТs, G., JШЧssШЧ, B.G., KШЮФТ, J., KЮЮХЮЯКТЧОЧ, T. & SСШrШСШЯК, E. 2011. FШrОsЭ ЧКЭЮrКХЧОss ТЧ ЧШrЭСОrЧ EЮrШЩО: ЩОrsЩОМЭТЯОs ШЧ ЩrШМОssОs, sЭrЮМЭЮrОs КЧН sЩОМТОs НТЯОrsТЭв. – SТХЯК FОЧЧТМК 45(5): 807–821. FrТНЦКЧ, J. & АКХСОТЦ, M. 2000. AЦШЮЧЭ, sЭrЮМЭЮrО, КЧН НвЧКЦТМs ШП НОКН аШШН ШЧ ЦКЧКРОН ПШrОsЭХКЧН ТЧ SаОНОЧ. FШrОsЭ EМШХШРв КЧН MКЧКРОЦОЧЭ, 131: 23–36. HЮЭЭЮЧОЧ, P. 1980. EКrХв ХКЧН ЮsО, ОsЩОМТКХХв ЭСО sХКsС-КЧН-ЛЮrЧ МЮХЭТЯКЭТШЧ ТЧ ЭСО МШЦЦЮЧО ШП LКЦЦТ, sШЮЭСОrЧ FТЧХКЧН, ТЧЭОrЩrОЭОН ЦКТЧХв ЮsТЧР ЩШХХОЧ КЧН МСКrМШКХ КЧКХвsОs. – AМЭК BШЭКЧТМК FОЧЧТМК 113: 1–45. IСКХКТЧОЧ, A. & MтФОХт, H. 2009. KЮШХХООЧ ЩЮЮsЭШЧ Цттrт EЭОХт- УК PШСУШТs-SЮШЦОssК 2004–2007. – MОЭsтЭТОЭООЧ КТФКФКЮsФТrУК 1:35–56. (IЧ FТЧЧТsС). JЮЧЧТЧОЧ, K., SТЦТХт, M., KШЮФТ, J. & KШЭТrКЧЭК, H. 2006. AssОЦЛХКРОs ШП аШШН ТЧСКЛТЭТЧР ПЮЧРТ КХШЧР ЭСО РrКНТОЧЭs ШП sЮММОssТШЧ КЧН ЧКЭЮrКХЧОss ТЧ ЛШrОКХ ЩТЧО НШЦТЧКЭОН ПШrОsЭs ТЧ FОЧЧШsМКЧНТК. – EМШРrКЩСв 29: 75–83. MКrЭТФКТЧОЧ, P., SТТЭШЧОЧ, J., PЮЧЭЭТХК, P., KКТХК, L. & RКЮС, J. 2000. SЩОМТОs rТМСЧОss ШП CШХОШЩЭОrК ТЧ ЦКЭЮrО ЦКЧКРОН КЧН ШХН РrШаЭС ЛШrОКХ ПШrОsЭs ТЧ sШЮЭСОrЧ FТЧХКЧН. – BТШХШРТМКХ CШЧsОrЯКЭТШЧ 94: 199–209. PОЧЭЭТХт, R., SТТЭШЧОЧ, J. & KЮЮsТЧОЧ, M., 2004. PШХвЩШrО НТЯОrsТЭв ТЧ ЦКЧКРОН КЧН ШХН-РrШаЭС ЛШrОКХ PТМОК КЛТОs ПШrОsЭs ТЧ sШЮЭСОrЧ FТЧХКЧН. – BТШХШРТМКХ CШЧsОrЯКЭТШЧ 117: 271–283. RШЮЯТЧОЧ, S., KЮЮХЮЯКТЧОЧ, T. & KКrУКХКТЧОЧ, L. 2002. CШКrsО аШШНв НОЛrТs ТЧ ШХН PТЧЮs sвХЯОsЭrТs НШЦТЧКЭОН ПШrОsЭs КХШЧР К РОШРrКЩСТМ КЧН СЮЦКЧ ТЦЩКМЭ РrКНТОЧЭ ТЧ ЛШrОКХ FОЧЧШsМКЧНТК. – CКЧКНТКЧ JШЮrЧКХ ШП FШrОsЭ RОsОКrМС 32: 2184–2200. SТЦТХт, M., KШЮФТ, J. & MКrЭТФКТЧОЧ, P. 2003. SКЩrШбвХТМ ЛООЭХОs ТЧ ЦКЧКРОН КЧН sОЦТЧКЭЮrКХ SМШЭs ЩТЧО ПШrОsЭs: qЮКХТЭв ШП НОКН аШШН ЦКЭЭОrs. – FШrОsЭ EМШХШРв КЧН MКЧКРОЦОЧЭ 174: 365–381. TТФФКЧОЧ, O.-P. & CСОrЧвКФШЯК, I.A. 2014. PКsЭ СЮЦКЧ ЩШЩЮХКЭТШЧ СТsЭШrв КППОМЭs МЮrrОЧЭ ПШrОsЭ ХКЧНsМКЩО sЭrЮМЭЮrО ШП VШНХШгОrШ NКЭТШЧКХ PКrФ, NШrЭСаОsЭ RЮssТК. – SТХЯК FОЧЧТМК. TТФФКЧОЧ, O.-P., RЮШФШХКТЧОЧ, A. & HОТФФТХт, R. 2014. RОМШЯОrв ШП ЛШrОКХ ПШrОsЭ ЧОКr КЛКЧНШЧОН ЯТХХКРОs ТЧ аОsЭОrЧ АСТЭО SОК KКrОХТК, RЮssТК. – SМКЧНТЧКЯТКЧ JШЮrЧКХ ШП FШrОsЭ RОsОКrМС 29: 152–161. 130 Reports of the Finnish Environment Institute 40 | 2014 2.5 Mires of the Zaonezhye Peninsula Oleg Kuznetsov*, Pavel Tokarev*, Stanislav Kutenkov*, Vladimir Antipin* and Tapio Lindholm** * Institute of Biology of the Karelian Research Centre of Russian Academy of Sciences, Petrozavodsk. 11 Pushkinskaya St., 185003 Petrozavodsk, Karelia, Russia ** The Finnish Environment Institute (SYKE), P.O.Box 140, 00251 Helsinki, Finland. Corresponding author: Tapio Lindholm E-mail: tapio.lindholm@ymparisto.i Introduction Mire ecosystems play an essential role in the boreal zone, both in landscape functioning and in biodiversity conservation. Since the mid-20th century, mires in the southern parts of the Republic of Karelia have been extensively drained for forestry and agriculture. Due to these practices, there has been a need for special research and decision making to protect the diversity of wetland ecosystems in the republic (Antipin & Kuznetsov 1998). Since 1950, the Mire Ecosystems Laboratory of the Institute of Biology of the Karelian Research Centre Russian Academy of Sciences has carried out multidisciplinary studies on wetland vegetation, stratigraphy, dynamics and natural resources, as well as their management and protection in the European North of Russia and adjacent regions (Kuznetsov 2003, Elina & Kuznetsov 2006, Elina et al. 2010). For nearly 30 years, the Mire Ecosystems Laboratory has been studying wetland diversity in eastern Fennoscandia as well as mire conservation issues in collaboration with colleagues from Finland (Heikkilä et al. 1997, 2001, Kuznetsov et al. 2012). Zaonezhye Peninsula lies between two long bays in the northern part of Lake Onega. Its nature is quite different from other parts of eastern Fennoscandia. First, the vegetation is highly diverse owing to the mineral-rich bedrock and soils. Secondly, the dissected terrain and the small size of mires have spared them from large-scale draining. Even though Zaonezhye has been inluenced by human activities already for a millennium, there are still substantial areas of undisturbed nature, which are of high conservation value for the entire Northern Europe. Different types of mires are the best-preserved ecosystems in Zaonezhye. Therefore, special research on mire ecosystems has been carried out within the project “Barents Protected Area Network, BPAN”, resulting in proposals for biodiversity conservation in Zaonezhye. Reports of the Finnish Environment Institute 40 | 2014 131 Study area Zaonezhye Peninsula features two contrasting landscapes: highly dissected tectonic-denudation ridge landscape in the northwestern and central parts, and glacial lacustrine plain landscape in the eastern and southeastern parts of Zaonezhye. The contrasting landscapes have shaped the patterns of paludiication as well as the distribution of mire types in the peninsula. The Mire Ecosystems Laboratory of the Institute of Biology of the Karelian Research Centre RAS has carried out botanical and stratigraphic surveys on some of the mires since 1951. A part of the results have been published (Kozlova 1971, Antipin et al. 1993, 1994, Dyachkova et al. 1993, Kuznetsov & Khokhlova 1994, Elina et al. 1999, Kuznetsov et al. 1999, 2000, 2013, Maksimov 2005). These results have also been used in preparing this paper. Material and methods Satellite imagery and in situ surveys revealed 642 undrained mires, covering an area of 15 000 ha. In Zaonezhye, small mires (0.5–10 ha) are widespread, whereas large mires (more than 200 ha) are few. In general, large mires represent mire systems that consist of several massifs, sometimes including different types of mires (Tab. 1, Fig. 1). In the Russian tradition of mire research, a mire massif has been the main object of research. According to this research tradition, individual mires develop in individual depressions. As depressions are illed with peat and expand, individual massifs become connected in mire systems. Mire massifs are classiied based on the composition and structure of plant cover in the central part, as well as the distribution of plant communities along the centre-to-margin gradient of the mire massif (Tsinzerling 1938, Elina et al. 1984, Yurkovskaya 1992). According to Yu.D. Tsinzerling (Tsinzerling 1938), aapa mire massifs also include minerotrophic fens where the central part consists of string-lark or hummock-lack systems. There is a sparse cover of herbs or herbs and mosses on the wet larks, and peat accumulation has either slowed down or ceased (Kuznetsov 1986, 2003). In this study, peat types were determined according to Russian classiication (Tyuremnov 1976), which includes distinctive features for Karelia (Elina et al. 1984). Vegetation dynamics of mires were reconstructed by analysing the botanical composition of peat. Samples were analysed microscopically (with 5% precision) and plant macrofossils were identiied (Korotkina 1939). Based on these data, diagrams were plotted to determine paleacommunities, determined by the dominant plant species in each stratum. Computer programme “Korpi” was used to draw these diagrams (Kutenkov 2013 a). Mire types with similar ecological properties, as well as those dificult to identify in satellite images, were grouped together. Thus, type V (Fig. 1) comprises herbaceous mires on lakeshores as well as herbaceous and herb-moss mires in depressions, which have a pronounced herbaceous cover despite not being associated with lakes. Results and discussion Mapped mires cover 7.6% of the peninsula. Nearly a half of the mires are minerotrophic, forested mires. The tree stands consist of different species and their canopy closure is 40% or higher. There are also areas of paludiied forests (with less than 30-cm-thick peat deposits) that raise the degree of paludiication on the peninsula to around 10%. A large amount of mires in the eastern and southeastern parts of the peninsula have been drained and converted into farmland. Altogether 38 drained mire massifs with a combined area of 3207 ha were identiied from cartographic materials (Peatland … 132 Reports of the Finnish Environment Institute 40 | 2014 1979) and satellite images (Fig. 2). There has been hardly any drainage for forestry, which has affected no more than 300 ha in the northern part of the peninsula. In Zaonezhye, mires occupy tectonic and glacial depressions, as well as overgrow bays of Lake Onega and other inland waterbodies. As a result, mires have a NW-SE orientation, which can be clearly seen in Figure 1. The mires of Zaonezhye were formed at different times. In higher parts of the peninsula, where the waters of Lake Onega retreated earlier, mires began forming 8000–9000 BP; whereas in the Lake Onega bays, mire formation occurred 3000–5000 BP (Elina et al. 1999, Kuznetsov et al. 1999). These mires are of both terrestrial and lacustrine origin. In tectonic depression, lacustrine-paludal deposits are often ive to seven (or nine) metres, and sapropel deposits one to several meters thick. In one herbaceous mire on the southern shore of Lake Karasozero, there is over eight metres of sapropel, with a metre of quagmire peat on top. There are also mires in depressions, resembling gullies, with four to six metres of peat deposits of terrestrial origin. Examples of peat stratigraphy and formation of massifs are given below. In moraine and lacustrine sediments, as well as in the Lake Onega bays, peat deposits are thinner (between one and three metres). Table 1. Types of mire massifs on Zaonezhye Peninsula. Type of mire massif Number Number Area, ha (%) Min. and max. area of massif, ha Min. and max. area of massif, ha Ombrotrophic ridge-hollow bogs (raised bogs) (I) Average area of massif, ha 238 61 – 358 Ombrotrophic pine-dwarf shrub-cottongrass-Sphagnum bogs (pine bogs) (II) Min. and max. area of massif, ha 12 0.5 – 200 Mesotrophic tree-grass-Sphagnum mires (III) 1730 (12) 14 0.5 – 184 Mesoeutrophic string-lark aapa mires (IV) 7 326 (2) 82 1 – 168 Mesoeutrophic and eutrophic herb-moss and herb mires (V) 118 2003 (13) 15 0.5 – 330 Minerotrophic forested mires (VI) 105 7378 (49) 77 2– 586 Undetermined mire type (VII)* 82 367 (3) 4 0.5– 19 Total 642 15064 (100) 24 0.5-586 *These include small mires whose plant cover could not be determined. Zaonezhye Peninsula is characterized by basic and ultrabasic bedrock, whose clasts are found also in Quaternary sediments. As a consequence, groundwater discharge to mires is highly mineralized and minerotrophic mires are widespread (Tab. 1). It has made little sense to drain mires in the ridge landscape due to the topography and the small size of mires. Therefore, nearly all mires on the peninsula remain intact. As a result, the mires of Zaonezhye feature a high diversity at several levels of ecosystem organization. The mires of Zaonezhye contain around 240 vascular plant species, which is over 70% of the entire mire lora in Karelia (Kuznetsov 2012). There are several regionally red-listed species (Ivanter & Kuznetsov 2007), including Epipactis palustris, Malaxis monophyllos and Dactylorhiza traunsteineri, as well as a number of Siberian species at the western limit of their distribution that are relatively rare in Fennoscandia, including Ligularia sibirica and Rubus humulifolius. The moss lora of the Zaonezhye mires is also relatively comprehensive. There are around 90 species, which account for more than 60% of the moss lora of Karelian mires. Also rare species occur, some of which are at the limit of their range, including Sphagnum pulchrum, S. lindbergii, S. Reports of the Finnish Environment Institute 40 | 2014 133 aongstroemii, Hamatocaulis vernicosus and Loeskypnum badium (Boychuk & Kuznetsov 2000, Maksimov & Syrjanen 2014). Also, the plant communities of Zaonezhye mires are highly diverse. They represent more than a half of known syntaxa of mire vegetation in Karelia (Kuznetsov, 2003, 2012). Especially noteworthy is the wide range of eutrophic communities of herbaceous and herb-moss mires as well as tree-herb-moss mires. These mires are of high conservation value for the whole of Northern Europe. Below we give a short description of plant cover and formation patterns of the main types of mire massifs in Zaonezhye. Ombrotrophic ridge-hollow Sphagnum bogs occupy 956 ha (6%) and comprise several relatively large mire systems (Yuno, Pivgozerskoe, and Koybozerskoe) in Zaonezhye. Their central parts are characterized by a ridge-hollow or hummock-hollow microtopography (Fig. 3). Dwarf shrub-Sphagnum communities with Sphagnum fuscum (sometimes S. magellanicum) and the occasional pine grow on the ridges, whereas the hollows are dominated by Sphagnum balticum and Eriophorum vaginatum, sometimes Scheuchzeria palustris. These mires may also have narrow water tracks, occupied by mesotrophic sedge-Sphagnum communities (Carex rostrata – Sphagnum fallax). The mire margins are covered by pine-cottongrass-dwarf shrub-Sphagnum communities, which are also habitats of cranberry and cloudberry. Among these mires, of particular conservation value is the Koybozerskoe mire, where moss species rare for Zaonezhye have been found, including Sphagnum pulchrum, S. lindbergii and S. aongstroemii (Kuznetsov et al. 2000). Ombrotrophic pine-dwarf shrub-cottongrass-Sphagnum bogs occupy ca. 2300 ha (15%) in Zaonezhye. These mires are represented by a large number of small mire massifs, ranging from 0.5 to 10 ha, and only a few mires larger than 100 ha. Their tree stands are sparse (with a canopy closure of 0.2–0.4%) and their tree layers are 4–10 m (sometimes 12–14 m) tall. The ground cover is dominated by Rubus chamaemorus, which is a common dwarf shrub on wetlands. Also Eriophorum vaginatum is often present. There is a continuous moss cover, comprising Sphagnum angustifolium, S. magellanicum, S. russowii, S. fuscum, S. capillifolium and Pleurozium schreberi in different proportions. There is little variation in microtopography, although dwarf shrubs are more abundant in elevated areas around tree trunks. These mires are usually relatively shallow (2–3 m thick). In most cases their formation began with minerotrophic stages. A proile of this type of mire is shown in Figure 4. Its formation began with a eutrophic horsetail-Sphagnum community (Borehole 2), which was soon replaced by a cottongrass-Sphagnum mesotrophic community, followed by an ombrotrophic stage. Peat bog deposits in the mire are two metres thick. At the margins (Boreholes 1 and 3) the mire has not gone though a minerotrophic stage. Aapa mires occupy 326 ha (2%) of the peninsula. These mires are conined to narrow depressions and abundantly fed by groundwater from the mineral banks. They form a part of a number of mire systems, together with other types of mire massifs. Central parts of aapa mires are characterized by string-lark and hummock-lark complexes, with herbaceous or herb-Hypnum larks. The formation of these complexes in the aapa mires of Zaonezhye began relatively recently. Therefore, the strings are low (10–20 cm) and the herbaceous cover of the larks is relatively dense. These complexes occupy 20–30% of the area of the massifs. Owing to highly mineralized groundwater and a high low rate, the vegetation of the complexes is eutrophic or mesoeutrophic. Microtopographic elevations are covered by herb-Sphagnum (Sphagnum centrale, S. warnstorii, S. subfulvum, S. teres) communities. The ield layer is dominated by Carex lasiocarpa and Molinia caerulea, with frequent Potentilla erecta and Trientalis europaea, as well as Juniperus communis and short pines. The larks host herbaceous and herb-Hypnum (Warnstoria exannulata, Scorpidium scorpioides) communities, sometimes with 134 Reports of the Finnish Environment Institute 40 | 2014 Sphagnum subsecundum and S. teres. The ield layer consists of sedges (Carex lasiocarpa, C. limosa, C. livida, C. chordorrhiza), Menyanthes trifoliata, Equisetum luviatile and Utricularia intermedia. Most of the area in aapa mires is occupied by herb-moss eutrophic and mesoeutrophic communities, and there is little variation in microtopography. The rims of aapa mires are covered by mesotrophic tree-herb-Sphagnum communities. Due to this feature, aapa mires in Zaonezhye are similar to herb-moss mires, which makes identifying these two types in satellite images and in-situ surveys problematic. Kalegubskoe mire massif (№ 15, Fig. 1) illustrates the formation of aapa mires. It covers 168 ha in a deep and narrow tectonic depression, which is over 5 km long, and its waters discharge to Lake Onega. The peat deposits of Kalegubskoe mire are 5.5 metres thick (Fig. 5, 6). Its formation began with eutrophic birch-reed communities (stage I, Fig. 6). These communities persisted for several millennia, during which the mire underwent changes in herb and moss cover composition (stages II, III). As a result, there are four metres of woody and woody-herbaceous fen peat deposits on Kalegubskoe mire. The central part of the mire is covered by 1.5 metres of sedge fen peat deposits from sedge-moss communities (stage IV). This is a typical situation for aapa mires, which have been developing since the early sub-Atlantic period (ca. 2500 BP) (Kuznetsov, 1986). A cooling climate and increased moisture were the driving forces in the formation of these mires, causing a rise in water level and water retention. In this speciic mire, trees have been replaced by wet herb-moss aapa complexes. Eutrophic and mesoeutrophic herb-moss mires develop in basins with an ample groundwater feed, sometimes from springs. These and mires on lakeshores together make up 13% of all the mires on the peninsula. Herb-moss mires feature a relatively diverse plant cover. The ield layer consists of various sedge species with several wetland herbs. The moss cover is composed of both Sphagna (Sphagnum obtusum, S. subsecundum, S. teres, S. centrale), and Bryidae (Warnstoria exannulata, Hamatocaulis vernicosus, Cynclidium stygium, Campylium stellatum, Paludella squarrosa, Scorpidium scorpioides, Tomentypnum nitens). The microtopography of the mires is indistinct, and the peat accumulation rate is high. There are only a few woody plants. Among them, Picea x fennica with drooping tops usually grow around hummocks, associated with groundwater springs. The lora of these mires comprises a number of rare and calciphile species, including Epipactis palustris, Malaxis monophyllos, Bistorta major, Rumex fontanopaludosus, Ligularia sibirica and Dactylorhiza traunsteineri. Dlinnoe mire (№ 7, Fig. 1) is a system of several herb-moss mire massifs, formed in narrow tectonic depressions. It consists of small ombrotrophic dwarf shrub-Sphagnum mires that are not looded by groundwater. At the centre of one of the mire massifs is Lake Chelozero. A stratigraphic proile has been established 100 metres south of the lake (Fig. 7). In this part, the depth of the mire is up to 6.5 metres. The lower strata of the deposit are made up of woody and woody-reed fen peat, suggesting that the mire developed from birch-reed communities on land. (Fig. 8, stage I). In this part of the mire, the lake has luctuated and its waters have spilled (as the lake has expanded) onto the mire surface more than once over the history of the mire. As a result, there are 0.5–1.5 m thick water lenses in the peat deposit (Fig. 7, boreholes 4, 5; Fig. 8, stages II, V). The analysis of plant succession from borehole 4 (Fig. 8) revealed a 75 cm water lens (II), suggesting that soon after 0.5 m of woody-reed peat was deposited, the mire was looded again (stage 1). Subsequently, a eutrophic reed-Sphagnum community (III) was formed, soon replaced by a meso-oligotrophic cottongrass-Sphagnum community (IV) with Sphagnum angustifolium. This succession means that there was no longer groundwater supply to the central part of the mire. Another two-metres-thick water lens (V) indicates yet another looding of the site. Eventually, the waterbed was covered with a loating mat, consisting of a mesotrophic Scheuchzeria-Sphagnum community with Sphagnum obtusum (VI), followed by a me- Reports of the Finnish Environment Institute 40 | 2014 135 so-oligotrophic cottongrass-Sphagnum community (VII) with Sphagnum magellanicum. In the deposit, the transition to an ombrotrophic stage (VIII) with Sphagnum fuscum is visible at the depth of one metre. This small (ca. 30 m wide) dwarf shrub-cottongrass-Sphagnum community in the centre of the mire has no inlux of groundwater. It is surrounded on all sides by eutrophic herb-moss communities. The vegetation dynamics of a sedge-Sphagnum community (borehole 3 in Fig. 7) are shown in Fig. 9. Also this part of the mire began with a tree-reed community (stage I), which was replaced by reed-Sphagnum communities (stages II, III). These communities persisted several millennia, resulting in 3.5-metre deposits of herb-Sphagnum fen peat. In the top 25 cm of the peat deposit, there is evidence of a recent rise in water content and reduction in low rate, which have driven plant succession at the site (stage IV). As a result, the hydrophilous Sphagnum subsecundum has increased, whereas reeds have nearly disappeared. On lakeshores, communities of herbaceous mires dominated by Carex elata spp. omskiana, C. diandra, C. cespitosa, C. vesicaria, Phragmites australis, Equisetum palustre, Comarum palustre and Menyanthes trifoliate are widespread (Fig. 10). These communities consist of over 100 vascular plant species, including a number of semi-aquatic plants that are not found in any other types of mires. Depending on the duration of spring and summer loods, the moss cover is either poor or completely missing in these mires. Their relatively shallow (1–2 m) peat deposits consist of herbaceous peat with high ash content (Kuznetsov et al. 2000). Mesotrophic tree-grass-Sphagnum mires cover 1730 ha (12%) in Zaonezhye. These small mire massifs occupy depressions of different genesis. Their tree layer consists of pine and birch stands that are between 3–4 and 6–8 metres high, with a canopy closure of 0.2–0.3. The ield layer is made up of sedges, wetland herb species and occasionally reeds. In addition, hummocks around tree trunks are often covered with wetland dwarf shrubs. There is also a continuous moss cover, dominated by Sphagnum angustifolium, with Sphagnum centrale, S. russowii, S. magellanicum and S. teres. Forested mires account for half of the total area of mires in Zaonezhye. Forested mires occur on moraine plains as well as in depressions in the ridge terrain. These mire massifs range in size from two to several hundred hectares, and nearly all of them are minerotrophic. The mires are of different genesis and their lacustrine-paludal deposits range from 0.5–1 to 5.5 metres in depth. Forested mires have a highly diverse plant cover, consisting of a wide range of tree-grass and tree-grass-moss communities. The tree stands are between 10–12 to 20–22 metres tall and their canopy closure is 0.4–0.7%. There are single-species as well as mixed stands of pine, spruce, downy birch and black alder on these mires (Kutenkov 2013 b). Forested mire communities either form separate mire massifs, or occur at the margins of other mires. Eutrophic spruce, birch and black alder stands are widespread. Their herbaceous ield layer is dominated by Filipendula ulmaria, sometimes Phragmites australis, sedges (Carex cespitosa, C. vesicaria, C. rostrata) and Calla palustris. The microtopography of these mires is characterized by wet microdepressions and high hummocks around tree trunks. Due to the high diversity of microhabitats, there is also a high diversity of plant communities: Up to 57 vascular plant species and 20 moss species have been found from one site. In forested mires, the moss cover is discontinuous and consists of a number of eutrophic species, including Sphagnum warnstorii, S. squarrosum, S. teres, S. centrale, Tomentypnum nitens, Campylium stellatum, Scorpidium revolvens, Calliergon cordifolium, Pseudobryum cinclidioides, Plagiomnium ellipticum and Calliergonella cuspidata. Sphagnum angustifolium, S. russowii and other forest bryophytes grow on the hummocks around tree trunks, together with dwarf shrub and herb species, associated with forests. Of special interest are eutrophic herb-Sphagnum pine mires, where Molinia caerulea dominates the ield layer. These mires are associated with carbonaceous bedrock and 136 Reports of the Finnish Environment Institute 40 | 2014 contain a number of calciphile species. Their moss layer is dominated by Sphagnum warnstorii, although other eutrophic species are also present. In Zaonezhye, mesotrophic grass-Sphagnum pine mires as well as bilberry-Sphagnum and horsetail-Sphagnum spruce mires are rare and small. Also ombrotrophic dwarf shrub-Sphagnum pine mires are rare. Overall, the lora of forested mires in Zaonezhye consists of 155 vascular plant species and 68 moss species. Due to their species diversity, the mires of Zaonezhye are of high conservation value (Kutenkov 2013 b). Mires conservation in Zaonezhye The Kizhy federal nature reserve was established to protect the diverse ecosystems of the skerries in the southestern part of Zaonezhye. There are also herbaceous mires on the lakeshores within the boundaries of the reserve. In addition, seven regional mire nature monuments have been established on Zaonezhye Peninsula (Tab. 2, Fig. 1). Also a number of other, both representative and unique, mires merit a conservation status (Tab. 2; Fig. 1). A feasibility study that has been carried out for the Zaonezhye landscape reserve and is under discussion at the Ministry of Nature Use and Environment of the Republic of Karelia (Gromtsev 2013). If the landscape reserve is established, all these mires will be protected and the biodiversity of mire ecosystems in Zaonezhye will be conserved. REFERENCES AЧЭТЩТЧ, V.K. & KЮгЧОЭsШЯ, O.L. 1998. . ., . . ДCШЧsОrЯКЭТШЧ ШП НТЯОrsТЭв ШП ЦТrОs ТЧ KКrОХТКЖ. – IЧ: KЮгЧОЭsШЯ, O.L. (ОН.), BТШНТЯОrsТЭв, НвЧКЦТМs КЧН МШЧsОrЯКЭТШЧ ШП ЦТrО ОМШsвsЭОЦs ТЧ ОКsЭОrЧ FОЧЧШsМКЧНТК. KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs PОЭrШгКЯШНsФ. Щ. 10–30. (IЧ RЮssТКЧ). AЧЭТЩТЧ, V.K., TШФКrОЯ, P.N. & SСОЯОХТЧ, P.F. 1993. . ., . ., . . , ДMТrО ШП ГКШЧОгСвО ЩОЧТЧsЮХК, ЭСОТr ЦОКЧТЧР КЧН МШЧsОrЯКЭТШЧЖ. – KТгСsФвТ ЯОsЭЧТФ 2: 79–87. (IЧ RЮssТКЧ). 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(55 ) ДTСО СТsЭШrв КЧН МЮrrОЧЭ sЭКЭЮs ШП ЦТrО rОsОКrМС ТЧ KКrОХТК. 55 вОКrs ЭШ MТrО EМШsвsЭОЦs LКЛШrКЭШrвЖ. − IЧ: KЮгЧОЭsШЯ, O.L., DУКМСФШЯК, T.ВЮ., ГЧКЦОЧsФТв S.R. (ОНs.), MТrО EМШsвsЭОЦs ТЧ NШrЭСОrЧ EЮrШЩО: DТЯОrsТЭв, DвЧКЦТМs, CКrЛШЧ BКХКЧМО, RОsШЮrМОs КЧН CШЧsОrЯКЭТШЧ. PrШМ. ШП IЧЭОrЧКЭТШЧКХ SвЦЩШsТЮЦ. PОЭrШгКЯШНsФ. Щ. 11–34. (IЧ RЮssТКЧ). EХТЧК, G.A., KЮгЧОЭsШЯ, O.L. & MКФsТЦШЯ, A.I. 1984. . ., . ., . . – . ДSЭrЮМЭЮrКХ КЧН ПЮЧМЭТШЧКХ ШrРКЧТsКЭТШЧ КЧН НвЧКЦТМs ШП ЦТrО ОМШsвsЭОЦs ТЧ KКrОХТКЖ. – LОЧТЧРrКН: 128 Щ. (IЧ RЮssТКЧ). EХТЧК, G.A., LЮФКsСШЯ, A.D., FТХТЦШЧШЯК, L.V. & KЮгЧОЭsШЯ, O.L. 1999. . ., . ., . ., . . ДLКЭО GХКМТКХ-HШХШМОЧО ЩКХОШЯОРОЭКЭТШЧ sЮММОssТШЧs ТЧ ЭСО ГКШЧОгСвО PОЧТЧsЮХК КЧН ЭСОТr НОЩОЧНОЧМО ШЧ LКФО OЧОРК ХОЯОХsЖ. – BШЭКЧТМСОsФв ГСЮrЧКХ 84 (6): 32–52. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 137 EХТЧК, G., LЮФКsСШЯ, A., ВЮrФШЯsФКвК, T. 2010: LКЭО GХКМТКХ КЧН HШХШМОЧО ЩКХКОШЯОРОЭКЭТШЧ КЧН ЩКХКОШРОШРrКЩСв ШП EКsЭОrЧ FОЧЧШsМКЧНТК . − TСО FТЧЧТsС EЧЯТrШЧЦОЧЭ 2010/4: 1–304. GrШЦЭsОЯ, A.N. (ОН.), 2013. . . ( .). : , ДSОХФК LКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ CСКrКМЭОrТsЭТМs, LКЧН UsО, CШЧsОrЯКЭТШЧЖ. – KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs PОЭrШгКЯШНsФ: RAS. 180 Щ. (IЧ RЮssТКЧ). HОТФФТХт, R., KЮгЧОЭsШЯ, O. & LТЧНСШХЦ, T. 1997: – CШЦЩКrТsШЧ ШП ЭСО ЯОРОЭКЭТШЧ КЧН НОЯОХШЩЦОЧЭ ШП ЭСrОО ЦТrОs ТЧ EХТЦвssКХШ NКЭЮrО RОsОrЯО. – LТЧНСШХЦ, T., HОТФФТХт, R. & HОТФФТХт, M. (ОНs.), : EМШsвsЭОЦs, ПКЮЧК КЧН lШrК ШП ЭСО FТЧЧТsС-RЮssТКЧ NКЭЮrО RОsОrЯО FrТОЧНsСТЩ. – SЮШЦОЧ вЦЩтrТsЭö 124: 63–82. HОТФФТХӓ, R., KЮгЧОЭsШЯ, O., LТЧНСШХЦ, T., AКЩКХК, K. & SСОЯОХТЧ, Щ. 2001. CШЦЩХОбОs, ЯОРОЭКЭТШЧ, lШrК КЧН НвЧКЦТМs ШП KКЮСКЧОЯК ЦТrО sвsЭОЦ, аОsЭОrЧ FТЧХКЧН. – TСО FТЧЧТsС EЧЯТrШЧЦОЧЭ 489. Щ. 1–97 IЯКЧЭОr, E.V. & KЮгЧОЭsШЯ, O. L. (ОНs.), 2007. . ., . . ( .). ДRОН DКЭК BШШФ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ. KКrОХТК. 368 Щ. (IЧ RЮssТКЧ). KШrШЭФТЧК, M. I. 1939. . . ДMКМrШПШssТХ КЧКХвsТs ШП ЩОКЭЖ. - IЧ: NОЮsМСЭКНЭ M.I. (ОН.) MОЭСШНs ПШr ТЧЯОsЭТРКЭТШЧs ШП ЩОКЭ ЦТrОs. PКrЭ II. MШsМШа. Щ. 5–59. (IЧ RЮssТКЧ). KШгХШЯК, R.P. 1971. . . ДVОРОЭКЭТШЧ КЧН sЭrКЭТРrКЩСв ЦКТЧ ЦТrО ЭвЩОs ТЧ sШЮЭС KКrОХТКЖ. − IЧ: LШЩКЭТЧ V.D. (ОН.) ArЭТМХОs ШЧ ЩХКЧЭ МШЯОr ШП KКrОХТКЧ ASSR. PОЭrШгКЯШНsФ: KКrОХТК. Щ. 73–94. (IЧ RЮssТКЧ). KЮЭОЧФШЯ, S.A. 2013 К. . . «KШrЩТ» ДKШrЩТ sШПЭаКrО ПШr ЩХШЭЭТЧР sЭrКЭТРrКЩСТМ НвЧКЦТМs ШП ЩОКЭ МШЦЩШsТЭТШЧ МСrШЧТМХОЖ. – PrШМООНТЧРs ШП ЭСО KКrОХТКЧ RОsОКrМС CОЧЭrО ШП ЭСО RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. EМШХШРТМКХ SЭЮНТОs SОrТОs 6: 171–176. (IЧ RЮssТКЧ). KЮЭОЧФШЯ, S. . 2013 Л. . . ДMТrО ПШrОsЭsЖ. – IЧ: GrШЦЭsОЯ A.N. (ОН.), SОХФК LКЧНscapes of the Zaonezhskii Peninsula: Natural Characteristics, Land Use, Conservation. Karelian Research CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 61–65. (IЧ RЮssТКЧ). KЮгЧОЭsШЯ, O. 1986. TСО sЭrЮМЭЮrО КЧН КРО ШП rТНРО-СШХХШа ККЩК ЦТrОs МШЦЩХОбОs. − PЮЛХТМКЭТШЧ ШП KКrОХТКЧ IЧsЭТЭЮЭО, JШОЧsЮЮ UЧТЯОrsТЭв 79: 73–79. KЮгЧОЭsШЯ, O.L. 2003. MТrО ЯОРОЭКЭТШЧ. − IЧ: BТШЭТМ НТЯОrsТЭв ШП KКrОХТК: МШЧНТЭТШЧs ШП ПШrЦКЭТШЧ, МШЦЦЮЧТЭТОs КЧН sЩОМТОs. GrШЦЭsОЯ, A., KТЭКОЯ, S., KrЮЭШЯ, V., KЮгЧОЭsШЯ, O., LТЧНСШХЦ, T.& ВКФШЯХОЯ, E. (ОНs.), – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 57–63. KЮгЧОЭsШЯ, O. L. 2012. MТrО lШrК КЧН ЯОРОЭКЭТШЧ КЧН ЭСОТr МШЧsОrЯКЭТШЧ ТЧ ЭСО RОЩЮЛХТМ ШП KКrОХТК, RЮssТК. − IЧ: LТЧНСШХЦ, T. & HОТФФТХт, R. (ОНs.), MТrОs ПrШЦ ЩШХО ЭШ ЩШХО. TСО FТЧЧТsС EЧЯТrШЧЦОЧЭ 38/2012: 133–142. KЮгЧОЭsШЯ, O. L., DУКМСФШЯК, T.ВЮ., & GrКЛШЯТФ, S.I. 2000. . ., . ., . . ДMТrОsЖ − IЧ: GrШЦЭsОЯ, A., KТЭКОЯ, S., KrЮЭШЯ, V., KЮгЧОЭsШЯ, O., LТЧНСШХЦ, T. & ВКФШЯХОЯ, E. (ОНs.), Biotic diversity of Karelia: conditions of formation, communities and species. Karelian Research Centre of RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 71–83. (IЧ RЮssТКЧ). KЮгЧОЭsШЯ, O. L., SЭШТФТЧК N.V., & BrКгШЯsФКвК T.I., 1999. . ., . ., . . , « » Д FХШrК, ЯОРОЭКЭТШЧ КЧН РОЧОsТs ШП ЦТrОs ТЧ ЛЮППОr гШЧО ШП ЦЮsОЮЦ “KТгСТ”Ж. – PrШМООНТЧРs ШП KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs 1: 48−54. (IЧ RЮssТКЧ). KЮгЧОЭsШЯ, O.L. & KСШСШХШЯК, T.ВЮ. 1994. . ., . . ДIЦЩШrЭКЧЭ ЧКЭЮrО ШЛУОМЭs ТЧ KТгСТ sФОrrТОs КЧН ГКШЧОгСвО BКвЖ. − KТгСsФвТ ЯОsЭЧТФ 3: 41–55. (IЧ RЮssТКЧ). KЮгЧОЭsШЯ, O., HОТФФТХт, R., LТЧНСШХЦ, T., MтФТХт, M. & FТХТЦШЧШЯК, L. 2012. HШХШМОЧО ЯОРОЭКЭТШЧ НвЧКЦТМs КЧН МКrЛШЧ КММЮЦЮХКЭТШЧ ШП ЭаШ ЦТrОs ТЧ FrТОЧНsСТЩ PКrФ, ОКsЭОrЧ FТЧХКЧН. − IЧ: LТЧНСШХЦ, T. & HОТФФТХт, R. (ОНs.), MТrОs ПrШЦ ЩШХО ЭШ ЩШХО. TСО FТЧЧТsС EЧЯТrШЧЦОЧЭ 2012/38: 91–112. KЮгЧОЭsШЯ, O.L, AЧЭТЩТЧ, V.K. & TШФКrОЯ, P.N. 2013. . ., . ., . . ДMТrОsЖ. − IЧ: GrШЦЭsОЯ A.N. (ОН.) SОХФК LКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ CСКrКМЭОrТsЭТМs, LКЧН UsО, CШЧsОrЯКЭТШЧ. KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. P. 54–61. (IЧ RЮssТКЧ). MКФsТЦШЯ, A.I. 2005. . . “ » ДCШЧЭОЧЭ ШП ЦКМrШ- КЧН ЦТМrШОХОЦОЧЭs ТЧ ЩОКЭ НОЩШsТЭs ШП ЦТrО ОМШsвsЭОЦs ЧОКr PКНЦК ШММЮrrОЧМОЖ. − IЧ: IОsСФШ, E.P. (ОН.), EМШХШРТМКХ ЩrШЛХОЦs ШП ЦКsЭОrТЧР ШММЮrrОЧМО “SrОНЧУКУК PКНЦК”. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 72–81. (IЧ Russian). MКФsТЦШЯ, A.I. & SвrУтЧОЧ, K. 2014. BrвШЩСвЭОs. – IЧ: LТЧНСШХЦ, T., JКФШЯХОЯ, J. & KrКЯМСОЧФШ, A. (ОНs.), Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia. RОЩШrЭs ШП ЭСО FТЧЧТsС EЧЯТrШЧЦОЧЭ IЧsЭТЭЮЭО 2014/40: 179–191. PОКЭХКЧН НОЩШsТЭs ШП KКrОХТКЧ ASSR. 1979. . – MТЧТsЭrв ШП РОШХШРв ШП RЮssТКЧ FОНОrКЭТШЧ. MШsМШа. 636 Щ. (IЧ RЮssТКЧ). TвЮrОЦЧШЯ, S.N. 1976. . . ДPОКЭ НОЩШsТЭsЖ. – MШsМШа, NОНrК. 487 Щ. (IЧ Russian). TгТЧsОrХТЧР, ВЮ. D. 1938. . . ДMТrО ЯОРОЭКЭТШЧЖ. − IЧ: VОРОЭКЭТШЧ ШП USSR. BШЭКЧТМКХ IЧsЭТЭЮЭО ШП ЭСО USSR AМКНОЦв ШП SМТОЧМОs. MШsМШа–LОЧТЧРrКН. Щ. 355–428. (IЧ RЮssТКЧ). ВЮrФШЯsФКвК, T.K. 1992. . . ДGОШРrКЩСв КЧН МКrЭШРrКЩСв ШП ЦТrО ЯОРОЭКЭТШЧ ШП ЭСО EЮrШЩОКЧ RЮssТК КЧН ЧОТЛРСЛШЮrТЧР ЭОrrТЭШrТОsЖ. – SЭ.-PОЭОrsЛЮrР: KШЦКrШЯ BШЭКЧТМКХ IЧsЭТЭЮЭО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. 256 Щ. (IЧ RЮssТКЧ). 138 Reports of the Finnish Environment Institute 40 | 2014 Table 2. Protected and nominated mires. № in Fig. 1 Name 1 Pigma Area, ha 365 Type of mire massif Mire system of M* treegrass-Sphagnum and ME herb mire massifs Conservation status NM**** 2 Lan’ 30 M tree-grass-Sphagnum RC***** 3 Maloe Unitskoe 31 M tree-grass-Sphagnum RC 4 Mire near Nizhnee Pigmosero Lake 101 O** pine bog RC 5 Yuno 249 O raised bog RC near village Mikheeva Selga 79 O pine bog RC 6 Syarg 118 M tree-grass-Sphagnum RC 7 Dlinnoe 330 Mire system of ME herb-moss mire massifs RC 8 Lovosinskoe 26 O pine bog RC 9 near Nizhnee Munosero Lake 75 ME*** herb mire RC 10 Munoserskoe 28 ME herb mire RC 11 Cherkoserskoe 23 O pine bog RC 12 Koiboserskoe 331 Mire system of O raised bog and M tree-grassSphagnum massifs RC 13 Troinoe 3 46 ME aapa mire RC 14 Troinoe 6 64 O raised bog RC 15 Kalegubskoe 168 Mire system of ME aapa mire and ME herb-moss mire massifs NM 16 near Lake Lelikosero 200 O pine bog NM 17 along Lel’rechka River 95 M tree-grass-Sphagnum NM 18 near Lake Kosmosero 10,6 ME aapa mire RC 19 Zamoshye 178 ME herb mire NM 20 near Petrikovo Bay 43 ME herb mire NM 21 Near village Bojarschina 24 ME herb mire NM 22 Kosmoserskoe 379 ME forested mire RC * M –mesotrophic, **O –ombrotrophic, ***ME – mesoeutrophic, ****NM - nature monument, ***** RC –recommended for conservation Reports of the Finnish Environment Institute 40 | 2014 139 Fig. 1. Undisturbed mires in Zaonezhye. I – VI – Types of mire massifs: I – Ombrotrophic ridge-hollow bog (raised bog), II – Ombrotrophic pine-dwarf shrub-cottongrass-Sphagnum bog (pine bog), III – Mesotrophic tree-grass-Sphagnum mire, IV – Mesoeutrophic string-lark aapa mire, V – Mesoeutrophic and eutrophic herb-moss and herb mire; VI – Minerotrophic forested mire, VII – Small mires of undetermined type. 1-22 – Protected and nominated mires. 140 Reports of the Finnish Environment Institute 40 | 2014 Fig. 2. Mires drained for agriculture in Zaonezhye. 1 - eutropic, 2 - mesotrophic, 3 - ombrotrophic Reports of the Finnish Environment Institute 40 | 2014 141 Fig. 3. Central part of an ombrotrophic ridge-hollow bog. (Photo Pavel Tokarev). Fig. 4. Stratigraphic proile of the pine-dwarf shrub-Sphagnum mire. Abbreviations: peat types: eutrophic (1-2): 1- Equisetum-Sphagnum, 2- Sphagnum, mesotrophic (3-4): 3- cottongrass-Sphagnum, 4- Sphagnum, ombrotrophic (5-9): 5-pine- cottongrass, 6- cottongrass- Sphagnum, 7- cottongrass, 8- magellanicum, 9- angustifolium; 10- degree of decomposition (%), 11- borehole number, 12- till, 13- clay 142 Reports of the Finnish Environment Institute 40 | 2014 Fig. 5. Stratigraphic proile of the Kalegubskoe aapa mire. Abbreviations: peat types (1-7): fen types: 1- woody, 2- woody-reed, 3- woody-Menyanthes, 4- sedge, 5- Hypnum-reed, 6- sedge-Menyanthes, 7- Menyanthes-Sphagnum; 8- degree of decomposition (%), 9- borehole number, 10- till, 11- clay. Fig. 6. Plant succession in the central part of the Kalegubskoe mire (borehole 5). PКХКОШМШЦЦЮЧТЭв (sЭКРО): I – Betula+Pinus – Phragmites+Equisetum, II - Betula – Phragmites+ Menyanthes –Warnstoria sp.+Calliergon sЩ., III – Betula+Pinus - Phragmites+ Menyanthes, IV – Carex (chordorrhiza+limosa+rostrate+diandra)+Scheuchzeria palustris – Sphagnum sect. Subsecunda. Reports of the Finnish Environment Institute 40 | 2014 143 Fig.7. Stratigraphic proile of the Dlinnoe mire. Abbreviations: peat types: eutrophic (1-15): 1- woody, 2- woody-reed, 3- woodysedge, 4-woody-grass, 5- sedge, 6- sedge-grass, 7- Menyanthes-sedge, 8- sedge-Sphagnum, 9-reed-Sphagnum, 10- Scheuchzeria-Sphagnum, 11- grass-Sphagnum, 12- cotton grass-Sphagnum, 13- sedge-Bryales, 14-grass-Bryales, 15- Sphagnum, mesotrophic (1618): 16- Scheuchzeria-Sphagnum, 17- cottongrass-Sphagnum, 18- Sphagnum, ombrotrophic (19-20): 19- fuscum, 20- magellanicum; 21- water, 22- degree of decomposition (%), 23- borehole number, 24- till, 2- clay Fig. 8. Plant succession in the central part of the Dlinnoe mire (borehole 4). 144 Reports of the Finnish Environment Institute 40 | 2014 Palaeocommunity (stage): I – Betula – Phragmites, II – water, III – Phragmites + Sphagnum warnstorii+S. centrale, IV – Eriophorum – Sphagnum angustifolium, V –water, VI – Scheuchzeria palustris+Carex rostrate – Sphagnum obtusum, VII – Eriophorum – Sphagnum magellanicum, VIII - Eriophorum – Sphagnum fuscum. Fig. 9. Plant succession in the eutrophic part of the Dlinnoe mire (borehole 3). Palaeocommunity (stage): I – Betula+Pinus – Phragmites, II – Phragmites+Equisetum+Menyantes – Sphagnum centrale+S. teres, III - Phragmites+Carex lasiocarpa – Sphagnum teres+S. warnstorii, IV – Carex lasiocarpa+Trichophorum – Sphagnum sect. Subsecunda. Reports of the Finnish Environment Institute 40 | 2014 145 Fig. 10. Mesoeutrophic herbaceous mire (Photo: V.L. Mironov). 146 Reports of the Finnish Environment Institute 40 | 2014 2.6 Meadows in Zaonezhye Sergey Znamenskiy Institute of Biology, Karelian Research Center of Russian Academy of Sciences. 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia E-mail: seznam@krc.karelia.ru Introduction Zaonezhye Peninsula, or Zaonezhye, is one of the most important grassland areas in Karelia. The total area of seminatural grasslands in Zaonezhye is estimated at 70 km2 (excluding abandoned, reclaimed ields), or approximately 3.5% of the total area. This amount of seminatural grassland is approximately nine times more than the average for Karelia (0.39% by 2012). 90% of the grasslands are located in the eastern lowlands of Zaonezhye that historically have been more suitable for agriculture and, therefore, human settlements. However, since the middle of the 20th century even this part of the region has not been able to meet the needs of modern intensive agriculture. People have moved out of villages, livestock has been drastically decreased and arable land has been abandoned. The decrease in cattle farming has caused a decline in hay meadows and pastureland. As a result, local grasslands have been reforestated. At the same time grassland area has slightly increased due to the growth of grassland vegetation on abandoned ields. These processes became even more drastic during the 1990s economic crisis. Large cattle farms almost disappeared, while small private farms became increasingly unproitable due to cheap dairy and meat products, imported from other regions. Nowadays extensive meadow landscapes can be found in the vicinity of the Tolvuya village (over 1000 hectares in total), in the Kizhi archipelago (ca. 1000 ha) and near the Kuzaranda village (ca. 800 hectares). Large grassland areas (over 100 ha) are located also close to settlements, including Lambasruchey, Velikaya Guba, Putka and Padmozero. Reports of the Finnish Environment Institute 40 | 2014 147 History of the study of the Zaonezhye’ grasslands The grasslands of Zaonezhye are probably the best studied in the Republic of Karelia. In the middle of the 20th century, Marianna Ramenskaya conducted reseach in the former Zaonezhye municipality. Discoveries made by her group are included in the monograph ‘Meadow vegetation of Karelia’ (Ramenskaya, 1958). This publication is still considered the basic work on Karelian grasslands. Biogeographically, the grasslands of Zaonezhye are a part of the Zaonezhye subprovince of the Southeastern grassland province. The subprovince also includes western parts of Medvezhegorsk and eastern parts of Kondopoga municipalities. On the whole, Zaonezhye is one of the most favorable areas for agriculture and also meadow vegetation in Karelia. First, the geological diversity of the region, especially its carbon-rich shungite mineraloids, provides dark and fertile soils. These soils maintain a better thermal regime during the long, light subpolar summer months. Secondly, the warm and humid climate of Zaonezhye is favourable for agriculture. The mean annual temperature is even higher here than in northern Ladoga. As a consequence, Zaonezhye has become one of the most important agricultural centres in the Russian North. As a result of traditional agricultural practises, grassland vegetation is well developed in Zaonezhye. In her monograph, Marianne Ramenskaya describes the rich vegetation of uncultivated areas in Zaonezhye as follows: “There is indeed a rich vegetation on the dark-coloured, gravel-rich uncultivated soils of Zaonezhye. Uncultivated land is exceptionally abundant, as stony soils are being abandoned due to dificulties in their mechanical treatment.” (p. 55). Unfortunately, the chapter on uncultivated land does not include information about its vegetation structure. Ramenskaya described in general terms six groups of grassland vegetation from dry to mesic meadows, three of which were found in Zaonezhye. In the 1980s and 1990s, Valentina Yudina studied meadows in Zaonezhye and later published the results on meadow vegetation on the islands of Kizhi and Volkostrov (Yudina 1999) as well as on mainland Kizhi (Yudina 2000). Yudina divided seven or eight associations of mesic grassland vegetation using the dominant approach. Syntaxa were named after their dominant vegetation type, e.g. “herb-rich” or “leguminous herb-rich”. During the late 1990s and early 2000s, Sergey Znamenskiy carried out ield studies on the Kizhi archipelago as well as in the vicinity of Tolvuya and Kuzaranda. As a result of these studies, Znamenskiy described ive vegetation associations based on ecology and topography. Different vegetation associations have different soil features, including soil nitrogen level and grain size. Each association is characterized by an ecologically uniform group of indicator species occurring in certain environmental conditions. In 2012 Znamenskiy also studied meadows of the western selkä area of Zaonezhye. Consequently, the classiication of grasslands in southern boreal Karealia now consists of four associations of dry and mesic meadows. Nitroilous tall-weed assosiations of Antriscetum sylvestris (Fig. 1) are one of the most widely distributed grassland associations in Zaonezhye. These associations occupy a large part of abandoned ields and hay meadows where the cessation of agriculture has resulted in the accumulation of dead litter, combined with the eutrophication of soils. A very low species density (on average 12-14 species/m2) and a large amount of nitrophilous species characterize these communities. Indicator species include Anthriscus sylvestris (L.) Hoffm., Artemisia vulgaris L., Heracleum sibiricum L., Dactylis glomerata L., Elymus repens (L.) Gould and Urtica dioica L., which are also dominant species in these communities. Depending on the history of the grassland vegetation, species from other ecological groups also occur as subdominant or satellite species. Also Siberian Hogweed (Heracleum sibiricum) is characteristic of 148 Reports of the Finnish Environment Institute 40 | 2014 the Antriscetum communities in Zaonezhye. However, Siberian Hogweed is mainly found in the eastern parts of the region, while Anthriscus sylvestris is more common in the western parts of Zaonezhye, as well as in southern boreal Karelia in general. As mentioned previously, the biodiversity of the Antriscetum communities is very low. However, their species pool can consist of up to 60-70 species of vascular plants. Therefore, Antriscetum communities can be turned into normal grassland with a few years of habitat management. Mesic meadows in Zaonezhye are divided into two associations that share a proportion of mesophytic plant species, including Achillea millefolium L. Campanula patula L., Galium album L., Hypericum maculatum Crantz., Lathyrus pratensis L., Phleum pratense L., Ranunculus acris L., Trifolium pratense L. Vicia cracca L and Veronica chamaedrys L. In the mesic meadows of Zaonezhye, Brown Knapweed (Centaurea jacea L.) is common, whereas Wig Knapweed (C. phrygia L.) is relatively rare, unlike in the rest of southern boreal Karelia. Also a third knapweed species, Greater Knapweed (C. scabiosa L.), occurs more frequently here than in neighbouring parts of Karelia. Tall grass association Magnograminetum (Fig. 2, 2a) occurs mainly on moderately humid clay soils on lacustrine plains and lat-topped eskers. This association is particularly common on the eastern plains of Zaonezhye. Indicator species include Carex ovalis Gooden., Cerastium fontanumBaumg., Festuca pratensis Huds., Leontodon autumnalis L. and Ranunculus repens L. Wood Cudweed (Gnaphalium sylvaticum L.) is practically absent here, unlike in the Magnograminetum grasslands of the Olonets and Pryazha municipalities. Nitrophilous species, characteristic of Antriscetum sylvestris associations (particularly Anthriscus sylvestris and Dactylis glomerata), can form a large part of the community. Sometimes these species can even become subdominant. One ecological variation of the Magnograminetum association is the tall grass vegetation of lacustrine clay deposits, with codominant Tussock grass (Deschampsia caespitosa (L.) Beauv.). In this variation, characteristic species are generally the same but the species density is lower than in the Magnograminetum association (13-14 in comparison with 19-20 species/m2). Another association of mesic meadows in Zaonezhie is more rare but much more biologically diverse: Forb-rich association Varioherbetum (Fig. 3) occurs on sandy soils on luvioglacial deposits and moraines. These associations grow on stony soils on steep slopes where mechanical soil treatment is dificult. Therefore, these sites have been soon abandoned and their vegetation has become rare. At present forb-rich meadows can only be found on small pastures near old villages. Nowadays there is almost no permanent population in smaller villages and, thus, no livestock. As a result, meadows are declining drastically as they turn into forests or nitrophilous tall-weed vegetation. Characteristic species for this association include Campanula glomerata L., Carum carvi L., Dianthus deltoides L., Festuca rubra L., Fragaria vesca L., Knautia arvensis (L.) Coult., Pimpinella saxifraga L., Plantago lanceolata L. and Plantago media L. Even though Rough Hawkbit (Leontodon hispidus L.) is a common indicator species of the Varioherbetum association in southern boreal Karelia, it is absent in Zaonezhye. However, Spotted Cat’s-ear (Hypochoeris maculata L.) is relatively common. There is also a wide range of satellite species in the association, including a number of meadow and forest plant species. This association is of crucial importance to grassland biodiversity in Zaonezhye. The species pool of Varioherbetum communities can include up to 7080 species of vascular plants. (There are 100-130 species within a single community in some Varioherbetum sites of southern Karelia.) The avarage species density is ca. 18-22 species/m2. A relatively rare association Deschampsietum lexuosae, or rocky meadows (Fig. 4), represents dry grasslands. These associations occur on shallow soils that cover neutral or slightly acidic bedrock outcrops. These meadows have a relatively high Reports of the Finnish Environment Institute 40 | 2014 149 species diversity (17-20 species/m2 and 70-80 vascular plants in the species pool). In addition to Wavy Hair-grass (Deschampsia lexuosa (L. Trin.), characteristic species include plants of rocky vegetation and boreal forests, such as Antennaria dioica (L.) Gaertn., Festuca ovina L., Luzula multilora L.., Rumex acetosella L., Vaccinium vitis-idaea L., Vaccinium myrtillus L. and Veronica oficinalis L. Another important species is Matgrass (Nardus stricta L.), which used to be a common species in Karelia half a century ago but is now becoming increasingly rare. Currently it occurs as a subdominant species in Deschampsietum lexuosae meadows only. Rare species such as orchids can grow on more or less basic rocks (e.g. dolomites). Future of grasslands in Zaonezhye The grasslands of Zaonezhye are declining rapidly. Between 1946 and 2000 grassland area in Karelia decreased 3-4 times (Znamenskiy 2000) and it continues to decrease now. Moreover, grasslands are becoming less diverse. Unmanaged meadows are turning into species-poor tall-weed communities that nowadays occupy more than 80% of the grassland area. One of the most endangered meadow associations is the forb-rich association, which is the main source of loristic diversity in Zaonezhye. Also rocky meadows also important, although these meadows are less endangered due to periodic droughts. The droughts regulate the regrowth of trees, which makes grassland vegetation more sustainable. However, even these communities need cattle grazing and mowing, which have nearly ceased as local villages have been converted into summer cottage communities. Nowadays traditional agriculture has concentrated on the outskirts of large villages, such as Velikaya Guba, Tolvuya or Kuzaranda, while the rest of the area is characterized by irregular land use. Unfortunately the future of grasslands in Zaonezhye does not look good. Even the development of protected areas does not help grasslands since meadow protection requires regular traditional agricultural activities. At present, agricultural activities are not allowed in the management plans of protected areas and even if they were, it would be dificult to arrange grazing and mowing there in practice. At the moment, the only opportunities for meadow protection exist on Kizhi Island where mowing is carried out regularly within the territory of the Kizhi open-air museum. However, local population should be encouraged to practice part-time small-scale farming part. In addition, regulations on small pastures and hay meadows within protected areas should be simpliied in order to protect at least some of the grassland biodiversity in Zaonezhye. Restoration of forest and tall-weed communities into meadows has not been studied enough and could be problematic. REFERENCES RКЦОЧsФКвК, M.L. 1958. ДMОКНШа ЯОРОЭКЭТШЧ ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ. 400 Щ. (IЧ RЮssТКЧ). ВЮНТЧК, V.F. 1999. . . ДMОКНШа ЯОРОЭКЭТШЧ ШП KТгСТ КЧН VШХФШsЭrШЯ ТsХКЧНsЖ. − IЧ: PrШМООНТЧРs ШП KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. BТШРОШРrКЩСв ШП KКrОХТК 1: 75–79. (ТЧ RЮssТКЧ). ВЮНТЧК, V.F. 2000. . . ДMОКНШаsЖ. – IЧ: GrШЦЭsОЯ, A.N. & KrЮЭШЯ, V.I. (ОНs.), BТШНТЯОrsТЭв ТЧЯОЧЭШrТОs КЧН sЭЮНТОs ТЧ ГКШЧОsСвО PОЧТЧsЮХК КЧН NШrЭСОrЧ sСШrО ШП LКНШРК LКФО. PОЭrШгКЯШНsФ. Щ. 84–93 (ТЧ Russian). ГЧКЦОЧsФТв, S.R. 1999. . . ДTСО ЦШНОrЧ sЭКЭЮs КЧН ЭСО КЭЭОЦЩЭ ЭШ ПШrОМКsЭ ЭСО НОЯОХШЩЦОЧЭ ШП ЦОКНШа МШЦЦЮЧТЭТОs ШП KТгСТ ТsХКЧНЖ. − IЧ: PrШМООНТЧРs ШП KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. BТШРОШРrКЩСв ШП KКrОХТК 1: 66–74. (IЧ RЮssТКЧ). ГЧКЦОЧsФТв, S.R. 2000. . . TrКНТЭТШЧКХ rЮrКХ ЛТШЭШЩОs ТЧ KКrОХТК. ДTrКНТЭТШЧКХ rЮrКХ ЛТШЭШЩОs ТЧ ЭСО NШrНТМ МШЮЧЭrТОs, ЭСО BКХЭТМ sЭКЭОs КЧН ЭСО RОЩЮЛХТМ ШП KКrОХТКЖ. − TОЦКNШrН 609: 49–55. 150 Reports of the Finnish Environment Institute 40 | 2014 ГЧКЦОЧsФТв, S.R. 2005. . . ( ) ДDrв КЧН ЦОsТМ ЦОКНШа ЯОРОЭКЭТШЧ ШП ГКШЧОгСвО (KКrОХТК)Ж − IЧ: PrШМООНТЧРs ШП KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. KКrОХТК 8: 168–177. (IЧ RЮssТКЧ). ГЧКЦОЧsФТв, S.R. 2013. . . ДMОКНШаsЖ. − IЧ: GrШЦЭsОЯ A.N. (ОН.) SОХФК ХКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ МСКrКМЭОrТsЭТМs, LКЧН UsО, CШЧsОrЯКЭТШЧ. PОЭrШгКЯШНsФ Щ. 75–81. (IЧ RЮssТКЧ). Fig. 1. Nitroilous tall-weed associations of Anthriscetum sylvestris (Photo Sergey Znamenskiy). Fig. 2. Tall grass association Magnograminetum (Photo Sergey Znamenskiy). Reports of the Finnish Environment Institute 40 | 2014 151 Fig. 3. Forb-rich association Varioherbetum (Photo Sergey Znamenskiy). Fig. 4. Deschampsietum lexuosae association, (rocky meadow) (Photo Sergey Znamenskiy). 152 Reports of the Finnish Environment Institute 40 | 2014 3 Flora and fauna in Zaonezhye Peninsula area 3.1 Vascular plant lora of Zaonezhye Peninsula Alexei V. Kravchenko*, Pertti Uotila**, Mikko Piirainen** and Alexander N. Sennikov** *Forest Research Institute of the Karelian Research Center of the Russian Academy of Sciences, Petrozavodsk, 11 Pushkinskaya St., RU-185910 Petrozavodsk, Karelia, Russia ** Botany Unit, Finnish Museum of Natural History, P.O.Box 7, FI-00014 University of Helsinki, Finland. Introduction Zaonezhye Peninsula is located in the Zaonezhye loristic district of Karelia (Ramenskaya 1960, 1983) as well as in the biogeographic province of Karelia onegensis (Kon), according to the biogeographic division of the Grand Duchy of Finland and adjacent Russia, developed by 19th century Finnish botanists and zoologists. Earlier the whole Karelia east of the Grand Duchy had been treated as a single region called Russian Karelia or Karelia rossica (Nylander & Saelan 1859). Karelia onegensis was delineated on the map for the irst time in the irst volume of Conspectus Florae Fennicae (Hjelt 1888) and the second edition of Herbarium Musei Fennici (Saelan et al. 1889). Since then its boundaries have been relatively stable compared to the boundaries of other provinces where there have been sometimes considerable changes (for Kola Peninsula, see Uotila 2013). The system of biogeographic provinces of East Fennoscandia has been regularly used in both publications and herbarium labels by northern European naturalists from the late 19th century up to the present day. Finnish botanist and phytogeographer Johan Petter Norrlin was a key person in developing the biogeographic division of East Fennoscandia. In 1870 he studied the vast territory of Zaonezhye (in its broad sense) up to Lake Segozero in the north, Petrozavodsk in the south and the border between the Olonets Province and the Grand Duchy of Finland in the west (i.e. practically the whole catchment area of River Suna). Norrlin provided a lot of information on the lora and vegetation of the territory. As a result, substantial differences between Zaonezhye and neighbouring territories Reports of the Finnish Environment Institute 40 | 2014 153 became evident (Norrlin 1871), which served as the background for recognizing the region as a separate biogeographic province. Fig. 1. The title page of Norrlin’s lora. On the basis of Norrlin’s inventories and subsequent studies by other Finnish botanists, Marianna L. Ramenskaya (1960, 1983) developed the loristic division of Karelia. The boundaries of her Zaonezhye loristic district coincide to a great extent with the boundaries of Karelia onegensis. Due to the natural border formed by Lake Onega, there is no difference between the eastern boundaries of the biogeographic province and the loristic district. Also the northern and southern boundaries are very similar. However, the western boundaries of Karelia onegensis and Zaonezhye loristic district differ substantially. Ramenskaya did not include the upper and middle parts of the Suna river basin in the Zaonezhye loristic district. These areas belong to the West Karelian Highlands that have a rather week relation to Zaonezhye (in both its broad and narrow sense). According to the division of Karelian nature, developed by 154 Reports of the Finnish Environment Institute 40 | 2014 Afanasiy I. Marchenko (1956), the western boundary of the Zaonezhye nature district is even further east, roughly along the 64° E longitude. History of loristic studies on the peninsula The nineteenth century Alexander K. Günther, who was a pharmacist at the Aleksandrovsk iron factory and later became the chief state forester of Olonets Province, carried out the irst studies in Zaonezhye Peninsula in 1863. There is a large amount of data collected, relating to the northernmost part of Zaonezhye as well as Kizhi and Klimentskiy islands. Günther (1867, 1880) published his observations of the lora of Obonezhie (i.e. the area around Lake Onega, including Zaonezhye in its broad sense). The few herbarium specimens he collected are deposited partly in the herbarium of St. Petersburg University (LECB), partly in the Botanical Museum of the University of Helsinki (H). In the same year 1863, the area was studied by two Finnish botanists, lecturer August Kullhem and student Theodor Simming (Norrlin 1871). They collected a lot of herbarium specimens, including some very rare species that have not been discovered since. Unfortunately, Kullhem and Simming did not publish their results. Their collections are located in H. J. P. Norrlin studied Zaonezhye for the whole summer of 1870. He made a few journeys together with Günther who called him «…my dear fellow researcher of the area» (Günther 1880: 11). Norrlin’s results, together with the data collected by Günther, Kullhem and Simming, were presented in general terms in the classic monograph of the lora of Karelia Onegensis (Norrlin 1871); the general part of the lora was also his doctoral thesis in botany. It included an annotated list of species of vascular plants and it was the irst detailed lora of any region in Karelia. The lora was divided into three areas – western, central and eastern – that were usually indicated in the list of taxa. The eastern area corresponds with Zaonezhye. For rare and phytogeographically or otherwise interesting species also localities were listed and features in variation, ecology and phytogeography were given. However, Norrlin only visited the surroundings of Velikaya Guba, Tolvuya and Shunga villages on the peninsula. Despite of its limitations, his work remains the main source on the lora of Zaonezhye for more than hundred years. Norrlin collected a large amount of herbarium specimens, which are deposited in H. At the end of the 19th century, also other Finnish scientists visited the area. In 1888 Norrlin’s student Alfred Oswald Kihlman (later Kairamo), better known for his expeditions to the Kola Peninsula and his later work in plant ecology, studied the surroundings of Kyappyaselkya, Kuzaranda and Shunga villages during his travel across the peninsula to Petrozavodsk (Virtanen 2014). Kihlman got advice on his excursion from Günther. In 1896 Bertil R. Poppius, a Finnish entomologist, made an entomological excursion to Karelia onegensis (see Jakovlev et al. 2014) and collected dozens of herbarium specimens especially from Zaonezhye Peninsula. Kihlman and Poppius visited localities that had been studied before by Norrlin, and collected some very rare species. Their studies can be considered one of the irst examples of monitoring lora. Unfortunately, only very little was published (Kihlman 1888, 1890). However, important indings by Kihlman and Poppius as well as previous researchers were published in Hjelt’s Conspectus (Hjelt 1888–1926). The specimens collected by Kihlman and Poppius are in H. In 1898 Aimo Kaarlo Cajander (another student of Norrlin, who later became professor of silviculture and three times Prime Minister of Finland) and Johan Ivar Lindroth (later Liro; who became professor of plant pathology in Helsinki) visited the southeastern corner of the territory, namely Kizhi, Klimenetskiy (village of Sennaya Guba), Uima and Yuzhnyi Oleniy Islands. They collected large number of specimens, Reports of the Finnish Environment Institute 40 | 2014 155 which are deposited in H. In addition to a brief report on their travel (Cajander & Lindroth 1900), there is a manuscript with a list of sites where observations and collections were made in the Archives of Botanical Museum, Helsinki (Kravchenko et al. 2005; Ahti & Boychuk 2006). The following century At the beginning of the 20th century, Saint Petersburg Society of Naturalists initiated a loristic study of Obonezhie. Petrozavodsk was the starting point of the long expedition of Eduard K. Bezays and A. Verdi in 1907 that ended in Povenets. They visited several places in the eastern shores of Zaonezhye Peninsula and the western shores of Unitsa Bay. The results of the excursion were soon published (Bezays 1911); in addition to the lora of each place studied, even environmental conditions such as landscape, relief, soils and features of land use were described in detail. Unfortunately, some published records are unreliable due to erroneous identiications. The rich collections are kept in Komarov Botanical Institute in St. Petersburg (LE). In 1927 Valentina A. Koroleva studied weeds in South Karelia and visited ca. 30 villages in Zaonezhye Peninsula. In the paper appeared very soon (Koroleva 1927–1928) she listed the main weeds of different crops as well as provided an annotated list of weeds of the entire region, where places in Zaonezhye were mentioned for some rather rare species. Specimens are stored in Herbarium of the N.I.Vavilov Institute of Plant Industry, St. Peterburg (WIR). The next period of loristic studies in Zaonezhye was during the Second World War. In 1941, on the initiative of the Geographical Society of Finland, the Executive committee on research of natural resources of East Karelia (i.e. Republic of Karelia) was established. Besides other natural resources, the lora and vegetation of the region were subjects of the study (Kravchenko & Uotila 1995). The loristic studies focused mainly on settlements and their surroundings, especially along roads. Thus, in 1942 the Swedish botanist Benkt Sparre, who served as a volunteer in the Finnish army, studied the lora of Azhepnavolok village and its vicinities (Sparre 1945). He gave exact localities for the most interesting species and collected 160 specimens from the area. In the same year, Aarno Kalela (son of A. K. Cajander and later professor of botany in Helsinki) visited Unitsa village where he collected a small number of herbarium specimens. The specimens collected by Sparre are housed in the Swedish Museum of Natural History, Stockholm (S), with a few duplicates in H, and the specimens collected by Kalela are housed in H. In 1943 two Finnish botanists, Lars Fagerström (later curator at the Botanical Museum, Helsinki) and Hans Luther (later professor of botany in Helsinki), visited the villages of Shunga, Tolvuya, Velikaya Niva and Velikaya Guba (and areas between the villages, including minor settlements) as well as Bolshoy Klimenetskiy Island. Even though they studied the area for only ive days, Fagerström and Luther prepared a detailed article on their excursion (Fagerström & Luther 1946), in which the most interesting indings were reported with their exact localities. They also presented an overview of previous inventories of the area. Furthermore, Luther, an aquatic plant botanist, prepared a special publication on the rare Caulinia lexilis (as Najas lexilis; Luther 1945), which was found from Velikaja Guba. Their herbarium collections are in H. During the same summer, Viljo Kujala (later professor of forest biology at the Forest Research Institute, Helsinki) travelled in the area and stayed longer, especially in Velikaya Guba. He collected several specimens and wrote a manuscript of his observations on plants; these specimens and the manuscript are in H. The next stage of studies in the area refers to the work of M. L. Ramenskaya, who in her time was a key igure in Karelian botany. She prepared the irst manual on the 156 Reports of the Finnish Environment Institute 40 | 2014 lora of Karelia (Ramenskaya 1960; see also Ramenskaya 1983; Ramenskaya & Andreeva 1982) and she also published a monograph on the meadows in Karelia with an enormous amount of relevés (Ramenskaya 1958). In the period between 17th August and 3rd September 1952, together with her pupil Vera A. Zaykova, Ramenskaya studied the northern part of Zaonezhye; the localities include minor settlements around the villages of Kuzaranda (Al’imovo, Koshkino and Shirokie Polya), Tolvuya (Adrianovskaya, Belokhino (Belokhinskaya), Voronino (Voroninskaya), Zagor’e, Kar-navolok, Padmozero and Pikalevskaya), Shunga (Bor Pudantsev, Deriguzovo, Enina Gora, Zagorskoe, Karpin Navolok, Krestnaya Gora, Putkozero and Seleznevo), and also the village of Velikaya Niva. A large number of relevés were studied, and a lot of specimens were collected. According to her notebook (preserved in the archives of the Karelian Research Centre of the Russian Academy of Sciences), they collected 143 (!) specimens in one day (18th August) only. Even though Ramenskaya worked for the Karelian Research Centre, the collected material is now in the herbarium of the Petrozavodsk State University (PZV). In 1964 Ramenskaya’s specimens – altogether more than 20 000 of them (including many duplicates from LE) – were moved from the Karelian Research Centre – from an unequipped and wet room without heating – to the University. Thus, the collection has been rescued (Gnatyuk 1995; Zaykova et al. 1995). Nevertheless, some specimens have been lost (Zaykova et al. 1995). After Ramenskaya, there was a long break in loristic research in Zaonezhye. Only Eugenia A. Klyukina studied the aquatic lora of few lakes (Valgomozero, Vangozero, Vikshezero, Kosmozero, Padmozero and Putkozero) in 1961 (Klyukina 1965). However, some records are unreliable and the determinations cannot be veriied in lack of voucher specimens. In 1979, Nina I. Ronkonen visited the northeastern part of the territory. She collected information mainly about species that are very rare and potentially in need of protection; the obtained data were taken into account when preparing the irst Red Data Book of Karelia (Volkov & Lapshin 1985). Ronkonen’s collections are kept in the herbarium of the Karelian Research Centre in Petrozavodsk (PTZ). Recent decades Alexei V. Kravchenko studied a number of sites throughout Zaonezhye in 1983, 1988, 1989, 1993, 1998, 1999 (together with M. Kashtanov), 2002–2004, 2007, 2010, 2012 and 2013 (Kravchenko & Sazonov 1992, Kravchenko 1993, Kravchenko et al. 2000 a, Kravchenko & Timofeeva 2012; for the trips in 2004 and 2013 see below). A large number of specimens were collected and later deposited in PTZ. Fig. 2. Alexei Kravchenko on dry meadow near Kuzaranda village, July 2004 (Photo Tapio Lindholm). Reports of the Finnish Environment Institute 40 | 2014 157 Floristic research on the islands of the peninsula continued in the 1980s, mainly within the boundaries of the protected area of Kizhskiy Reserve. As a result, lists of vascular plants of Kizhi Island (Shtan’ko & Lantratova 1985, Kravchenko & Sazonov 1992) as well as the other islands of the area (Kuznetsov 1993, 1997) were published. The largest amount of information was collected from Kizhi Island as well as adjacent islands and the mainland shore by Oleg L. Kuznetsov and his student Elena S. Drosdova. Numerous specimens are kept in PTZ. At the time, also the most important nature protection areas, including botanical sites, were designated (Khokhlova & Semina 1988, Antipin et al. 1994, Kuznetsov & Khokhlova 1994, Khokhlova & Kuznetsov 1996, Kravchenko et al. 2000 a, b, Kuznetsov et. al. 2000). After more than a 30-year break, the study of meadows continued in 1985–1987 (Drozdova 1987). At that time, mires in the vicinities of Lambasruchey and Karasozero villages were studied (Dyachkova et. al. 1993, Antipin et. al. 1994). All the results were documented and some specimens were stored in PTZ. In 1997–2000, a postgraduate student Maksim V. Kashtanov studied the northern part of the peninsula as well as its islands (Kashtanov 1997, 1998 a, b, 1999 a, b). Kashtanov also studied Azhepnavolok village and obtained new data on the lora of the village, studied ca. 60 years earlier by Sparre (Kashtanov 1999 b). Furthermore, he compiled lists of species for 18 islands of the peninsula. Kashtanov collected a great number of specimens, which are kept mainly in PTZ, but also in PZV. Within the framework of several projects sponsored by the Finnish Ministry of the Environment, including an inventory of biological diversity of Zaonezhye Peninsula, further research in the area was carried out in 1998 and 1999. During this time, Oksana A. Butskikh, Alexander M. Kryshen’ and Vera V. Timofeeva visited the vicinities of Kosmozero village, Lakes Kalozero and Chelozero as well as the southern part of Svyatukha Bay of Lake Onega. Collected specimens are kept in PTZ. Within the framework of the last project in 1999, O. L. Kuznetsov and Natalia V. Stoykina studied mires and collected mire plants (Kuznetsov et al. 2000). In addition, Stanislav A. Kutenkov studied paludiied forests in 2002 and 2012 (Kutenkov 2006, 2013). The few collected specimens are kept in PTZ. From 1998 to 2004 Natalia V. Markovskaya studied the distribution and population age structure of orchid species on the islands (Dyachkova & Markovskaya 2003, Markovskaya & Dyachkova 2003, Markovskaya 2004, 2005, Markovskaya et al. 2007). A small number of samples were deposited in PZV. A Russian-Finnish expedition was arranged to the area in 3rd–6th July 2004. Participants from Russia included Elena P. Gnatyuk, A. V. Kravchenko, A. M. Kryshen’ and O. L. Kuznetsov; and from Finland Tapio Lindholm, Mikko Piirainen, Rauno Ruuhijärvi and Pertti Uotila. They visited several islands: Bolshoi Klimenetsky (Klimetsky Nos Cape and Lukovo Cape), Bolshoi Lelikovsky (Radkolye Cape), Megostrov, Paleostrov, Rechnoy, Shunevskiy and Yuzhnyi Oleniy islands, and also the mainland shores in the neighbourhood of Kuzaranda and Tipinitsy villages. A relatively large number of specimens were collected; specimens collected by the Russian participants were deposited in PTZ, and those by the Finnish participants in H. Since 1999 the study of meadows has continued, mainly on Kizhi Island but also on other islands (Yudina 1999, 2000; Znamenskiy 1999, 2000, 2005 a, b, 2010, 2013; Yudina & Stoykina 2005; Timofeeva 2013; Znamenskiy & Timofeeva 2013). As a result, relevés as well as extensive lists of meadow species have been provided. Collections (which are not rich) are in PTZ. In 2009 and 2010, teachers and students of the Petrozavodsk State University studied the shores of Kizhi Island and some other islands (Morozova et al. 2010, 2011); the collected material is kept in PZV. Vera V. Timofeeva studied the mainland opposite Kizhi Island in 2011 (Timofeeva & Nikolaeva 2012), and Unitsa Bay in 2013. In addition, she carried out inventories of 158 Reports of the Finnish Environment Institute 40 | 2014 plants in several lakes (Verkhnee Myagrozero, Gizhozero, Kovshozero, Kondozero, Lelikozero) in 2011–2013. Relatively abundant collections are stored in PTZ. In 2013, two Russian-Finnish expeditions were arranged as pilot projects in the framework of BPAN project leaded by Finnish Environment Institute. During these expeditions, surroundings of Kaskoselga, Lipovitsy, Oyatevstchina, Polya, Tambitsy, Tipinitsy, Vegaruksa, Velikaya Guba, Uzkaya Salma and Zubovo villages, and Lake Rugozero were visited. The participants of the expedition included botanists, zoologists and ecologists. A number of loristic observations were made mainly by A. V. Kravchenko and Kimmo Syrjänen, although botanical data were collected also by Timo Kuuluvainen, Olli Manninen, Jyri Mikkola, and Olli-Pekka Tikkanen. The collected specimens are deposited mainly in PTZ, but also in the herbarium of the University of Turku (TUR). During the last two decades rich loristic material, including ca. 2000 herbarium specimens and a great amount of loristic ield notes, has been collected from Zaonezhye. However, although many papers have been published, detailed data have been included in only a few of them, mainly dealing with red-listed species (Kravchenko et al. 2000 a) and the lora of the planned Zaonezhye Landscape Reserve (Kravchenko & Timofeeva 2013). Information from Zaonezhye was also taken into account in the preparation of the Red Data Book of Republic of Karelia (Ivanter & Kuznetsov 2007). Fig. 3. Pertti Uotila, Elena Gnatyuk and Margarita Boychuk on dry meadow near Kuzaranda village, July 2004 (Photo Tapio Lindholm). Reports of the Finnish Environment Institute 40 | 2014 159 Present knowledge Despite the long history of botanical studies in Zaonezhye, loristic knowledge of this fairly limited territory is still variable. There is relatively comprehensive data available from the southeastern islands, so called Kizhi Skerries (Kizhi Island and numerous surrounding islands as well as a narrow strip of the mainland), and from the northeastern part of Zaonezhye (Tolvuya – Shunga area), as well as from areas along the main roads. However, less data are available from the northwestern part of Zaonezhye. Nevertheless, it is assumed that indigenous species are relatively well known because very few indigenous species have been found since Norrlin’s studies. However, according to available data, many indigenous species are considered rare. But this is rather an artefact, and their distribution will be clariied in the future. In total, ca. 530 indigenous species have been discovered from Zaonezhye Peninsula (excluding microspecies of Ranunculus auricomus, R. cassubicus, R. fallax, Hieracium, Pilosella, and Taraxacum). In earlier studies (Norrlin 1871; Fagerström & Luther 1946), a relatively large number of species were considered unique for Zaonezhye (in its broad sense). However, at present only one of them, Polemonium boreale, is only known in Karelia from the area. Other extremely rare species include Caulinia lexilis, which is known in Karelia from only three localities, two of which are in Zaonezhye; and Helianthemum nummularium, which is known from two localities in Karelia, one of which is in Zaonezhye. Many other species are more frequent in Zaonezhye than in any other region of Karelia, namely Ulmus laevis, Myosoton aquaticum, Cotoneaster antoninae, C. melanocarpus, Chaerophyllum aromaticum, Cuscuta europaea, Pseudolysimachion spicatum, Lycopus europaeus, Eupatorium cannabinum, Potamogeton friesii, P. rutilus, Carex muricata. The majority of these species belong to thermophilous species. About 60 species in Zaonezhye have a mainly southern distribution. Many of them grow near the northern limits of their distribution areas. Some, like Carex muricata, Chaerophyllum aromaticum, Odontites vulgaris and Cuscuta europaea, occur here in their northernmost known localities in Russia; while others, like Dracocephalum ruyschiana and Pseudolysimachion spicatum, are in their northernmost localities in Fennoscandia. In Karelia, Zaonezhye provides the northernmost known localities for species, including Stellaria alsine, Ulmus laevis, Corydalis bulbosa, Myosoton aquaticum, Chaerophyllum aromaticum, Cuscuta europaea, Pseudolysimachion spicatum, Glyceria maxima and Scolochloa festucacea. Fig. 4. Rubus humulifolius (Photo Kimmo Syrjänen). 160 Reports of the Finnish Environment Institute 40 | 2014 Fig. 5. Eupatorium cannabinum (Photo Kimmo Syrjänen). There is a number of southern species that are not rare in Zaonezhye and often play a signiicant part in the composition of plant communities. These species include woody plants Tilia cordata, Ulmus glabra, Alnus glutinosa, Lonicera xylosteum, Daphne mezereum and Solanum dulcamara as well as several herbs, like Polygonatum odoratum, Iris pseudacorus, Campanula persicifolia, Viola mirabilis and Chaerophyllum aromaticum. There is also a small number of northern species, including Woodsia alpina, Cerastium alpinum, Saxifraga nivalis and Poa alpina, occupying outcrops of bedrock, sometimes together with southern species. In addition, Astragalus subpolaris and Oxytropis sordida have been found from dry pine forests. In Zaonezhye, all northern species are very rare, in contrast to northern Lake Ladoga where a small number of northern species are known from several, sometimes dozens of localities; see, e.g., Heikkilä et al. (1999). Some eastern («Siberian») species, e.g., Atragene sibirica, Lonicera pallasii, Aconitum septentrionale, Viola selkirkii, Rubus humulifolius, Ligularia sibirica and Saussurea alpina, can be found from Zaonezhye close to the western limit of their distribution areas. Without certain features of the region, the number of species with mainly eastern distribution could be higher. First, Lake Onega forms a natural barrier to the east. Secondly, if species have managed to jump over or get around the lake, they cannot move further west because of the rivers running east towards Lake Onega and the watershed blocking them in the west. River basins play an essential role in spreading many species. Good examples include Atragene sibirica and Rubus humulifolius that are common especially on the shores of water bodies east of Lake Onega. Reports of the Finnish Environment Institute 40 | 2014 161 Fig. 6. Carex rhynchophysa (Photo Kimmo Syrjänen). Fig. 7. Diplazium sibiricum (Photo Kimmo Syrjänen). Sandy beaches are sometimes inhabited by a few species typical for seashores, including Lathyrus aleuticus, Calamagrostis meinshausenii, Festuca arenaria and Leymus arenarius. Long-term land use has enriched the lora with alien species; their total number in Zaonezhye is ca. 220 (ca. 30% of the vascular lora). The composition of alien lora 162 Reports of the Finnish Environment Institute 40 | 2014 has changed during the course of the past decades. Some weeds, such as Apera spica-venti and Centaurea cyanus, that were common and abundant decades ago have totally disappeared. At the same time, many newcomers have appeared during recent decades, including aggressive invasive species such as Heracleum sosnowskyi and Impatiens glandulifera. In the future, many new species – mainly escapees of ornamental, edible and medicinal plants – are likely to be recorded in the area. Such species have been discovered during the past ive years from, for instance, the villages of Lambasruchey, Pod’elniki, Ruch’i, Shunga, Tolvuya and Velikaya Guba. The large numbers of threatened species and their localities, as well as the number of indicators of biologically valuable forests demonstrate the value of Zaonezhye Peninsula for the lora of Karelia. On the basis of several relatively common and widespread indicator species, all the forests on the peninsula could be considered biologically valuable. This means that practically the whole peninsula, which is more or less covered by forests, is biologically valuable. Table l. The richest plant families in Karelia onegensis, in Zaonezhye Peninsula, and in two protected areas inside the Zaonezhye Peninsula: Kizhi Federal Zoological Reserve (Kizhi Skerries), and the planned Zaonezhye Landscape Reserve. Note that the status indigenous/introduced (alien) was revised for the lora in Kravchenko (2007), thus the numbers of indigenous species given in Gnatyuk et al. (2003 b), which is not revised here, can in few families exceed those for the whole Zaonezhye Peninsula. Karelia onegensis * Zaonezhye Peninsula Kizhi Federal Zoological Reserve ** Planned Zaonezhye Landscape Reserve *** Acreage ca. 30 000 km2 ca. 3 000 km2 500 km2 1100 km2 Family Number of indigenous species / (%) Ordinal number Number of indigenous species / (%) Ordinal number Number of indigenous species / (%) Ordinal number Number of indigenous species / (%) Ordinal number Cyperaceae 69 (10.2) 1 56 (10.4) 1 45 (9.7) 1 42 (9.8) 1 Poaceae 60 (8.9) 2 42 (8.0) 2 35 (7.5) 2 37 (8.5) 2 Asteraceae **** 44 (6.5) 3 41 (7.6) 3 32 (6.9) 3 37 (8.5) 2 Rosaceae 35 (5.2) 4 24 (4.5) 6 28 (6.0) 4 18 (4.1) 5 Ranunculaceae 29 (4.3) 5 25 (4.6) 4 21 (4.5) 5 18 (4.1) 5 Scrophulariaceae 29 (4.3) 5 25 (4.6) 4 18 (3.9) 6 21 (5.0) 4 Caryophyllaceae 27 (4.0) 7 24 (4.5) 6 17 (3.6) 7 18 (4.1) 5 Orchidaceae 27 (4.0) 7 18 (3.3) 8 15 (3.2) 8 15 (3.5) 8 Polygonaceae 19 (2.8) 9 15 (2.8) 9 14 (3.0) 10 9 (2.1) . Brassicaceae 17 (2.5) 10 7 (1.3) . 9 (1.9) . 7 (1.6) . Lamiaceae 15 (2.2) . 13 (2.4) . 15 (3.2) 8 10 (2.3) . Juncaceae 14 (2.1) . 15 (2.8) 9 8 (1.7) . 11 (2.5) 9 Salicaceae 16 (2.4) . 11 (2.0) . 10 (2.1) . 11 (2.5) 9 Total number in the ten richest families / (%) 356 (52.8) 287 (53.2) 240 (51.6) 228 (52.5) 674 539 465 434 Province / Area Total number of indigenous species * Gnatyuk et al. (2003 a); ** Gnatyuk et al. (2003 b); *** Kravchenko & Timofeeva (2013). **** As to Hieracium and Pilosella, all microspecies of each section have been counted as one (collective) species, 4 in Hieracium and 4 in Pilosella. Reports of the Finnish Environment Institute 40 | 2014 163 List of vascular plant species of Zaonezhye, with annotations for threatened and indicator species Explanations The nomenclature mainly follows Kravchenko (2007), and some important synonyms have been given in parentheses. The red-listed and indicator species as well as aliens have been marked with symbols in front of the species name. * red-listed species. ** indicator of biologically valuable forests for Northwest Russia (Andersson et al. 2009). a alien. Each species is provided by an estimation of frequency (printed in bold italics) in Zaonezhye according to the following scale: rr (very rare), r (rare), str (fairly rare), p (here and there), stfq (fairly frequent), fq (frequent and very frequent). For red-listed and indicator species, as well as for some other interesting species, the documentation is given by listing localities with herbarium specimens and related publications. A herbarium specimen is indicated by the year of collecting and collector’s surname (in italics). For the herbaria in which the specimens are kept, see the paragraph History of loristic studies. In a few cases the relevant herbarium is mentioned in the list. Frequencies and localities given by Norrlin (1871) are given within parentheses. An asterisk means that the frequency is given by Norrlin for the whole Karelia onegensis (including Zaonezhye Peninsula), not separately for Zaonezhye Peninsula and Kizhi = Svyatnavolok. The threat categories according to 3 different sources are given at the end of the relevant species descriptions: RDB RF = Red Data Book of Russian Federation (Trutnev et al. 2008), the respective IUCN categories given in parenthesis: 1– ДЮЧНОr ЭСО rТsФ ШП ОбЭТЧМЭТШЧЖ (= МrТЭТМКХХв endangered) 2– ДЧЮЦЛОr ШП ТЧНТЯТНЮКХs Тs НОМХТЧТЧРЖ (= ОЧНКЧРОrОН) 3– ДrКrОЖ (ЭСТs МКЭОРШrв МШЯОrs ЩКrЭ ШП IUCN ЯЮХЧОrКЛХО + ЧОКr ЭСrОКЭОЧОН) RDB RK = RОН DКЭК BШШФ ШП RОЩЮЛХТМ ШП KКrОХТК (IЯКЧЭОr & KЮгЧОЭsШЯ 2007), ЭСО rОsЩОМЭТЯО IUCN МКЭОРШrТОs РТЯОЧ ТЧ ЩКrОЧЭСОsТs: 1– ДЮЧНОr ЭСО rТsФ ШП ОбЭТЧМЭТШЧЖ – 1 (CR, critically endangered), 2– ДЧЮЦЛОr ШП ТЧНТЯТНЮКХs Тs НОМХТЧТЧРЖ – 2 (EN, endangered) 3– ДrКrОЖ – 3 (VU) + 3 (NT) + 3 (LC) (= ЯЮХЧОrКЛХО + ЧОКr ЭСrОКЭОЧОН + ХОКsЭ concern) 4– ДМКЭОРШrв ЮЧФЧШаЧЖ – 4 (DD, НКЭК НОiМТОЧЭ) Note that for the categories given in Red Data Book of Karelia, the erroneous category 3 (LC) Тs МШrrОМЭОН ЭШ 3 (NT). 164 Reports of the Finnish Environment Institute 40 | 2014 RDB EF = RОН DКЭК BШШФ ШП EКsЭ FОЧЧШsМКЧНТК (KШЭТrКЧЭК ОЭ КХ. 1998): 1 – Endangered, 2 – Vulnerable 3 – Rare 4 – Declining ? – Data Deicient Note. Special attention as source of information must be paid to the maps in Hultén (1971). These are handmade maps, for Karelia mainly completed in Helsinki, where information about specimens, literature and archives were added by pencil to the maps of the irst edition of Hultén (1950). At the time, there was no demand for detailed documentation of each dot and the work was done in a short time, using not very detailed maps. As a result, there may be inaccuracies in the locations of the dots, and the maps should be understood more as indicators of general distributions than exact locations of single indings. On the other hand, V. Kujala, one of the persons who commented on the maps and added information especially about Karelia, may have added dots from primary data unknown from other sources, due to his extensive travels in Karelia onegensis during the war. Dubious and erroneously recorded species are given at the end of the list. Huperzia selago (L.) BОrЧС. Об SМСrКЧФ & MКrЭ. – Str. (Norrlin 1871: *Stfq.) Diphasiastrum complanatum (L.) HШХЮЛ – Str. (Norrlin 1871: *Fq.) Lycopodium annotinum L. – Fq. (Norrlin 1871: *Fq.) Lycopodium clavatum L. – Stfq. (Norrlin 1871: *Stfq.) Selaginella selaginoides (L.) P. BОКЮЯ. Об SМСrКЧФ & MКrЭ. – Str. (Norrlin 1871: Fq ТЧ NА ЩКrЭ.) *Isoёtes echinospora DЮrТОЮ – P, ЛЮЭ fq in Kizhi Skerries: more than 30 registered localities. (NШrrХТЧ 1871: SСЮЧРК, V. GЮЛК, ОЭМ.) – RDB RF: 2, RDB RK: 3 (LC) *Isoёtes lacustris L. – P: more than 30 registered localities. (Norrlin 1871: Stfq.) – RDB RF: 3, RDB RK: 3 (LC) Equisetum arvense L. – Fq. (Norrlin 1871: *Fq.) EquТsetum luvТatТle L. – Fq. (Norrlin 1871: *Fqq.) Equisetum hyemale L. – Str. (Norrlin 1871: Str: Shunga, etc.) Equisetum palustre L. – Fq. (Norrlin 1871: *Fq–fqq.) Equisetum pratense EСrС. – Fq. (Norrlin 1871: *Stfq–fq.) Equisetum scirpoides MТМСб. – Rr, rОМОЧЭ rОМШrНs: RОМСЧШв IsХ. (2004 Kravchenko). (Norrlin 1871: Azhepnavolok, fq in Padmozero.) Equisetum sylvaticum L. – Fq. (Norrlin 1871: *Fq–fqq.) Equisetum variegatum SМСХОТМС. Об F. АОЛОr & D. MШСr – Rr. Ashepnavolok (1870 Norrlin, 1896 Poppius); TКЦЛТЭsв – KКsФШsОХРК (2013 Syrjänen). *Botrychium boreale MТХНО – Rr: Azhepnavolok (1996 Kashtanov; KrКЯМСОЧФШ ОЭ. КХ. 2000 К). – RDB EF: 3, RDB RK: 3 (LC) *Botrychium lanceolatum (S. G. GЦОХ.) йЧРsЭr. – Rr: KЮгКrКЧНК (HЮХЭцЧ 1971); B. KХТЦ., Motalovo (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ. КХ. 2000 К). – RDB EF: 4, RDB RK: 3 (NT) Botrychium lunaria (L.) Sа. – Str. (Norrlin 1871: P–stfq.) BotrycСТum multТidum (S. G. GЦОХ.) RЮЩr. – R: ЛОЭаООЧ PrШsОЯsФКвК КЧН BШХ ГКrОЯШ ЯТХХКРОs (FКРОrsЭröЦ & LЮЭСОr 1946); AгСОЩЧКЯШХШФ (SЩКrrО 1945); MОНЯОНОЯШ (1979 Ronkonen); VОrФСЧОО MвКРrШгОrШ (2012 Bogdanova PTГ; 2012 TТЦШПООЯК). – RDB EF: 3 Ophioglossum vulgatum L. – R: Okatovstchina (1952 Ramenskaya & Zaykova); ЛОЭаООЧ VШrШЧТЧsФШО КЧН TШХЯЮвsФТв BШr ЯТХХКРОs (1952 RКЦОЧsФКвК, ШЛs.); TШХЯЮвК (HЮХЭцЧ 1971); Reports of the Finnish Environment Institute 40 | 2014 165 KТгСТ КrОК (HЮХЭцЧ 1971); LТМСФШЯ IsХ. (1998 Kashtanov; KrКЯМСОЧФШ ОЭ. КХ. 2000 К); BШХ. KХТЦ, KШsОХ′РК (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ. КХ. 2000 К); V. GЮЛК (2010 Kravchenko). – RDB EF: 3 Pteridium latiusculum (DОsЯ.) HТОrШЧ. Об Fr. (Pteridium pinetorum C. N. Page & R. R. Mill, P. aquilinum L., s. ХКЭ.) – Stfq. (Norrlin 1871: Fq.) Thelypteris palustris Schott – R. Phegopteris connectilis (MТМСб.) АКЭЭ – Fq. (Norrlin 1871: Fq.) Dryopteris carthusiana (VТХХ.) H. P. FЮМСs – Fq. (Norrlin 1871: Fqq; ТЧМХ. D. expansa) Dryopteris cristata (L.) A. GrКв – R: ca. 10 current records. ** Dryopteris expansa (C. PrОsХ) FrКsОr-JОЧФ. & JОrЦв – Str–stfq. DryopterТs ilТx-mas (L.) SМСШЭЭ – Fq. (Norrlin 1871: Fq.) AtСyrТum ilТx-femТna (L.) RШЭС. – Fq. (Norrlin 1871: Fq.) Cystopteris fragilis (L.) BОrЧС. – Stfq. (Norrlin 1871: Stfq.) **Diplazium sibiricum (TЮrМг. Об G. KЮЧгО) SК. KЮrКЭК – Rr: rОМОЧЭ rОМШrНs B. LОХТФ. IsХ. (2004 Kravchenko); RОМСЧШв IsХ. (2004 Kravchenko, Piirainen); PКХОШsЭШЯ IsХ. (2004 Uotila); Lipovitsy (2013 Syrjänen). (Norrlin 1871: Dianova Gora.) Gymnocarpium dryopteris (L.) NОаЦКЧ – Fq. (Norrlin 1871: *Fqq.) *Woodsia alpina (BШХЭШЧ) GrКв – Rr: Gizhozero (2012 Timofeeva; KrКЯМСОЧФШ & TТЦШПООЯК 2013). – RDB EF: 3, RDB RK: 3 (VU) Woodsia ilvensis (L.) R. Br. – Stfq. (Norrlin 1871: Suoyarvi, Shunga.) **Matteuccia struthiopteris (L.) TШНКrШ – Str. (Norrlin 1871: R.) *,**Asplenium septentrionale (L.) HШППЦ. – Str: МК. 16 ХШМКХТЭТОs TШХЯЮвК – KХТЦ NШs КЧН ЛОЭаООЧ BЮЭОЧОЯШ КЧН ГКsОХОгСвО ЯТХХКРОs (FКРОrsЭröЦ & LЮЭСОr 1946); TОХ′ЩШгОrШ (1952 Ramenskaya & Zaykova PTГ, PГV); SЩТrШЯФК (1979 Ronkonen, 2012 Timofeeva); FШЦТЧШ (1988 KrКЯМСОЧФШ, ШЛs.); LКФО KШгЦШгОrШ, SТХ’ЧвТ IsХ. (1999 Butskih, Kryshen & Timofeeva); KШsЦШгОrШ (1999 Butskih, Kryshen & Timofeeva); PКХОШsЭrШЯ (1999 Kravchenko & Kashtanov, 2004 Uotila); B. KХТЦ., PОrЯвО GКrЧТЭsв & VЭШrвО GКrЧТЭsв (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К), LЮФШЯвТ CКЩО (2004 Kravchenko, Uotila); RОМСЧШв IsХ (2004 Lindholm PTГ); B. LОХТФ. (2004 Kravchenko); VКЧМСШгОrШ (2006 Talbonen PTГ, 2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013); VОФСФШгОrШ (2012 Kravchenko); UЧТЭsФКвК BКв, SОЯОrЧвТ SШФШХТв IsХ. (2013 Timofeeva). (NШrrХТЧ 1871: VОРШrЮФsК.) – RDB EF: 4, RDB RK: 3 (LC→NT) **Asplenium trichomanes L. – R: МК. 9 ХШМКХТЭТОs AгСОЩЧКЯШХШФ (SЩКrrО 1945); SЯвКЭЮФСК BКв, Zimnaya Mt. (1989 Kravchenko); KШsЦШгОrШ (1999 Timofeeva, Rudkovskaya & Kryshen); V. NТЯК (1999 Timofeeva & Rudkovskaya PTГ); B. LОХТФ. (2004 Kravchenko, Uotila); LКФО Ladmozero (2012 Kravchenko, 2012 Rudkovskaya PTГ); VОФСФШгОrШ (2012 Kravchenko); UЧТЭsФКвК BКв, ЦКТЧХКЧН КЭ SШФШХТв IsХ. (2013 Timofeeva). (Norrlin 1871: Shunga.) Polypodium vulgare L. – Fq. (Norrlin 1871: Stfq–fq.) Picea abies (L.) KКrsЭ. – R. (Norrlin 1871: *Fqq; ТЧМХ. P. × fennica.) P. × fennica (Regel) Kom. (P. abies × obovata) – Fq: the most common taxon of Picea in Zaonezhye and the entire Karelia. P. obovata LОНОЛ. (P. abies sЮЛsЩ. obovata (LОНОЛ.) DШЦТЧ) – Str. (NШrrХТЧ 1871: V. GЮЛК.) Pinus sylvestris L. – Fq. (Norrlin 1871: *Fqq.) Juniperus communis L. – Fq. (Norrlin 1871: *Fqq.) Nuphar lutea (L.) SТЛЭС. & SЦ. – Fq. (Norrlin 1871: Fq.) Nuphar pumila (TТЦЦ) DC. – Str. Nuphar × spenneriana Gaudin (N. lutea × pumila (TТЦЦ) DC.) – R. (NШrrХТЧ 1871: V. GЮЛК.) Nymphaea × borealis Camus (N. alba × candida) – R. Nymphaea candida J. PrОsХ & C. PrОsХ – Fq. (Norrlin 1871: Fq ТЧ V. GЮЛК, Кs N. alba L. s. lat.) Ceratophyllum demersum L. – Rr: Putkozero (Shunga) (1952 Ramenskaya & Zaykova; 2012 Kravchenko); PКНЦШгОrШ (KХвЮФТЧК 1965). (NШrrХТЧ 1871: SСЮЧРК.) a Aconitum × cammarum auct. (A. × stoerkianum KШОХХО) – Rr: V. GЮЛК (2010 Kravchenko); TШХЯЮвК (2011 Timofeeva). 166 Reports of the Finnish Environment Institute 40 | 2014 **Aconitum septentrionale Koelle (A. lycoctonum L. sЮЛsЩ. septentrionale (KШОХХО) KШrsС.)– Fq. (Norrlin 1871: Fq.) **Actaea erythrocarpa (FТsМС.) KШЦ. – Str: Azhepnavolok (1996 Kashtanov); BЮФШХЧТФШЯsФТв IsХ. (1999 Kashtanov); KШХРШsЭrШЯ (1986 Kuznetsov); LКФО CСОХШгОrШ (1999 Rudkovskaya & Timofeeva); MОРШsЭrШЯ IsХ. (2004 Kravchenko); PКХОШsЭrШЯ IsХ. (1999 Kravchenko & Kashtanov); RОМСЧШв IsХ. (2004 Kravchenko); VШХФШsЭrШЯ (1996 Kuznetsov). IЧ МШЦЦЮЧТЭТОs domiЧКЭОН Лв Pinus sylvestris, Picea abies, Alnus incana and A. glutinosa, ЛШЭС ТЧ ШХН-РrШаЭС КЧН ЦТННХО КРОН ПШrОsЭs (ТЧ ЭаШ ХШМКХТЭТОs ЭСО ЦОКsЮrОН КРО ШП ЭrООs аКs МК. 60 вОКrs). Actaea spicata L. – Stfq. (Norrlin 1871: Stfq.) Anemonoides nemorosa (L.) HШХЮЛ (Anemone nemorosa L.) – Str: mainly in Kizhi Skerries КЧН ТЧ ЮЩ ЭШ 5–10 Ц аТНО ЧКrrШа sЭrТЩО КХШЧР ЭСО sСШrОs ШП LКФО OЧОРК. (Norrlin 1871: B. Klim. (Simming, Günther).) a Aquilegia vulgaris L. – Rr: V. GЮЛК (2012 KrКЯМСОЧФШ, ШЛs.). **Atragene sibirica L. (Clematis alpina (L.) MТХХ. sЮЛsЩ. sibirica (MТХХ.) KЮЧЭгО) – R: Kuzaranda (no date Günther H; 1896 Poppius); FШЦТЧШ (1988 Kravchenko; KrКЯМСОЧФШ ОЭ КХ. 2000 К); SЩТrШЯШ (2001 Shelekhov PTГ); RОРТЦКЭФК (2012 Kravchenko); TКЦЛТЭsв – KКsФШsОХga (2013 Syrjänen). CШХХОМЭОН ПrШЦ sОМШЧНКrв ПШrОsЭs НШЦТЧКЭОН Лв МШЧТПОrs Шr КsЩОЧ. TСО sЩОМТОs Тs ПКТrХв МШЦЦШЧ ОКsЭ ШП LКФО OЧОРК, Кs аОХХ Кs ШЧ ТsХКЧНs ЛОЭаООЧ ГКШЧОгСвО КЧН E sСШrО ШП LКФО OЧОРК аСТМС КrО ПШrЦОН ШП ЦШrКТЧО Шr sКЧН НОЩШsТЭs (КХЦШsЭ КХХ ШП ЭСОsО ТsХКЧНs ХТО ШЮЭsТНО ЭСО ГКШЧОгСвО КrО НОХТЦТЭОН СОrО). IЧ KКrОХТК ТЭ Тs ЯОrв rКrО КХsШ ШЧ ЭСО А sСШrОs ШП LКФО OЧОРК, ЛЮЭ ТЧ NNА ЭСО КrОК ОбЭОЧНs ЮЩ ЭШ LКФО SОРШгОrШ (HЮХЭцЧ 1971). – RDB EF: 3 *Batrachium confervoides Fr. (B. eradicatum (LКОsЭ. Об NвЦКЧ) Fr., Ranunculus confervoides (Fr.) Fr., R. eradicatus (LКОsЭ. Об NвЦКЧ) F. JШСКЧsОЧ) – R: PЮЭФШгОrШ (KХвЮФТЧК 1965); Shiltya (1999 Butskikh, Kryshen & Timofeeva; KrКЯМСОЧФШ ОЭ КХ. 2000 К); RШРШsЭrШЯ IsХ. (1999 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); KКгСЦК (2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013). RКrО ЭСrШЮРСШЮЭ KКrОХТК, ЦШrО МШЦЦШЧ ТЧ ЭСО ЧШrЭС-аОsЭОrЧЦШsЭ ЩКrЭ (О.Р. ТЧ ЭСО PККЧКУтrЯТ КrОК). – RDB RK: 3 (LC→NT) Batrachium dichotomum (SМСЦКХС.) TrКЮЭЯ. (Ranunculus peltatus Schranck, s. lat.) – Stfq, especially in Kizhi Skerries. (Norrlin 1871: *Fq.) Caltha palustris L. – Fq. (Norrlin 1871: *Fqq.) a Consolida regalis GrКв – Rr: TШХЯЮвК (GüЧЭСОr 1880; KШrШХОЯК 1927–1928; FКРОrsЭröЦ & LЮЭСОr 1946; 1952 Ramenskaya & Zaykova PTГ, PГV; 1993 Antikainen PTГ); PКНЦШгОrШ (BОгКТs 1911; 1979 Ronkonen.) a Delphinium × cultorum VШss. – R: B. KХТЦ., SОЧЧКвК GЮЛК (1998 Kashtanov; KrКЯМСОЧФШ 2007). *Delphinium elatum L. – Rr: Unitsa (1942 Kalela; HЮХЭцЧ 1971). – RDB EF: 3, RDB RK: 3 (VU) *Ficaria verna (L.) HЮНs. – Rr: B. Klim., Seredka (1988 Kuznetsov; KЮгЧОЭsШЯ 1993). – RDB EF: 3, RDB RK: 3 (LC→NT) a Myosurus minimus L. – Rr: VЭШrвО GКrЧТЭsв (1998 Kashtanov); KЮгКrКЧНК (2004 Kravchenko & Kuznetsov). Ranunculus acris L. – Fq. (Norrlin 1871: *Fqq.) Ranunculus auricomus L. aggr. – Fq. (Norrlin 1871: *Fq.) Ranunculus cassubicus L. aggr. – Rr: B. KХТЦ., LКФО OЛШгОrШ (1997 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); UЧТЭsФКвК BКв, ЦКТЧХКЧН КЭ GКЯШsЭrШЯ IsХ. (2013 Timofeeva). (Norrlin 1871: B. KХТЦ. (KЮХХСОЦ).) – RDB RK: 3 Ranunculus fallax (АТЦЦ. & GrКЛ.) SХШЛШНК КРРr. – Rr: Kizhi (Kuznetsov 1993, no speciЦОЧs КЯКТХКЛХО). Ranunculus lammula L. – R: ЦКТЧХв ТЧ KТгСТ SФОrrТОs. (NШrrХТЧ 1871: SЯвКЭШУЧШs (SТЦЦТЧР); Kizhi (Günther).) Ranunculus lingua L. – Stfq. (NШrrХТЧ 1871: V. GЮЛК stfq; SСЮЧРК.) Ranunculus polyanthemos L. – Stfq. (NШrrХТЧ 1871: ЛОЭаООЧ V. GЮЛК КЧН VОРШrЮФsК.) Ranunculus repens L. – Fq. (Norrlin 1871: Stfq.) Reports of the Finnish Environment Institute 40 | 2014 167 Ranunculus reptans L. – Fq. (Norrlin 1871: *Fq.) Ranunculus sceleratus L. – Stfq. (Norrlin 1871: Stfq.) **Ranunculus subborealis TгЯОХ. (R. acris sЮЛsЩ. borealis (RОРОХ) NвЦКЧ) – Rr: Lipovitsy (2013 Kravchenko). *Thalictrum aquilegiifolium L. – R: KЮгКrКЧНК (HЮХЭцЧ 1971); TШХЯЮвК (HЮХЭцЧ 1971); KrШФСino (1952 Ramenskaya & Zaykova: KrКЯМСОЧФШ ОЭ КХ. 2000 К); ЛОЭаООЧ V. NТЯК КЧН VОРШrЮФsК (1896 Poppius); CСКЩШгОrШ (1896 Poppius); KКгСЦК (2013 Kravchenko); LТЩШЯТЭsв (2013 SвrУтЧОЧ, ШЛs.); TКЦЛТЭsв (2013 SвrУтЧОЧ, ШЛs.). – RDB EF: 3, RDB RK: 3 (NT) Thalictrum lavum L. – Fq. (Norrlin 1871: Fq.) Thalictrum simplex L. – R: SСЮЧРК (NШrrХТЧ 1871); AгСОЩЧКЯШХШФ (SЩКrrО 1945); KЮгКrКЧНК (HЮХЭцЧ 1971); TОХвКЭЧТФШЯШ (KЮгЧОЭsШЯ 1997); KТгСТ (KЮгЧОЭsШЯ 1993; 2007 Znamenskiy PTГ); VШХФШsЭrШЯ (1996 Kuznetsov; KЮгЧОЭsШЯ 1997); RОМСЧШв IsХ. (2004 Kravchenko). – RDB EF: 4 Trollius europaeus L. – Fq. (Norrlin 1871: Fq.) a Chelidonium majus L. – R. Kizhi (Norrlin 1871: Svyatnavolok (Simming, Günther).) a Papaver pseudoorientale (FОННО) MОНа. – Rr: Kizhi (2011 Timofeeva.) a Papaver somniferum L. – Rr: TШХЯЮвК (2011 Timofeeva); V. GЮЛК (2011 Timofeeva); KКгСЦК (2012 Kravchenko). **Corydalis solida (L.) CХКТrЯ. – R: ЦКТЧХв ТЧ KТгСТ SФОrrТОs, KТгСТ КЧН ПОа КНУКМОЧЭ ТsХКЧНs КЧН ЦКТЧХКЧН (KЮгЧОЭsШЯ 1993), Кs аОХХ Кs BОrОгШЯОЭs IsХ. Лв KХТЦ NШs ТЧ ЭСО NШrЭС (1988 Kuznetsov). a FumarТa oficТnalТs L. – Str. (Norrlin 1871: Fq.) *Ulmus glabra HЮНs. – R: TШХЯЮвК (HЮХЭцЧ 1971); LКНЦШгОrШ, SвЩЮЧ GШrК (1989 KrКЯМСОЧФШ, ШЛs.; KrКЯМСОЧФШ ОЭ КХ. 2000 К); OвКЭОЯsЭМСТЧК (1992 Kuznetsov; KЮгЧОЭsШЯ 1993); B. KХТЦ. (HЮХЭцЧ 1971), B. KХТЦ., KШsОХ′РК (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К) КЧН VШrШЛ’Т (2007 Kravchenko); NТгСЧОО MвКРrШгОrШ (2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013); LТЩШЯТЭsв, LКФО BОгНШЧЧШО (2013 Syrjänen). – RDB EF: 3, RDB RK: 3 (LC→NT) *Ulmus laevis PКХХ. – Stfq ШЧ LКФО OЧОРК sСШrОs ТЧ KТгСТ SФОrrТОs (ФЧШаЧ ПrШЦ КЭ ХОКsЭ 30 ХШМКХТЭТОs); ШЮЭsТНО sСШrОs ШЧХв V. NТЯК (HЮХЭцЧ 1971). (NШrrХТЧ 1871: SЯвКЭЧКЯШХШФ (KТгСТ).) – RDB EF: 3, RDB RK: 3 (LC→NT) *aHumulus lupulus L. – Rr: Paleostrov (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3, RDB RK: 3 (NT); МЮХЭТЯКЭОН КЧН ОsМКЩОН ТЧ ЭСО КrОК, КЧН ЭСОsО ШММЮrrences are not protected. Urtica dioica L. – Fq. (Norrlin 1871: Fq.) a Urtica urens L. – Rr, ЭСО ШЧХв rОМОЧЭ rОМШrН: V. GЮЛК (1999 Timofeeva). (Norrlin 1871: *Fq.) Alnus glutinosa (L.) Gaertn. – Stfq. (Norrlin 1871: Fq ТЧ TШХЯЮвК – V. GЮЛК – VОРШrЮФsК КrОК, also Dianova Gora.) Alnus × hybrida Gaertn. (A. × pubescens TКЮsМС) – R. (NШrrХТЧ 1871: V. GЮЛК.) Alnus incana (L.) MШОЧМС – Fq. (Norrlin 1871: *Fqq). VКr. argentata Norrlin (A. argentata (NШrrХ.) TгЯОХ.) НОsМrТЛОН Лв NШrrХТЧ (1871: 168) ШЧ ЭСО ЛКsТs ШП ЭСО ЦКЭОrТКХ МШХХОМЭОН ПrШЦ ЭСО КrОК (SСЮЧРК, AгСОЩЧКЯШХШФ & V. GЮЛК). Betula nana L. – Fq. (Norrlin 1871: *Fq–fqq.) *Betula pendula RШЭС – Fq. (Norrlin 1871: *Fq.) *VКr. karelica (MОrМФХ.) HтЦОЭ-AСЭТ Тs ФЧШаЧ ПrШЦ ЭСО ОЧЭТrО ГКШЧОгСвО (SШФШХШЯ 1950; AЭХКs.., 1973), КЧН ЭСО ЧЮЦЛОr ШП ФЧШаЧ ЭrООs аКs ОsЭТЦКЭОН ЭШ ЛО МК. 3 500 (LКЮr 1997). HШаОЯОr, ЧШаКНКвs ЭСТs rКМО Тs ЮЧНОr ЭСrОКЭ to disappear from the peninsula due to negative ecological and genetic factors and illegal МЮЭЭТЧРs (VОЭМСТЧЧТФШЯК ОЭ КХ. 2013). – RDB RK: 2 (EN) Betula pubescens Ehrh. – Fq. (Norrlin 1871: *Fqq.) Montia fontana L. – Rr, ШЧХв ТЧ KТгСТ SФОrrТОs: BШвКrsЭМСТЧК (KЮгЧОЭsШЯ 1993); B. LОХТФ. (1998 Kashtanov); ГЮЛШЯШ (2012 Kravchenko); PШН’ОХЧТФТ (2012 KrКЯМСОЧФШ, ШЛs.). (NШrrХТЧ 1871: *Stfq–fq.) a Agrostemma githago L. – OЧХв ШХН rОМШrНs: KТгСТ (HЮХЭцЧ 1971). 168 Reports of the Finnish Environment Institute 40 | 2014 Alsine media L. (Stellaria media (L.) CТrТХХШ) – Fq. (Norrlin 1871: *Fqq.) Arenaria serpyllifolia L. – Fq. (Norrlin 1871: Fq.) *Cerastium alpinum L. – Rr: MОХШТРЮЛК (HЮХЭцЧ 1971); B. KХТЦ., SОЧЧКвК GЮЛК (1898 LТЧНrШЭС & CКУКЧНОr) КЧН GrвгЧКЯШХШФ CКЩО (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). (NШrrХТЧ 1871: SСЮЧРК). – RDB RK 3: (NT) Cerastium holosteoides Fr. (C. fontanum BКЮЦР. sЮЛsЩ. vulgare (HКrЭЦ.) GrОЮЭОr & BЮrНОЭ) – Fq. (Norrlin 1871: *Fqq.) Cerastium scandicum (H. GКrЭЧОr) KЮгОЧ. (C. fontanum sЮЛsЩ. fontanum) – R. (Norrlin 1871: AгСОЩЧКЯШХШФ КЧН VОРШrЮФsК; Кs C. alpestre HКrЭЦ.) CoccygantСe los-cuculТ (L.) RМСЛ. (LycСnТs los-cuculТ L.) – Fq. (Norrlin 1871: *Fq–fqq.) *Dianthus arenarius L. s. sЭr. – Rr: B. Lelik., Radkol’e Cape (1988 Kuznetsov: Kuznetsov 1997). – RDB RK: 3 (LC→NT) a Dianthus barbatus L. – R: ПОа rОМШrНs КПЭОr 2007. Dianthus deltoides L. – Fq. (Norrlin 1871: Stfq.) Dianthus superbus L. – Rr: TШХЯЮвК (HЮХЭцЧ 1971). Hylebia nemorum FШЮrr. (Stellaria nemorum L.) – Str. a Melandrium album (Mill.) Garcke (Silene latifolia PШТr. sЮЛsЩ. alba (Mill.) Greuter & BurНОЭ) – Fq. (Norrlin 1871: Fqq.) a Melandrium dioicum (L.) Coss. & Germ. (Silene dioica (L.) CХКТrЯ.) – R: ПОа rОМШrНs КПЭОr 1999. Moehringia trinervia (L.) CХКТrЯ. – Stfq. (NШrrХТЧ 1871: V. GЮЛК.) Myosoton aquaticum (L.) MШОЧМС. – Stfq ТЧ KТгСТ SФОrrТОs: irsЭ rОМШrНОН ПrШЦ KТгСТ IsХ. (1898 Cajander & Lindroth; CКУКЧНОr & LТЧНrШЭС 1900); ЧЮЦОrШЮs rОМОЧЭ МШХХОМЭТШЧs (KЮгЧОЭsШЯ 1997; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3 a Oberna behen (L.) IФШЧЧ. (Silene vulgaris (MШОЧМС) GКrМФО) – Fq. (Norrlin 1871: *Stfq–fq.) a Psammophiliella muralis (L.) IФШЧЧ. (Gypsophila muralis L.) – OЧХв ШХН rОМШrНs: ЛОЭаООЧ TШХЯЮвК КЧН KШsЦШгОrШ (NШrrХТЧ 1871). Sagina nodosa (L.) FОЧгХ – Str. (Norrlin 1871: Stfq ТЧ NE (AгСОЩЧКЯШХШФ – PКНЦШгОrШ).) Sagina procumbens L. – Stfq. (Norrlin 1871: *Fq.) a SaponarТa oficТnalТs L. – Rr, ПОа rОМШrНs КПЭОr 2010. Scleranthus annuus L. – Str. Scleranthus polycarpos L. – Fq. *Silene nutans L. – OЧХв ШХН rОМШrНs: MТгСШsЭrШЯ (BОгКвs 1911); KЮгКrКЧНК (H; BОгКвs 1911); HКrХШЯШ (HЮХЭцЧ 1971). – RDB RK: 3 (LC→NT) a Spergula sativa Boenn. (S. arvensis L. sЮЛsЩ. sativa (MОrЭ. & А. D. J. KШМС) ČОХКФ.) – P. (Norrlin 1871: *Fq, as S. arvensis s. lat.) a Spergularia rubra (L.) J. PrОsХ & C. PrОsХ – P. (Norrlin 1871: Shunga.) Stellaria alsine GrТЦЦ – Rr: KХТЦ NШs КЧН VОРШrЮФsК (HЮХЭцЧ 1971); TЮrКsЭКЦШгОrШ (2012 Kravchenko). Stellaria crassifolia EСrС. – Rr: KКsФШsОХРК (2013 SвrУтЧОЧ, ШЛs.); TКЦЛТЭsв (2013 SвrУтЧОЧ, ШЛs.). Stellaria fennica (MЮrЛ.) PОriХ – R: TТЩТЧТЭsв, VКrЧКЯШХШФ (2004 Piirainen); B. KХТЦ., KШЧНК (2004 Uotila), VШrШЛ’Т (2007 Kravchenko); RОМСФК (2012 Kravchenko); VОrФСЧОО MвКРrШгОrШ (2012 Kravchenko); LКФО RЮРШгОrШ (2013 Kravchenko). Stellaria graminea L. – Fq. (Norrlin 1871: *Fqq.) Stellaria holostea L. – Rr: B. Klim., Klimenitsy (2004 Kravchenko, 2004 Piirainen). Stellaria longifolia MüСХ. Об АТХХН. – Rr: Padmozero (1993 Kravchenko); RОМСЧШв IsХ. (2004 Kravchenko); V. GЮЛК (2013 Kravchenko). Stellaria palustris HШППЦ. – Stfq. Viscaria viscosa (Scop.) Aschers. (Lychnis viscaria L.) – R. a AmarantСus retrolexus L. – Rr: Shunga (2011 Timofeeva). a Atriplex prostrata Boucher ex DC. (A. latifolia АКСХОЧЛ.) – Rr: V. NТЯК (1999 Timofeeva & Rudkovskaya). a Atriplex patula L. – R. a Chenopodium album L. – Fq. (Norrlin 1871: *Fqq; ТЧМХ. C. suecicum.) a Reports of the Finnish Environment Institute 40 | 2014 169 Chenopodium glaucum L. – R. Chenopodium polyspermum L. – R. a Chenopodium suecicum MЮrr – Str. Bistorta oficТnalТs DОХКrЛrО – Str. (NШrrХТЧ 1871: SСЮЧРК, TШХЯЮвК.) Bistorta vivipara (L.) DОХКrЛrО – R. (Norrlin 1871: *Fqq.) a Fallopia convolvulus (L.) Á. LöЯО – Fq. (Norrlin 1871: *Fq.) a Fallopia dumetorum (L.) HШХЮЛ – OЧХв ШХН rОМШrНs: V. GЮЛК (FКРОrsЭröЦ & LЮЭСОr 1946). Persicaria amphibia (L.) GrКв – Fq. (Norrlin 1871: Fqq.) Persicaria hydropiper (L.) SЩКМС – Stfq. (Norrlin 1871: Fq.) Persicaria lapathifolia (L.) GrКв – Str. (Norrlin 1871: Fq.) Persicaria minor (HЮНs.) OЩТг – Fq. (Norrlin 1871: Fq; Кs Polygonum mitis Schrank.). a Persicaria tomentosa (Schrank) Bicknell (Persicaria lapathifolia sЮЛsЩ. pallida (АТЭС.) S. EФЦКЧ & T. KЧЮЭssШЧ) – Fq. (Norrlin 1871: Shunga.) a Polygonum arenastrum Boreau (P. aviculare sЮЛsЩ. microspermum (JШrН. Об BШrОКЮ) BОСОr) – R. a Polygonum aviculare L. – Fq. (Norrlin 1871: *Fqq.) a Rheum rhabarbarum L. – Rr: KТгСТ IsХ. (1998 Kravchenko; KrКЯМСОЧФШ 2007). Rumex acetosa L. – Fq. (Norrlin 1871: *Fqq.) Rumex acetosella L. – Fq. (Norrlin 1871: *Fqq.) Rumex maritimus L. – Rr: ШЧХв ШХН rОМШrНs: V. GЮЛК. – RDB EF: 3 Rumex aquaticus L. – Stfq. (Norrlin 1871: *P.) Rumex crispus L. – R. Rumex fontanopaludosus Kalela (R. acetosa var. fontanopaludosus (KКХОХК) HвХ.) – Rr: Shunga (1942 Kalela). Rumex longifolius DC. – Fq. (Norrlin 1871: *Fqq.) a Rumex obtusifolius L. – Rr: KТгСТ IsХ. (2007 Kravchenko). Rumex pseudonatronatus BШrЛпs – Str. Rumex rossicus MЮrЛ. (Rumex maritimus L. sЮЛsЩ. rossicus (MЮrЛ.) KrвХ.) – Rr: аТЭСШЮЭ ОбКМЭ ХШМКХТЭв (BШrШНТЧК 1977: ЦКЩ; ЧШ ЯШЮМСОr ТЧ LE). Rumex tСyrsТlorus FТЧРОrС. – Stfq. Hypericum maculatum CrКЧЭг – Fq. (Norrlin 1871: *Fq.) *Hypericum perforatum L. – R: ШЧХв ТЧ KТгСТ SФОrrТОs, аСОrО ПШr ЭСО irsЭ ЭТЦО rОМШrНОН КЭ B. KХТЦ., GКrЧТЭsв (FКРОrsЭröЦ & LЮЭСОr 1946); ХКЭОr КХsШ Grвг IsХ. (1988 Kuznetsov; KЮгЧОЭsШЯ 1993; 1999 Kravchenko & Kashtanov); BЮФШХ′ЧТФШЯsФТв IsХ. (1999 Kashtanov); B. LОХТФ IsХ. (2004 Kravchenko H); OrШгС IsХ. (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); ВКЦ IsХ. (1998 Kashtanov). ДErrШЧОШЮsХв ПrШЦ RКНФШХвО IsХ. (KrКЯМСОЧФШ ОЭ КХ. 2000 К).Ж – RDB EF: 3, RDB RK: 3 (LC→NT) Elatine hydropiper L. – Str: V. GЮЛК (1870 Norrlin; NШrrХТЧ 1871; 2000 Timofeeva & Rudkovskaya; 2010 Kravchenko); KКЧОЯ IsХ. (1999 Kashtanov); B. KХТЦ., GКrЧТЭsв BКв (1999 Kravchenko & Kashtanov), KЮrРОЧТЭsв КЧН VШrШЛ’Т (ЛШЭС 2007 Kravchenko); BШХЧТМСЧвТ (2010 Kravchenko); KКгЦК (2012 Kravchenko). *Elatine triandra SМСФЮСr. – Rr: AгСОЩЧКЯШХШФ (SЩКrrО 1945); V. GЮЛК (1870 Norrlin; NШrrХТЧ 1871; 2010 Kravchenko); VОРШrЮФsК КrОК (HЮХЭцЧ 1971). – RDB EF: 3, RDB RK: 3 (VU) a Viola arvensis MЮrrКв – Str. (Norrlin 1871: *Fq.) Viola canina L. – Rr: Mikkovo (1999 Timofeeva, Rudkovskaya & Kryshen); V. GЮЛК (2010 Kravchenko). ДNШrrХТЧ (1871) НТН ЧШЭ sОЩКrКЭО V. canina from V. nemoralis, sОО ЛОХШаЖ. *,**Viola collina BОssОr – Rr: Padmozero (1986 Kuznetsov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3, RDB RK: 3 (LC→NT) Viola epipsila LОНОЛ. – Fq. (Norrlin 1871: *Fq–fqq.) Viola mirabilis L. – Stfq. (Norrlin 1871: *Stfq.) Viola nemoralis Kütz. (V. montana КЮМЭ. ЧШЧ L.) – Fq. (Norrlin 1871: *Fq, as V. lavТcornТs (SЦ.) NШrrХТЧ (1871), Кs аОХХ Кs sОЯОrКХ rОМОЧЭ КЮЭСШrs (О.Р., MКrМЮssОЧ 2010) НШ ЧШЭ sОЩКrКЭО V. nemoralis from V. canina. Viola palustris L. – Fq. (Norrlin 1871: *Fq–fqq.) a a 170 Reports of the Finnish Environment Institute 40 | 2014 Viola rupestris F. А. SМСЦТНЭ – Str. (Norrlin 1871: Fq ТЧ SСЮЧРК КЧН TШХЯЮвК). Viola riviniana RМСЛ. – Fq. (Norrlin 1871: *Fq.) Viola selkirkii PЮrsС Об GШХНТО – Str. (Norrlin 1871: P.) Viola tricolor L. – Fq. (Norrlin 1871: Fq.) *Helianthemum nummularium (L.) Mill. – Rr: B. Lelik., Radkol’e Cape (1988 Kuznetsov; KЮгЧОЭsШЯ 1993, 1997; ЧЮЦОrШЮs rОМОЧЭ sЩОМТЦОЧs ТЧ H КЧН PTГ). OЧХв ШЧО ЦШrО ХШМКХТЭв ТЧ KКrОХТК, КЭ LКФО ВКЧТsвКrЯТ ТЧ Karelia ladogensis. – RDB EF: 2, RDB RK: 2 (EN) Arabidopsis thaliana (L.) HОвЧС. – Stfq. (NШrrХТЧ 1871: SОЧЧКвК GЮЛК (SТЦЦТЧР).) a Armoracia rusticana G. GКОrЭЧ., B. MОв. & SМСОrЛ. – Rr. a Barbarea arcuata (OЩТг Об J. PrОsХ & C. PrОsХ) RМСЛ. (Barbarea vulgaris R. Br. var. arcuata OЩТг Об J. PrОsХ & C. PrОsХ) Fr. – Fq. Barbarea stricta AЧНrг. – Stfq. (Norrlin 1871: *Stfq.) a Brassica campestris L. (B. rapa L. sЮЛsЩ. campestris (L.) A. R. CХКЩСКЦ) – Str. a Bunias orientalis L. – R. a Camelina alyssum (MТХХ.) TСОХХ. – OЧХв ШХН rОМШrНs: stfq in Shunga (Norrlin 1871). a Capsella bursa-pastorТs (L.) MОНТФ. – Fq. (Norrlin 1871: *Fqq.) **Cardamine amara L. – R, ЛЮЭ stfq in Kizhi Skerries. Cardamine dentata Schult. (C. pratensis L. sЮЛsЩ. paludosa (KЧКП) ČОХКФ.) – Fq. (Norrlin 1871: R; SСЮЧРК, V. GЮЛК.) Descurainia sophia (L.) АОЛЛ. Об PrКЧЭХ – R. Draba nemorosa L. – Rr: KЮгКrКЧНК, VТЭsТЧШ (1998 Kravchenko); B. KХТЦ., LШЧРКsв (1987 Kuznetsov); MОРШsЭrШЯ IsХ. (2004 Kravchenko). – RDB EF: 4 a Erophila verna (L.) CСОЯКХХ. – Rr. AгСОЩЧКЯШХШФ (SЩКrrО 1945); KТгСТ КrОК (HЮХЭцЧ 1971). – RDB EF: 3 a Erysimum cheiranthoides L. – Fq. (Norrlin 1871: *Fq.) Erysimum strictum G. GКОrЭЧ., B. MОв. & SМСОrЛ. – Rr: only old records: Shunga (Norrlin 1871); KЮгКrКЧНК (GüЧЭСОr 1880). a Hesperis matronalis L. – Rr. a Lepidium ruderale L. – Rr. a Neslia paniculata (L.) DОsЯ. – OЧХв ШХН rОМШrНs: SСЮЧРК (NШrrХТЧ 1871; GüЧЭСОr 1880). a Raphanus raphanistrum L. – Str. (Norrlin 1871: *Fq.) Rorippa palustris (L.) BОssОr – Fq. (Norrlin 1871: *Fq.) a Sinapis arvensis L. – Rr. Subularia aquatica L. – Str. (Norrlin 1871: Fq ТЧ V. GЮЛК). a Thlaspi arvense L. – Fq. (Norrlin 1871: *Fqq.) a Thlaspi caerulescens J. PrОsХ & C. PrОsХ – Rr: VШХФШsЭrШЯ (1996 Kuznetsov; KЮгЧОЭsШЯ 1997). Turritis glabra L. – P. (Norrlin 1871: P.) a Populus balsamifera L. – Rr: Rechka (2012 Kravchenko). Populus tremula L. – Fq. (Norrlin 1871: *Fqq; МШЩТШsО ТЧ V. GЮЛК – VОРШrЮФsК.) Salix aurita L. – Stfq. (Norrlin 1871: *Stfq–fq.) Salix caprea L. – Fq. (Norrlin 1871: *Fq.) Salix cinerea L. – Fq. (Norrlin 1871: *Fq.) Salix lapponum L. – Str. (NШrrХТЧ 1871: V. GЮЛК – VОРШrЮФsК.) Salix myrsinifolia SКХТsЛ. – Fq. (Norrlin 1871: Fq ТЧ V. GЮЛК.) Salix myrtilloides L. – R. Salix pentandra L. – Fq. (Norrlin 1871: *Fq.) Salix phylicifolia L. – Fq. (Norrlin 1871: *Fq.) Salix rosmarinifolia L. (S. repens L. sЮЛsЩ. rosmarinifolia (L.) AЧНОrssШЧ) – R. (Norrlin 1871: Shunga.) Salix starkeana АТХХН. (S. livida АКСХОЧЛ.) – Str. (Norrlin 1871: *Fq–fqq.) a Salix viminalis L. – Rr. ErЧТЭsФТв IsХ. (1999 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 4 Andromeda polifolia L. – Str. (Norrlin 1871: Fq.) Reports of the Finnish Environment Institute 40 | 2014 171 ArctostapСylos uva-ursТ (L.) SЩrОЧР. – Str. (Norrlin 1871: *Fq.) Calluna vulgaris (L.) HЮХХ. – Fq. (Norrlin 1871: *Fq.) Chamaedaphne calyculata (L.) MШОЧМС. – Fq. (Norrlin 1871: *Fqq.) Ledum palustre L. (Rhododendron tomentosum HКrЦКУК) – Stfq. (Norrlin 1871: Fq ТЧ V. GЮЛК – VОРШrЮФsК.) Oxycoccus microcarpus TЮrМг. Об RЮЩr. (Vaccinium microcarpum (TЮrМг. Об RЮЩr.) SМСЦКХС.) – Rr: ШЧХв iОХН ЧШЭОs, О.Р. LКФО VКЧМСШгОrШ (2012 KrКЯМСОЧФШ, ШЛs.). Oxycoccus palustris Pers. (V. oxycoccos L.) – Stfq. (Norrlin 1871: *Fq– fqq.) Vaccinium myrtillus L. – Fq. (Norrlin 1871: Fqq.) Vaccinium uliginosum L. – Stfq. (Norrlin 1871: Fq ТЧ SА ЩКrЭ.) VaccТnТum vТtТs-Тdaea L. – Fq. (Norrlin 1871: *Fqq.) Moneses unТlora (L.) A. GrКв. – Str. (Norrlin 1871: Str– p.) Orthilia secunda (L.) HШЮsО. – Fq. (Norrlin 1871: *Fq.) Pyrola chlorantha Sа. – R. (Norrlin 1871: *P.) Pyrola minor L. – Stfq. (Norrlin 1871: *Fq.) Pyrola media Sа. – R. Pyrola rotundifolia L. – Fq. (Norrlin 1871: *Fq–fqq.) P. rotundifolia var. chloranthoides NШrrХТЧ (1871:160) аКs НОsМrТЛОН ПrШЦ V. GЮЛК. *Hypopitys monotropa (L.) CrКЧЭг sЮЛsЩ. hypopitys (Monotropa hypopitys L.) – R, mainly in KТгСТ SФОrrТОs: KТгСТ IsХ. (1899 Cajander & Lindroth; CКУКЧНОr & LТЧНrШЭС 1900); KШsЦШгОrШ, GШrsФКвК (1979 RШЧФШЧОЧ, ШЛs.); RКНФШХвО, LвМСФШЯ КЧН EРХШЯ IsХОs (КХХ 1998 Kashtanov); BЮФШХЧТФШЯsФТв КЧН KКХРШЯ IsХОs (ЛШЭС ТЧ 1999 Kashtanov); B. KХТЦ., ErЧТЭsФТв КЧН MвКХ IsХОs (all 1999 Kravchenko & Kashtanov); VОrЭТХШЯШ (1999 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); B. Klim. (2000 Polevoy PTГ); VКЧМСШгОrШ (2004 Talbonen PTГ; KrКЯМСОЧФШ & TТЦШПООЯК 2013); ВЮгСЧвТ OХОЧТв IsХ. (2004 Kravchenko); LТЩШЯТЭsв (2013 Polevoy PTГ); TТЩТЧТЭsв, VКrЧКЯШХШФ (2004 Piirainen). – RDB EF: 3, RDB RK: 3 (LC→NT) Empetrum nigrum L. – R. (Norrlin 1871: *Fq.) PОrСКЩs ШЧХв sЮЛsЩ. hermaphroditum (HКРОrЮЩ) BöМСОr (E. hermaphroditum HКРОrЮЩ) ШММЮrs ТЧ ЭСО КrОК. a Androsace ilТformТs Retz. – R: ПОа rОМШrНs sТЧМО 2010. Lysimachia vulgaris L. – Fq. (Norrlin 1871: *Stfq.) NaumburgТa tСyrsТlora (L.) RМСЛ. (LysТmacСТa tСyrsТlora L.) – Fq. (Norrlin 1871: *Stfq.) Trientalis europaea L. – Fq. (Norrlin 1871: *Fq–fqq.) **Tilia cordata MТХХ. – R, ЛЮЭ fq ТЧ KТгСТ SФОrrТОs. SШЦОЭТЦОs ПШrЦs ЩЮrО sОМШЧНКrв СОrЛ rТМС ПШrОsЭs ШЧ sШЦО ТsХКЧНs ХТФО BОrОгШЯОЭs, DШХРТв, Grвг, KКХРШЯ, UТЦв, ОЭМ. (rОХОЯцs ЩrШЯТНОН Лв KЮгЧОЭsШЯ 1997). AММШrНТЧР ЭШ GüЧЭСОr (1880: 19) ШММЮЩТОs «…КХЦШsЭ КХХ ТsХКЧНs ТЧ LКФО OЧОРК». (NШrrХТЧ 1871: SСЮЧРК.) a Abutilon theophrasti MОНТФ. – Rr: V. GЮЛК (2010 Kravchenko). a Lavatera thuringiaca L. – Rr: V. GЮЛК (2010 Kravchenko); TШХЯЮвК (2011 Timofeeva); Kazhma (2012 Timofeeva). a Malva pusilla SЦ. – OЧХв ШХН rОМШrНs: ЦКТЧХв НЮrТЧР АШrХН АКr II (FКРОrsЭöЦ & LЮЭСОr 1945; HЮХЭцЧ 1971). a Euphorbia helioscopia L. – OЧХв ШХН rОМШrНs: TШХЯЮвК (GüЧЭСОr 1880; KШrШХОЯК 1927–1928). a Euphorbia virgata АКХНsЭ. & KТЭ. (E. esula L. sЮЛsЩ. tommassiniana (BОrЭШХ.) KЮгЦКЧШЯ) – R. **Daphne mezereum L. – Fq. (Norrlin 1871: P.) **Chrysosplenium alternifolium L. – R. (Norrlin 1871: *P.) Saxifraga hirculus L. – Rr: TКЦЛТЭsв – KКsФШsОХРК (2013 Syrjänen). (Norrlin 1871: P.) – RDB EF: 3 Saxifraga nivalis L. – Rr: AгСОЩЧКЯШХШФ (SЩКrrО 1945; 1996 Kashtanov); TОХЩШгОrШ (1952 Ramenskaya & Zaykova; KrКЯМСОЧФШ ОЭ КХ. 2000 К); VОРШrЮФsК, TШХЯЮвК & FОНШЭШЯШ (HЮХЭцЧ 1971, ЛЮЭ ЧШ ЯШЮМСОrs ТЧ H). (NШrrХТЧ 1871: AгСОЩЧКЯШХШФ.) – RDB EF: 3 a Hylotelephium triphyllum (HКа.) HШХЮЛ (Hylotelephium telephium (L.) H. OСЛК, МШХХ.) – Rr: KТгСТ IsХ. (Kravchenko 2007). Sedum acre L. – R. (Norrlin 1871: Fq in Shunga.) 172 Reports of the Finnish Environment Institute 40 | 2014 GrossularТa uva-crТspa (L.) Mill. (RТbes uva-crТspa L.) – Rr: V. GЮЛК (2012 Kravchenko); LКЦЛКsrЮМСОТ (2013 Timofeeva). Ribes nigrum L. – Stfq. (Norrlin 1871: Stfq ТЧ V. GЮЛК.) **Ribes spicatum E. RШЛsШЧ – Fq. (Norrlin 1871: Stfq, as R. rubrum L.) Parnassia palustris L. – Str. (Norrlin 1871: *Fqq.) Drosera anglica HЮНs. – Str. (NШrrХТЧ 1871: ЛОЭаООЧ V. GЮЛК КЧН VОРШrЮФsК.) Drosera rotundifolia L. – Stfq. (Norrlin 1871: *Fq.) a Alchemilla acutiloba OЩТг – Fq. (Norrlin 1871: *Fqq; Кs Alchemilla vulgaris L.) a Alchemilla baltica SКЦ. Об JЮг. – R. a Alchemilla conglobata H. LТЧНЛ. – Rr: Oyatevstchina (2012 Kravchenko). a Alchemilla cymatophylla JЮг. – Rr: Oyatevstchina (2012 Kravchenko). a Alchemilla glaucescens АКХХr. – Stfq. a Alchemilla hirsuticaulis H. LТЧНЛ. – R. a Alchemilla micans BЮsОr – Str. a Alchemilla monticola OЩТг – Fq. a Alchemilla propinqua H. LТЧНЛ. Об JЮг. – Str. a Alchemilla sarmatica JЮг. – R. a Alchemilla subcrenata BЮsОr – Fq. a Cerasus vulgaris Mill. (Prunus cerasus L.) – Rr: ГЮЛШЯШ (2012 Kravchenko); KТгСТ IsХ. (2014 Timofeeva). Comarum palustre L. – Fq. (Norrlin 1871: *Fqq.) Cotoneaster antoninae JЮг. – Str: Kizhi Skerries (1986 Khokhlova; 1988 Kuznetsov; 1999 Kravchenko & Kashtanov) and Kosmozero (1999 Timofeeva et al.; KrКЯМСОЧФШ 2010). – RDB EF: 4 Cotoneaster laxТlorus JКМq. Об LТЧНХ. (C. melanocarpus (BЮЧРО) LШЮНШЧ; C. vulgaris auct. ЧШЧ LТЧНХ.) – P. (NШrrХТЧ 1871: AгСОЩЧКЯШХШФ, SСЮЧРК; МШХХОМЭТЯОХв Кs C. vulgaris). a Crataegus monogyna JКМq. – Rr: Shunga (2012 Kravchenko). Filipendula ulmaria (L.) MКбТЦ. – Fq. (Norrlin 1871: *Fqq.) a Fragaria × ananassa (АОsЭШЧ) DЮМСОsЧО Об RШгТОr – Rr: B. Klim., Klimenitsy (2004 Kravchenko). Fragaria vesca L. – Fq. (Norrlin 1871: *Fqq.) Geum rivale L. – Fq. (Norrlin 1871: Fqq ТЧ SСЮЧРК КЧН V. GЮЛК.) Geum urbanum L. – Stfq. (Norrlin 1871: Shunga.) a Malus domestica BШrФС. – Rr: KТгСТ IsХ. (2014 Timofeeva). Padus avium Mill. (Prunus padus L.) – Fq. (Norrlin 1871: *Fqq.) Potentilla anserina L. – Fq. (Norrlin 1871: Fq.) Potentilla argentea L. – Fq. (NШrrХТЧ 1871: V. GЮЛК, fq in Shunga.) Potentilla erecta (L.) RКОЮsМС. – Fq. (Norrlin 1871: *Fqq.) Potentilla goldbachii (Rupr.) Rupr. (P. thuringiaca sЮЛsЩ. goldbachii (RЮЩr.) TС. АШХП) – Rr: KТгСТ IsХ. (1896 Poppius); TШХЯЮвК (1993 Kravchenko). Potentilla heidenreichii Zimmeter (P. intermedia sЮЛsЩ. heidenreichii (ГТЦЦОЭОr) TгЯОХОЯ) – Rr, only old records: Shunga (Norrlin 1871). Potentilla “impolita” КЮМЭ., ЧШЧ АКСХОЧЛ. – Str. Potentilla intermedia L. – Stfq. (Norrlin 1871: Shunga.) Potentilla norvegica L. – Stfq. (NШrrХТЧ 1871: V. GЮЛК.) **Rosa acicularis LТЧНХ. – Fq. (Norrlin 1871: Fq.) Rosa majalis HОrrЦ. – Fq. (NШrrХТЧ 1871: V. GЮЛК, SСЮЧРК.) Rubus arcticus L. – Str. (NШrrХТЧ 1871: SСЮЧРК, V. GЮЛК.) Rubus chamaemorus L. – Str. (NШrrХТЧ 1871: SШsХКЧШЯЧКЯШХШФ, V. GЮЛК.) **Rubus humulifolius C. A. MОв. – Rr: TШХЯЮвК КЧН KХТЦ NШs (HЮХЭцЧ 1971); UЧТЭsК (1896 Poppius); V. GЮЛК (1896 Poppius); KКsФШsОХРК (2013 SвrУтЧОЧ, ШЛs.); LТЩШЯТЭsв (2013 Kravchenko); PШХвК (2013 SвrУтЧОЧ, ШЛs.); TКЦЛТЭsв (2013 SвrУтЧОЧ, ШЛs.); TТЩТЧТЧТЭsв (2013 SвrУтЧОЧ, ШЛs.); UгФТв SКХЦв (2013 SвrУтЧОЧ, ШЛs.). – RDB EF: 3 Rubus idaeus L. – Fq. (Norrlin 1871: Fqq.) a Reports of the Finnish Environment Institute 40 | 2014 173 Rubus saxatilis L. – Fq. (Norrlin 1871: Fqq.) SanguТsorba oficТnalТs L. – Rr: B. Klim. (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ 2007); TТЩТЧТЭsв (2013 Syrjänen). Sorbus aucuparia L. – Fq. (Norrlin 1871: Fq.) Amoria hybrida (L.) C. Presl (Trifolium hybridum L.) – P. Amoria repens (L.) C. Presl (T. repens L.) – Fq. (Norrlin 1871: Fqq.) Chrysaspis aurea (Pollich) Greene (T. aureum PШХХТМС) – Str. (NШrrХТЧ 1871: V. GЮЛК.) Chrysaspis spadicea (L.) Greene (T. spadiceum L.) – R. (Norrlin 1871: Fq in Shunga.) a Galega orientalis LКЦ. – Rr: V. NТЯК (2011 Timofeeva). Lathyrus aleuticus (GrООЧО) PШЛОН. (L. japonicus АТХХН. ЯКr. aleuticus (HКrЭЦ.) KКrХssШЧ) – Rr: MОРШsЭrШЯ IsХ. (2004 Kravchenko); RОМСЧШТ IsХ. (2004 Piirainen). Lathyrus palustris L. – Stfq. (Norrlin 1871: Shunga.) a Lathyrus pisiformis L. – Rr: KТгСТ IsХ. (2007 Znamenskiy PTГ; KrКЯМСОЧФШ 2007). Lathyrus pratensis L. – Fq. (Norrlin 1871: *Fq.) Lathyrus sylvestris L. – R: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.; HЮХЭцЧ 1971); ЛЮЭ stfq in Kizhi SФОrrТОs: KТгСТ IsХ. (1994 Kuznetsov; KЮгЧОЭsШЯ 1997); KКХРШЯ IsХ. (1999 Kashtanov); BЮФШХ’ЧТФШЯsФТв IsХ. (1999 Kashtanov); ОЭМ. Lathyrus vernus (L.) BОrЧС. – Fq. (Norrlin 1871: *Stfq.) a Lupinus polyphyllus LТЧНХ. – Rr: Pod’elniki (2012 Kravchenko). a Melilotus albus MОНТФ. – Rr: KТгСТ IsХ. (1996 Kuznetsov; KЮгЧОЭsШЯ 1997). a MelТlotus oficТnalТs (L.) LКЦ. – Rr: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1945); KКгСЦК (2012 Kravchenko). a Pisum sativum L. – Rr: Kazhma (2012 Kravchenko & Fadeeva). Trifolium medium L. – Fq. (NШrrХТЧ 1871: V. GЮЛК.) Trifolium pratense L. – Fq. (Norrlin 1871: Fq.) Vicia cracca L. – Fq. (Norrlin 1871: Fqq.) a Vicia hirsuta (L.) GrКв – R. (Norrlin 1871: Fq in Shunga.) a Vicia sativa L. – Rr: Kosmozero (1999 Timofeeva & Rudkovskaya). (Norrlin 1871: Shunga.) Vicia sepium L. – Fq. (Norrlin 1871: *Fq.) Vicia sylvatica L. – Str. (Norrlin 1871: *P.) Vicia tetrasperma (L.) SМСrОЛ. – R. Lythrum salicaria L. – Fq. (Norrlin 1871: Fq.) Peplis portula L. Str. – R: several recent records from B. Klim. (Norrlin 1871: Fq ТЧ V. GЮЛК.) NШЭ rОМШrНОН ПrШЦ V. GЮЛК ТЧ 1999–2013. Chamaenerion angustifolium (L.) Scop. (Epilobium angustifolium L.) – Fq. (Norrlin 1871: *Fqq.) **Circaea alpina L. – Str. (Norrlin 1871: B. Klim.) a Epilobium adenocaulon HКЮssФЧ. – Fq. Epilobium collinum C. C. Gmel. – R. Epilobium montanum L. – Str. (Norrlin 1871: *Stfq–fq.) Epilobium palustre L. – Fq. (Norrlin 1871: Stfq.) a Epilobium pseudorubescens A. Skvorts. (E. ciliatum RКП.) – Rr: V. GЮЛК (2010 Kravchenko); Kazhma (2012 Kravchenko). MyrТopСyllum alternТlorum DC. – Fq. (Norrlin 1871: R in Shunga.) Myriophyllum sibiricum KШЦ. – Str. (Norrlin 1871: Fq; Кs M. spicatum L.) *Myriophyllum verticillatum L. – R: ЛОЭаООЧ TКrШЯsФКвК КЧН BШРШЦШХШЯsФКвК КЧН TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1945); ГСКrЧТФШЯШ (1986 Stoikina PTГ); V. GЮЛК (1999 Butskih, Kryshen & Timofeeva); VШХФШsЭrШЯ (1986 & 1992 Kuznetsov); B. KХТЦ., GКrЧТЭsФКвК BКв (1999 Kravchenko & Kashtanov); OrШгС IsХ. (1999 Kravchenko & Kashtanov); VШгСЦКrТСК RТЯОr (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB RK: 3 (DD) a Acer platanoides L. – Rr: V. GЮЛК (2010 Kravchenko). Linum catharticum L. – Str. (NШrrХТЧ 1871: SСЮЧРК – PКНЦШгОrШ; V. GЮЛК.) Oxalis acetosella L. – Fq. (Norrlin 1871: *Fqq.) 174 Reports of the Finnish Environment Institute 40 | 2014 Erodium cicutarium (L.) L’HОr. – R. (NШrrХТЧ 1871: V. GЮЛК.) Geranium palustre L. – Rr: B. KХТЦ. КrОК (HЮХЭцЧ 1971); RОМСФК (2012 Kravchenko). a Geranium pratense L. – OЧХв ШХН rОМШrНs: SСЮЧРК (NШrrХТЧ 1871). Geranium sylvaticum L. – Fq. (Norrlin 1871: Fqq.) a Impatiens glandulifera Royle – R: ПОа rОМШrНs sТЧМО 2010. Impatiens nolТ-tangere L. – Rr: Putkozerka River (1999 Butskih, Kryshen & Timofeeva); Unitsa (2012 Rudkovskaya). Polygala amarella Crantz – R. a *Polygala comosa SМСФЮСr. – Rr. TШХЯЮвК (1993 Kauhanen PTГ; IЯКЧЭОr & KЮгЧОЭsШЯ 1995). – RDB EF: 1, RDB RK: 3 (VU) Chamaepericlymenum suecicum (L.) AsМС. & GrКОЛЧ. (Cornus suecica L.) – Rr: Lelikozero (1995 Kuznetsov). Aegopodium podagraria L. – Fq. (Norrlin 1871: Fq in Shunga.) a Anethum graveolens L. – Rr: V. GЮЛК (2010 Kravchenko); TШХЯЮвК (2011 Timofeeva); PШХвК (2013 Kravchenko). Angelica sylvestris L. – Fq. (Norrlin 1871: Fq.) Anthriscus sylvestris (L.) HШППЦ. – Fq. (Norrlin 1871: Fq ТЧ V. GЮЛК.) a Carum carvi L. – Fq. (Norrlin 1871: Fqq.) a Chaerophyllum aromaticum L. – Fq КЧН КЛЮЧНКЧЭ ТЧ KТгСТ SФОrrТОs (ШПЭОЧ НШЦТЧКЭОs ТЧ КЛКЧНШЧОН iОХНs): V. NТЯК – CСОХШгОrШ (1999 Butskih, Kryshen & Timofeeva); TШХЯЮвК (HЮХЭцЧ 1971); KЮгКrКЧНК (1988 Kravchenko; KrКЯМСОЧФШ ОЭ КХ. 2000 К); V. GЮЛК (2010 Kravchenko). – RDB EF: 3 a Chaerophyllum prescottii DC. – OЧХв ШХН rОМШrНs: KТгСТ IsХ. (HЮХЭцЧ 1971). Cicuta virosa L. – Fq. (Norrlin 1871: Fq.) Conioselinum tataricum HШППЦ. – Rr, only old records: Unitsa (Norrlin 1871: Rr SТЦЦТЧР); Shunga (1952 Ramenskaya & Zaikova). a Conium maculatum L. – Rr: TШХЯЮвК (2011 Timofeeva); SСЮЧРК КЧН LКФСЧШЯШ (ЛШЭС 2012 Kravchenko). a Eryngium planum L. – OЧХв ШХН rОМШrНs: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946). Heracleum sibiricum L. – Fq. (Norrlin 1871: *Fq–fqq.) a Heracleum sosnowskyi MКЧНОЧ. – Str, ЦКТЧХв ТЧ ЧШrЭСОrЧ ЩКrЭ, КХsШ V. GЮЛК. a Pastinaca sativa L. – Rr: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); SСЮЧРК (2012 Timofeeva). Pimpinella saxifraga L. – Fq. (Norrlin 1871: *Fq.) Sium latifolium L. – R: FОНШЭШЯШ КЧН OвКЭШЯsЭМСТЧК (BОгКТs 1911); V. GЮЛК (2010 Kravchenko). (Norrlin 1871: Fq ТЧ V. GЮЛК.) Thyselium palustre (L.) Raf. (Peucedanum palustre (L.) MШОЧМС). – Fq. (Norrlin 1871: *Fq.) a HТppopСaё rСamnoТdes L. – Rr: TШХЯЮвК (2011 Timofeeva). Frangula alnus Mill. (Rhamnus frangula L.) – Fq. (Norrlin 1871: *Fq.) Galium album Mill. – Fq. (Norrlin 1871: *Fqq, as Galium mollugo L.) Galium boreale L. – Fq. (Norrlin 1871: Fq in Shunga.) Galium elongatum C. Presl (G. palustre L. sЮЛsЩ. elongatum (C. Presl) Lange) – Rr: Lipovitsy КЧН PШХвК (ЛШЭС 2013 Kravchenko). *,** Galium odoratum (L.) SМШЩ. – Rr: B. Klim. (1996 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); B. Lelik. (2004 Kravchenko, Piirainen, Uotila; KrКЯМСОЧФШ 2007); TКЦЛТЭsв (2013 Polevoy PTГ; 2013 Syrjänen). OЮЭsТНО ГКШЧОгСвО ЭСО sЩОМТОs Тs ФЧШаЧ ПrШЦ KКrОХТК, аОsЭ ШП LКФО OЧОРК, ПrШЦ ХОss ЭСКЧ ЭОЧ ХШМКХТЭТОs. – RDB EF: 3, RDB RK: 3 (NT) Galium palustre L. – Fq. (Norrlin 1871: *Fq–fqq.) a Galium ruthenicum АТХХН. – OЧХв ШХН rОМШrНs: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946). Galium trТidum L. – Str. (Norrlin 1871: Fq ТЧ V. GЮЛК.) – RDB EF: 4 **Galium trТlorum Michaux – Str. Galium uliginosum L. – Fq. (Norrlin 1871: *Fqq.) a Galium vaillantii DC. – Str. (Norrlin 1871: *Fq.) a a Reports of the Finnish Environment Institute 40 | 2014 175 Gentianella amarella (L.) BörЧОr – Rr: TШХЯЮвК (1888 KТСХЦКЧ); V. GЮЛК, TКЦЛТЭsв – Kaskoselga (2013 Syrjänen). (NШrrХТЧ 1871: sОО ЛОХШа.) – RDB EF: 4 Gentianella lingulata (C. Agardh) N. M. Pritch. (G. amarella var. lingulata (C. Agardh) KКrХssШЧ) – Stfq. ДNШrrХТЧ (1871) ЭrОКЭОН G. amarella collectively and included f. lingulata; ЭСО ПrОqЮОЧМв ПШr МШХХОМЭТЯО G. amarella is fqЖ. – RDB EF: 3 Menyanthes trifoliata L. – Fq. (Norrlin 1871: Fq). a Sambucus racemosa L. – Rr: VОРШrЮФsК (2013 Kravchenko); LКЦЛКsrЮМСОТ (2013 Timofeeva). **Viburnum opulus L. – Fq. (Norrlin 1871: Fq.) Linnaea borealis L. – Fq. Lonicera pallasii LОНОЛ. (L. caerulea L.) – Stfq. (Norrlin 1871: Fq.) **Lonicera xylosteum L. – Fq. (Norrlin 1871: Soslanovnavolok, Shunga.) Adoxa moschatellina L. – Str. Knautia arvensis (L.) CШЮХЭ. – Fq. (Norrlin 1871: *Fqq). a Calystegia sepium (L.) R. Br. – Rr: V. GЮЛК (2010 Kravchenko); KКгСЦК (2012 Kravchenko). a Calystegia spectabilis (BrЮЦЦТЭЭ) TгЯОХОЯ (C. sepium sЮЛsЩ. spectabilis BrЮЦЦТЭЭ) – Rr: V. GЮЛК (2010 Kravchenko). a Convolvulus arvensis L. – R: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); VОРШrЮФsК (1989 Kravchenko); B. KХТЦ., PОЭrв (1998 Kashtanov), Longasy (1999 Kravchenko & Kashtanov) КЧН VШrШЛ’Т (2007 Kravchenko); V. GЮЛК (2010 Kravchenko). Cuscuta europaea L. – Str. (NШrrХТЧ 1871: V. GЮЛК.) *Polemonium boreale AНКЦs. – Rr: Azhepnavolok (1870 Norrlin; NШrrХТЧ 1871; 1888 KТСlman; 1888 Günther LE; 1896 Poppius; 1907 Bezays & Verdi LE; 1942 Sparre H; SЩКrrО 1945; 1997 Kashtanov; 2001 Kuznetsova PTГ); SСЮЧРК (1979 RШЧФШЧОЧ, ШЛs.; KrКЯМСОЧФШ ОЭ КХ. 2000 К); PКНЦШгОrШ (1870 Norrlin; NШrrХТЧ 1871; 1875 Günther H; 1942 Kalela H; 1999 Kuznetsov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). Polemonium onegense KХШФ. аКs НОsМrТЛОН ШЧ ЭСО ЛКsТs ШП ЭСО ЦКЭОrТКХ МШХХОМЭОН ПrШЦ AгСОЩЧКЯШХШФ Лв BОгКвs КЧН VОrНТ ТЧ 1907 (KХШФШЯ 1955). – RDB EF: 3, RDB RK: 3 (VU) Polemonium caeruleum L. – Stfq. a Buglossoides arvensis (L.) I. M. JШСЧsЭ. (Lithospermum arvense L.) – OЧХв ШХН rОМШrНs: ОЯОrваСОrО (KШrШХОЯК 1927–1928); TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946). (NШrrХТЧ 1871: *Fq). a Cynoglossum oficТnale L. – OЧХв ШХН rОМШrНs: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946), SСЮЧРК (HЮХЭцЧ 1971). a Echium vulgare L. – Rr: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); B. KХТЦ. (1999 Kravchenko & Kashtanov). a Lappula squarrosa (RОЭг.) DЮЦШrЭ – OЧХв ШХН rОМШrНs: TШХЯЮвК (KШrШХОЯК 1927–1928). a Lycopsis arvensis L. (Anchusa arvensis (L.) M. BТОЛ.) – Rr: TШХЯЮвК КЧН KХТЦ NШs, SСТЭТФТ (FКРОrsЭröЦ & LЮЭСОr 1946); VОРШrЮФsК (1989 Kravchenko); B. KХТЦ., LШЧРКsв КЧН PОЭrв (1999 Kravchenko & Kashtanov). a Myosotis arvensis (L.) HТХХ – Fq. (Norrlin 1871: *Stfq–fq.) Myosotis caespitosa Schultz (M. laxa sЮЛsЩ. caespitosa (SМСЮХЭг) NШrНС.) – Str. (Norrlin 1871: *Fq). Myosotis palustris (L.) L. (M. scorpioides L.) – Fq. (Norrlin 1871: *Fq.) a Myosotis sparsТlora J. G. MТФКЧ Об PШСХ – Rr: Ladmozero (2012 Kravchenko). Myosotis stricta Link ex Roem. & Schult. – R. a Nonea rossica Steven (Nonea pulla DC.) – OЧХв ШХН rОМШrНs: AгСОЩЧКЯШХШФ (SЩКrrО 1945). Pulmonaria obscura DЮЦШrЭ. – Rr: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.; HЮХЭцЧ 1971). a Symphytum caucasicum M. BТОЛ. – Rr: KТгСТ IsХ. (2011 Timofeeva); RОМСФК (2012 Kravchenko); LКЦЛКsrЮМСОТ (2013 Timofeeva). a Symphytum asperum L. – Rr: FШТЦШРЮЛК (2013 Timofeeva). Acinos arvensis (Schur) Dandy (Satureja acinos (L.) SМСООХО) – Str. (Norrlin 1871: Padmozero.) Clinopodium vulgare L. – Fq. *Dracocephalum ruyschiana L. – R, mainly in Kizhi Skerries: Kosmozero (1896 Poppius); B. KХТЦ., SОЧЧКвК GЮЛК (1898 Cajander & Lindroth), Pervye Garnitsy (1998 Kashtanov; 176 Reports of the Finnish Environment Institute 40 | 2014 1998 Potakhin PTГ) КЧН GrвгЧКЯШХШФ CКЩО (1999 Kravchenko & Kashtanov); TШХЯЮвК КЧН SСЮЧРК (HЮХЭцЧ 1971); FШЦТЧШ (1988 KrКЯМСОЧФШ, ШЛs.); RКНФШХвО КЧН RОМСЧШТ IsХОs (1988 Kuznetsov; KЮгЧОЭsШЯ 1993); Grвг IsХ. (1992 Kuznetsov; KЮгЧОЭsШЯ 1993; 1999 Kravchenko & Kashtanov); OrШгС КЧН ВКЦ IsХОs (1998 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); LКЦЛКгЧТФ IsХ. (1999 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); PКХОШsЭrШЯ IsХ. (1999 Kravchenko & Kashtanov, 2004 Kravchenko); B. LОХТФ., RКНФШХ’О CКЩО (2004 Kravchenko, Kuznetsov & Gnatyuk, Piirainen). – RDB RK: 3 (LC→NT) a Dracocephalum tСymТlorum L. – Rr: KТгСТ КrОК (HЮХЭцЧ 1971); MОРШsЭrШЯ IsХ. (2004 Kravchenko). Galeopsis bТida BШОЧЧ. – Fq. a Galeopsis ladanum L. – Rr, the only recent record: Paleostrov (2001 Kuznetsova PTГ). (Norrlin 1871: *Fq.) a Galeopsis speciosa MТХХ. – Fq. (Norrlin 1871: *Fq.) a Galeopsis tetrahit L. – Fq. (Norrlin 1871: *Fq; G. bТida included.) Glechoma hederacea L. – Str, mainly in Kizhi Skerries. (Norrlin 1871: Svyatoinos (Simming, KЮХХСОЦ) КЧН KТгСТ “МШЩТШsО” (GüЧЭСОr).) a Lamium amplexicaule L. – OЧХв ШХН rОМШrНs: SСЮЧРК КЧН PКНЦШгОrШ (NШrrХТЧ 1871). a Lamium confertum Fr. – Rr: Kuzaranda (1888 Kihlman; MОЧЧОЦК 1989; 2004 Kravchenko & Kuznetsov). a Lamium dissectum АТЭС. (L. hybridum VТХХ.) – Str. a Lamium purpureum L. (L. purpureum var. incisum (АТХХН.) PОrs.) – Stfq. (Norrlin 1871: Fq.) a Leonurus villosus Desf. ex d’Urv. (L. cardiaca L. sЮЛsЩ. villosus (DОsП. Об Н’UrЯ.) HвХ.) – Rr: TШХЯЮвК (2011 Timofeeva); TТЩТЧТЭsв (2013 Timofeeva). Lycopus europaeus L. – Fq. (Norrlin 1871: Shunga.) Mentha arvensis L. – Fq. (Norrlin 1871: *Fq.) a Mentha × dalmatica TКЮsМС – Rr: V. GЮЛК (2010 Kravchenko); SСЮЧРК (2012 Kravchenko). a Mentha longifolia (L.) HЮНs. – Rr: V. GЮЛК (2010 Kravchenko). *Origanum vulgare L. – R, ЦКТЧХв ТЧ KТгСТ SФОrrТОs: B. KХТЦ., SОЧЧКвК GЮЛК (1898 Cajander & Lindroth; CКУКЧНОr & LТЧНrШЭС 1900), GrвгЧКЯШХШФ CКЩО, KШsОХРК КЧН PОЭrв (КХХ 1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); RКНФШХвО IsХ. (1898 Cajander & Lindroth; 1988 Kuznetsov; KЮгЧОЭsШЯ 1993; 1998 Kashtanov); PКХОШsЭrШЯ IsХ. (1979 Ronkonen PTГ; 1999 Kravchenko& Kashtanov); RОМСЧШТ IsХ. (1988 Khokhlova PTГ); OrШгС IsХ. (1998 Kashtanov; 1999 Kravchenko & Kashtanov); Grвг IsХ. (1999 Kravchenko & Kashtanov); KКХРШЯ, KШЧОЯ, LКЦЛКгЧТФ, RШРШsЭrШЯ КЧН BЮФШХЧТФШЯsФТв IsХОs (КХХ ТЧ 1999 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); ВЮгСЧвТ OХОЧТв IsХ. (1988 Kuznetsov; 1999 Kravchenko & Kashtanov; 2004 Gnatyuk & Kryshen). – RDB EF: 3, RDB RK: 3 (LC→NT) Prunella vulgaris L. – Fq. (Norrlin 1871: *Fq.) Scutellaria galericulata L. – Fq. (Norrlin 1871: *Fq.) Stachys palustris L. – Fq. (Norrlin 1871: Fq, Unitsa.) Stachys sylvatica L. – R. Thymus serpyllum L. – Str. (Norrlin 1871: Fq in Shunga.) *Thymus subarcticus KХШФ. ОЭ SСШsЭ. – Rr: B. Lelik., Radkol’e Cape (1988 Kuznetsov; Kuznetsov 1993, 1997). – RDB EF: 2, RDB RK: 3 (LC→NT) Callitriche cophocarpa Sendtn. – Rr: B. Klim., Petry (1999 Kravchenko & Kashtanov); SСТХЭвК – PЮЭФШгОrФК RТЯОr (1999 Timofeeva & Rudkovskaya); LКНЦШгОrШ (2012 Kravchenko). Callitriche hermaphroditica L. – Rr: UЧТЭsК (HЮХЭцЧ 1971); SСЮЧРК – PЮЭФШгОrШ (HЮХЭцЧ 1971; 1952 Ramenskaya & Zaikova PГV & PTГ; 2012 Kravchenko); B. KХТЦ., GКrЧТЭsФКвК GЮЛК Bay and Longasy (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); V. GЮЛК (1999 Timofeeva & Rudkovskaya; 2010 Kravchenko); KКгСЦК (2012 Kravchenko). – RDB EF: 3 Callitriche palustris L. – Fq. (Norrlin 1871: *Fq?) a Hyoscyamus niger L. – OЧХв ШХН rОМШrНs: PКХОШsЭrШЯ (GüЧЭСОr 1880; KШrШХОЯК 1927–1928); TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946). a Lycopersicon esculentum Mill. – Rr: V. GЮЛК (2010 Kravchenko); KТгСТ IsХ. (2011 Timofeeva). Reports of the Finnish Environment Institute 40 | 2014 177 Solanum dulcamara L. – Str: mainly Kizhi Skerries. a Solanum tuberosum L. – Rr: V. GЮЛК (2010 Kravchenko). Euphrasia brevipila Burn. & Gremli (E. sricta J. F. LОСЦ. ЯКr. stricta) – Fq. Euphrasia hirtella auct. (E. rostkoviana HКвЧО sЮЛsЩ. fennica (KТСХЦ.) KКrХssШЧ) – Str. EupСrasТa oficТnalТs L. s. ХКЭ. – Rr: V. NТЯК (1999 Timofeeva & Rudkovskaya). (Norrlin 1871: *Fq–fqq.) Euphrasia onegensis A. CКУКЧНОr – ?Rr: TШХЯЮвК (sвЧЭвЩЮs ТЧ H). EupСrasТa parvТlora JЮг. (E. nemorosa (PОrs.) АКХХr.) – Stfq. Euphrasia vernalis List (E. stricta J. P. АШХПП Об J. F. LОСЦ. ЯКr. tenuis (BrОЧЧОr) JКХКs) – Str. Limosella aquatica L. –R: V. NТЯК (HЮХЭцЧ 1971); KТгСТ КrОК (HЮХЭцЧ 1971); KКгСЦК (2012 Kravchenko). (NШrrХТЧ 1871: V. GЮЛК.) – RDB EF: 4 Linaria vulgaris Mill. – Fq. (Norrlin 1871: Stfq.) * Melampyrum cristatum L. – OЧХв ШХН rОМШrНs: ЛОЭаООЧ KЮгКrКЧНК КЧН PКНЦШгОrШ (1874 Günther H; HЮХЭцЧ 1971). – RDB EF: 3, RDB RK: 2 (EN) Melampyrum nemorosum L. – Str. Melampyrum pratense L. – Fq. (Norrlin 1871: Fq.) Melampyrum sylvaticum L. – Fq. (Norrlin 1871: *Fqq.) a Odontites vulgaris Moench – Str. (Norrlin 1871: Fq in Shunga.) Pedicularis palustris L. – Fq. (Norrlin 1871: *Fqq.) Pseudolysimachion longifolium (L.) Opiz (Veronica longifolia L.) – Fq. (Norrlin 1871: Fq.) Pseudolysimachion maritimum (L.) Á. LöЯО &. D. LöЯО (Veronica longifolia var. maritima (L.) HКrЭЦ. – Rr: B. Klim. and Paleostrov (Kravchenko 2007). *Pseudolysimachion spicatum (L.) Opiz (Veronica spicata L.) – R: Kosmozero (1896 Poppius); B. KХТЦ., SОЧЧКвК GЮЛК (1898 Cajander & Lindroth; CКУКЧНОr & LТЧНrШЭС 1900); B. ГКrОЯШ КЧН PШвКХТЭsТЧsФКвК (ЛШЭС 1943 Fagerström H; FКРОrsЭröЦ & LЮЭСОr 1946); TОХЩШгОro (1952 Ramenskaya & Zaykova); FШЦТЧШ (1988 KrКЯМСОЧФШ, ШЛs.); ГТЦЧвКв MЭ. (1988 Kravchenko); SЯвКЭЮСК BКв (1999 Butskih, Kryshen & Timofeeva; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3, RDB RK: 3 (NT) Rhinanthus minor L. – Fq. (Norrlin 1871: *Fqq.) Rhinanthus serotinus (SМСöЧС.) OЛШrЧý – Fq. (Norrlin 1871: Fqq.) Scrophularia nodosa L. – Str. (NШrrХТЧ 1871: SСЮЧРК, V. GЮЛК.) a Verbascum nigrum L. – Str. (NШrrХТЧ 1871: ЛОЭаООЧ V. GЮЛК КЧН KШsЦШгОrШ, fq ТЧ V. GЮЛК.) Verbascum thapsus L. – Str. Veronica arvensis L. – Str. Veronica chamaedrys L. – Fq. (Norrlin 1871: *Fqq.) VeronТca oficТnalТs L. – Fq. (Norrlin 1871: *Fq.) a Veronica persica Poir. – Rr: V. GЮЛК (2010 Kravchenko). Veronica scutellata L. – Str. (NШrrХТЧ 1871: V. GЮЛК; SСЮЧРК (Кs ЯКr. villosa L.) Veronica serpyllifolia L. – Fq. (Norrlin 1871: *Fqq.) Veronica verna L. – Str. (Norrlin 1871: Fq.) *LТttorella unТlora (L.) Asch. – Rr: VОРШrЮФsК (2013 Kravchenko). – RDB RF: 2, RDB EF: 2, RDB RK: 2 (EN) Plantago lanceolata L. – Stfq: ОsЩОМТКХХв ТЧ KТгСТ SФОrrТОs. (NШrrХТЧ 1871: KТгСТ IsХ. (GüЧЭСОr).) Plantago major L. – Fq. (Norrlin 1871: *Fqq.) Plantago media L. – Str. (NШrrХТЧ 1871: TШХЯЮвК.) Pinguicula vulgaris L. – Str. (Norrlin 1871: Fq in the north.) Utricularia intermedia HКвЧО – Str. (Norrlin 1871: Fq.) Utricularia minor L. – R. Utricularia vulgaris L. – Stfq (Norrlin 1871: Stfq.) Hippuris vulgaris L. – Str. (Norrlin 1871: Shunga.) Campanula cervicaria L. – R: B. KХТЦ., KЮгЧОЭsв; KКХРШsЭrШЯ IsХ.; KЮгКrКЧНК КЧН TОХвКЭЧТФШЯШ (КХХ BОгКвs 1911); V. GЮЛК (1942/1943 KЮУКХК, ШЛs.); PОrРЮЛК КrОК КЧН V. GЮЛК (HЮХЭцЧ 1971); B. KХТЦ., MОНЯОгСТК GШrК (1997 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); ВЮгСЧвТ OХОЧТв 178 Reports of the Finnish Environment Institute 40 | 2014 (2004 PТТrКТЧОЧ, ШЛs.); LТsТЭsТЧШ (2004 PТТrКТЧОЧ, ШЛs.). (NШrrХТЧ 1871: DТКЧШЯК GШrК.) – RDB EF: 3, RDB RK: 3 (LC→NT) Campanula glomerata L. – Fq. (Norrlin 1871: Fq.) *,**Campanula latifolia L. – R: TТЩТЧТЭsв, VКrЧКЯШХШФ (2004 Kravchenko); OвКЭОЯsЭМСТЧК (2011 escaped Timofeeva & Nikolaeva PTГ; TТЦШПООЯК & NТФШХКОЯК 2012); LТЩШЯТЭsв, TКЦЛТЭsв КЧН TТЩТЧТЭsв (2013 SвrУтЧОЧ, ШЛs.). – RDB EF: 4, RDB RK: 3 (LC→NT) Campanula patula L. – Fq. (Norrlin 1871: *Fq–fqq.) Campanula persicifolia L. – Stfq. (Norrlin 1871: Fq.) Campanula rapunculoides L. – Stfq. (Norrlin 1871: Fq.) Campanula rotundifolia L. – Fq. (Norrlin 1871: Fq.) *Lobelia dortmanna L. – Stfq, ОsЩОМТКХХв ТЧ KТгСТ SФОrrТОs. SЩОМТОs Тs ФЧШаЧ ПrШЦ МК 25 localities. (Norrlin 1871: P.) – RDB RF: 3, RDB RK: 3 (LC→NT) Achillea millefolium L. – Fq. (Norrlin 1871: *Fqq.) a Achillea nobilis L. – Rr: PrвКХТМСТЧsФКвК (FКРОrsЭröЦ & LЮЭСОr 1946); V. GЮЛК (RКЦОЧsФКвК 1983, ЧШ ЯШЮМСОrs КЯКТХКЛХО) Antennaria dioica (L.) GКОrЭЧ. – Fq. (Norrlin 1871: *Fqq.) a Anthemis arvensis L. – R. (NШrrХТЧ 1871: V. GЮЛК.) a Anthemis tinctoria L. – OЧХв ШХН rОМШrНs: V. GЮЛК (NШrrХТЧ 1871); OвКЭОЯsЭМСТЧК (BОгКТs 1911); KТгС IsХ., TШХЯЮвК КЧН V. GЮЛК (FКРОrsЭröЦ & LЮЭСОr 1946). a Arctium minus (HТХХ) BОrЧС. – Rr: V. GЮЛК (2010 Kravchenko). (Norrlin 1871: Shunga, stfq ТЧ V. GЮЛК.) a Arctium tomentosum MТХХ. – Stfq. (Norrlin 1871: Stfq in Shunga.) a Artemisia absinthium L. – Rr: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); V. GЮЛК (2010 Kravchenko). a Artemisia rupestris L. – OЧХв ШХН rОМШrНs: SСЮЧРК (FКРОrsЭröЦ & LЮЭСОr 1946). a Artemisia vulgaris L. – Stfq. (NШrrХТЧ 1871: V. GЮЛК КЧН fq ТЧ TШХЯЮвК.) a Aster novТ-belgТТ L. – Rr: V. GЮЛК (2010 Kravchenko). a Aster salignus АТХХН. – Rr: V. GЮЛК (2010 Kravchenko). Bidens cernua L. – Str: mainly in Kizhi Skerries. (Norrlin 1871: Fq ТЧ V. GЮЛК.) Bidens radiata TСЮТХХ. – R. Bidens tripartita L. – Fq. (Norrlin 1871: Fq.) a Calendula oficТnalТs L. – Rr: Kazhma (2012 Kravchenko). a Carduus crispus L. – Str. (Norrlin 1871: Fq.) Centaurea jacea L. – Fq. (Norrlin 1871: Fqq in Shunga.) Centaurea phrygia L. – Fq. (Norrlin 1871: Fq–fqq.) Centaurea scabiosa L. – Stfq. (Norrlin 1871: Fq.) a Cichorium intybus L. – OЧХв ШХН rОМШrНs: SСЮЧРК КЧН V. GЮЛК (FКРОrsЭröЦ & LЮЭСОr 1946). a Cirsium arvense L. (C. arvense var. arvense) – Rr: V. GЮЛК (2010 Kravchenko). Cirsium heterophyllum (L.) HТХХ. – Fq. (Norrlin 1871: *Fq.) Cirsium oleraceum (L.) SМШЩ. – Str. Cirsium palustre (L.) SМШЩ.– Stfq. (Norrlin 1871: *Fq.) a Cirsium setosum (АТХХН.) BОssОr (C. arvense var. mite (АТЦЦ. & GrКЛ.) LКЧРО) – Fq. (Norrlin 1871: *Fqq; Кs Cirsium arvense L. s. lat.) a Cirsium vulgare (SКЯТ) TОЧ. – P. (Norrlin 1871: Shunga and fq ТЧ V. GЮЛК.) a Conyza canadensis (L.) CrШЧq. (Erigeron canadensis L.) – Rr: V. GЮЛК (2010 Kravchenko); Kazhma (2012 Kravchenko). Crepis biennis L. – Str: irsЭ rОМШrНОН ПrШЦ TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); rОМОЧЭ rОМШrНs ПrШЦ МК. 15 ЩХКМОs ТЧ ЦОКНШаs, rШКНsТНОs, iОХНs КЧН sСШrОs. – RDB EF: 4 Crepis paludosa (L.) MШОЧМС – P. (NШrrХТЧ 1871: V. GЮЛК.) Crepis tectorum L. – R. (Norrlin 1871: *Fq.) a Cyanus segetum (L.) HТХХ (Centaurea cyanus L.) – R. (Norrlin 1871: *Fq.) Erigeron acris L. – Fq. (Norrlin 1871: *Fq.) Erigeron uralensis Less. (E. acris sЮЛsЩ. brachycephalus (H. LТЧНЛ.) HТТЭШЧОЧ) – Str. Reports of the Finnish Environment Institute 40 | 2014 179 *Eupatorium cannabinum L. – Str: KТгСТ IsХ. КЧН SОЧЧКвК GЮЛК (ЛШЭС ТЧ 1898 Cajander & Lindroth; CКУКЧНОr & LТЧНrШЭС 1900) КЧН МК. 25 rОМОЧЭ rОМШrНs, ЦКТЧХв ПrШЦ KТгСТ SФОrrТОs. – RDB EF: 3, RDB RK: 3 (LC→NT) Gnaphalium uliginosum L. – Fq. (Norrlin 1871: *Fq.) a Helianthus tuberosus L. – Rr: V. NТЯК (2011 Timofeeva); SСЮЧРК (2012 Kravchenko). HТeracТum caesТТlorum AХЦq. Об NШrrХ. (H. subcaesium КЮМЭ.) – PКХОШsЭrШЯ (2004 Uotila); Kizhi (1898 Liro & Cajander). Hieracium chlorelliceps NШrrХ. Об оФsТЩ – SОЧЧКвК GЮЛК (1898 Liro & Cajander). Hieracium coronarium Brenner (H. adunans NШrrХ.) – KТгСТ (1898 Liro & Cajander). Hieracium diaphanoides LТЧНОЛ. – B. LОХТФ., RКНФШХ’О (2004 Uotila). Hieracium distendens Brenner (H. fenno-orbТcans NШrrХ.) – SОЧЧКвК GЮЛК (1898 Liro & Cajander). Hieracium incurrens NШrrХ. – B. LОХТФ., RКНФШХ’О (2004 Uotila). Hieracium karelorum (Norrl.) Norrl. (H. multiglandulosum оФsТЩ; H. prenanthoides auct.) – Str. VКrЧКЯШХШФ (2004 Kravchenko & Piirainen); B. KХТЦ., OЛШгОrШ (1999 Kravchenko & Kashtanov); ЩrШЛКЛХв КХsШ ПrШЦ UгФКвК SКХЦК (2013 Kravchenko), Uimy isles (1986 Khokhlova), ЦКТЧХКЧН Лв KКХРШЯ IsХ. (1986 Kuznetsov), Klimenitsy (2004 Kravchenko), VШrШЛ’Т (2007 Kravchenko). TСОrО КrО ЦШrО, вОЭ ЮЧНОsМrТЛОН ЭКбК ШП H. sect. Prenanthoidea KШМС, аСТМС are found in Azhepnavolok (1870 Norrlin) and Shunga (Norrlin 1871, as H. prenanthoides) and Nizhnee Myagrozero (2002 Kravchenko). Hieracium laeticolor (AХЦq.) LöЧЧr. (H. prolixiforme NШrrХ.) – KТгСТ (1898 Liro & Cajander); SОЧЧКвК GЮЛК (1898 Liro & Cajander); PКХОШsЭrШЯ (2004 Uotila). Hieracium oistophyllum Pugsl. (H. sagittatum (LТЧНОЛ.) NШrrХ.) – LКФО KШsЦШгОrШ (1996 Poppius). Hieracium pruiniferum (NШrrХ.) NШrrХ. – B. KХТЦ. (1997 Kashtanov). Hieracium ravidum Brenner (H. galbanum (DКСХsЭ.) BrОЧЧОr) – KТгСТ (1898 Liro & Cajander); SОЧЧКвК GЮЛК (1898 Liro & Cajander); PКХОШsЭrШЯ (2004 Uotila). Hieracium sagittipotens NШrrХ. – SОЧЧКвК GЮЛК (1898 Liro & Cajander). Hieracium tenuiglandulosum NШrrХ. – B. LОХТФ. (2001 Kuznetsova PTГ). Hieracium umbellatum L. – Fqq. (Norrlin 1871: *Fqq.) a Inula britannica L. – OЧХв ШХН rОМШrНs: PrвКХТМСТЧsФКвК (FКРОrsЭröЦ & LЮЭСОr 1946). Inula salicina L. – Rr: Ladmozero (2012 Kravchenko). – RDB EF: 3 a Lapsana communis L. – R. (Norrlin 1871: *Stfq–fq.) Leontodon autumnalis L. – Fq. (Norrlin 1871: *Fq–fqq.) Leontodon hispidus L. – Str. (NШrrХТЧ 1871: BОЭаООЧ TШХЯЮвК КЧН V. GЮЛК.) a Lepidotheca suaveolens (Pursh) Nutt. (Matricaria discoidea DC., M. matricarioides КЮМЭ.) – Fq. Leucanthemum ircutianum TЮrМг. Об DC. (L. vulgare L.) – Fq. (Norrlin 1871: *Fqq.) Ligularia sibirica (L.) CКss. – R. (Norrlin 1871: Unitsa (Simming).) a Logia arvensТs (L.) HШХЮЛ (Filago arvensis L.) – Rr: V. GЮЛК (2010 Kravchenko). a Matricaria recutita L. (M. chamomilla L.) – Rr: V. GЮЛК (2010 Kravchenko). Mulgedium sibirum (L.) Cass. ex Less. (Lactuca sibirica (L.) MКбТЦ.) – Str. (Norrlin 1871: Str ТЧ V. GЮЛК.) Omalotheca sylvatica (L.) SМС. BТЩ. & F. А. SМСЮХЭг (Gnaphalium sylvaticum L.) – Fq. (Norrlin 1871: * Fq–fqq.) **Petasites frigidus (L.) Fr. – R: KЮгКrКЧНК (HЮХЭцЧ 1971); LКФО KШЩКЧОЭг (1999 Kravchenko & Kashtanov); RвКЛШЯШ (2010 Kravchenko); VОrФСЧОО MвКРrШгОrШ (2012 Kravchenko); Lipovitsy and Uzkie Salmy (2013 Kravchenko); TТЩТЧТЭsв (2013 SвrУтЧОЧ, ШЛs.). (NШrrХТЧ 1871: SСЮЧРК – TШХЯЮвК.) Picris hieracioides L. – Str. (Norrlin 1871: Str.) Pilosella × cymТlora (NтРОХТ & PОЭОr) S.BrтЮЭ. & GrОЮЭОr (HТeracТum cymТlorum NтРОХТ & PОЭОr; H. conferciens NШrrХ.; P. oficТnarum < P. pubescens) – KТгСТ (1898 Liro & Cajander); SОЧЧКвК GЮЛК (1898 Liro & Cajander). Hieracium conferciens NШrrХ. (1904) аКs НОsМrТЛОН ШЧ ЭСО ЛКsТs ШП ЭСО МТЭОН МШХХОМЭТШЧs ПrШЦ KТгСТ КЧН SОЧЧКвК GЮЛК. 180 Reports of the Finnish Environment Institute 40 | 2014 Pilosella × fallacina (F.А.SМСЮХЭг) F.А.SМСЮХЭг (Hieracium fallacinum F.А.SМСЮХЭг; Pilosella oficТnarum × Pilosella praealta × Pilosella pubescens) – SОЧЧКвК GЮЛК (1898 Liro & Cajander). Pilosella × lagellarТs (АТХХН.) ArЯ.-TШЮЯ. (HТeracТum lagellare АТХХН.; PТlosella oficТnarum > Pilosella onegensis) – SОЧЧКвК GЮЛК (1898 Liro & Cajander); ЩrШЛКЛХв КХsШ KКХРШЯ IsХ. (1986 Kuznetsov). PТlosella lorТbunda (АТЦЦ. & GrКЛ.) Fr. (P. suecica (Fr.) F. SМСЮХЭг & SМС. BТЩ., P. fennica (Norrl.) Norrl., Hieracium lorТbundum АТЦЦ. & GrКЛ., H. suecicum Fr., H. fennicum (NШrrХ.) MОХК) – Stfq: SОЧЧКвК GЮЛК (1898 Liro & Cajander), VШХФШsЭrШЯ IsХ. (1986 Kuznetsov). (Norrlin 1871: *Stfq–fq.) Pilosella × glomerata (FrШОХ.) Fr. (Hieracium glomeratum FrШОХ.; P. pubescens × P. onegensis) – B. KХТЦ. (1997 Kashtanov; 2004 Piirainen); SОЧЧКвК GЮЛК (1898 Liro & Cajander). PТlosella oficТnarum F. SМСЮХЭг & SМС. BТЩ. (Hieracium pilosella L.) – Stfq: Kizhi (1898 Liro & Cajander); SОЧЧКвК GЮЛК (1898 Liro & Cajander); RКНФШХвО IsХ. (1988 Kuznetsov); Pod’elniki (2012 Kravchenko). (Norrlin 1871: *Fq–fqq.) Pilosella onegensis Norrl. (Hieracium onegense (NШrrХ.) NШrrХ.; H. caespitosum КЮМЭ.) – Stfq. NШЭ НШМЮЦОЧЭОН Лв sЩОМТЦОЧs. TСТs sЩОМТОs Тs rКЭСОr МШЦЦШЧ ТЧ Kon (Norrlin 1871: *Stfq; Кs H. caespitosum) ТЧ sЩТЭО ШП ЭСО КЛsОЧМО ШП ЩrОsОrЯОН sЩОМТЦОЧs ПrШЦ ГКШЧОгСТО. Pilosella peleteriana (Mцr.) F. SМСЮХЭг & SМС. BТЩ. (Hieracium peleterianum Mцr.) – Rr: SОЧЧКвК GЮЛК (1898 Liro & Cajander). Pilosella pubescens Norrl. (Hieracium pubescens HОХХsЭr.; H. cymosum auct., H. vaillantii КЮМЭ.) – Stfq: SОЧЧКвК GЮЛК (1898 Liro & Cajander); VШХФШsЭrШЯ (1986 Kuznetsov); KТгСТ (1986 Kuznetsov). (Norrlin 1871: *Fq.) Ptarmica cartilaginea (LОНОЛ. Об RМСЛ.) LОНОЛ. (Achillea salicifolia BОssОr) – Rr: Shunga (Putkozero) (Norrlin 1871, 1979 Ronkonen, 2012 Kravchenko); КХХ rОМШrНs ПrШЦ sСШrОs ШП the same lake. Ptarmica vulgaris HТХХ (Achillea ptarmica L.) – Rr: V. NТЯК (1999 Timofeeva & Rudkovskaya); V. GЮЛК (2010 Kravchenko). Saussurea alpina L. – Rr: FОНШЭШЯШ (BОгКТs 1911); TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); Karasozero (1999 Kuznetsov); TТЩТЧТЭsв – KКsФШsОХРК (2013 Syrjänen). a Senecio vulgaris L. – Str. Solidago virgaurea L. – Fq. (Norrlin 1871: Fq ЛОЭаООЧ V. GЮЛК КЧН VОРШrЮФsК.) a Sonchus arvensis L. – Str. (Norrlin 1871: *Fqq.) a Sonchus asper (L.) HТХХ – R. (NШrrХТЧ 1871: SСЮЧРК КЧН V. GЮЛК.) a Sonchus oleraceus L. – R. (NШrrХТЧ 1871: ТЧ ЭСО аСШХО ГКШЧОгСвО PОЧТЧsЮХК.) Tanacetum vulgare L. – Fq. (Norrlin 1871: Str, ЛЮЭ fq ТЧ V. GЮЛК; UЧТЭsК (KЮХХСОЦ).) Taraxacum oficТnale АТРР. МШХХ. – Fq. (Norrlin 1871: *Fq.) Tripleurospermum inodorum (L.) SМС. BТЩ. – Fq. (Norrlin 1871: *Fqq.) Trommsdorfia maculata (L.) Bernh. (Hypochaeris maculata L.) – Stfq. (NШrrХТЧ 1871: V. GЮЛК.) Tussilago farfara L. – Fq. (Norrlin 1871: *P.) Paris quadrifolia L. – Fq. (Norrlin 1871: Fq ТЧ V. GЮЛК.) Convallaria majalis L. – Fq. (Norrlin 1871: Fq.) Maianthemum bifolium (L.) F. А. SМСЦТНЭ – Fq. (Norrlin 1871: *Fqq.) Polygonatum odoratum (MТХХ.) DrЮМО – Str. (Norrlin 1871: Azhepnavolok and near Shunga.) Allium oleraceum L. – Str: ШЧХв ТЧ KТгСТ SФОrrТОs, irsЭ rОМШrН КЭ KТгСТ IsХ. (1995 Heikkilä PTГ; KЮгЧОЭsШЯ 1997); КХsШ OrШгС IsХ. (1998 Kashtanov); KКХРШЯ IsХ. (1999 Kashtanov); МК. 10 localities after 1997 at B. Klim. Allium schoenoprasum L. – Rr: MвsС’Т IsХОs (1986 Khokhlova PTГ); IгЛЮsСОМСЧвТ IsХ. (1988 Kravchenko); SОЯОrЧвТ MвsСТв IsХ. (1988 Kuznetsov); B. KХТЦ., IХКТЧКЯШХШФ (1997 Kashtanov), Pervye Garnitsy (1998 Kashtanov) and Lukova Bay (2004 Kravchenko, Piirainen, Uotila); B. Lelik. (2001 Kuznetsova). a Asparagus oficТnalТs L. – Rr: Rechka (2012 Kravchenko). Reports of the Finnish Environment Institute 40 | 2014 181 Gagea minima (L.) KОr GКаХ. – Rr: KТгСТ IsХ. (HЮХЭцЧ 1971; 1986 Drozdova; KЮгЧОЭsШЯ 1993; 1998 Kravchenko, 1999 Znamenskiy, 2003 Kravchenko & Kuznetsov); ЛОЭаООЧ TОХТКЭЧТФШЯШ and Zharnikovo (1986 Drozdova; KЮгЧОЭsШЯ 1993); KХТЦ NШs (2001 Shelekhov). Iris pseudacorus L. – Stfq. (NШrrХТЧ 1871: V. GЮЛК.) Coeloglossum viride (L.) HКrЭЦ. – Str: mainly in Kizhi Skerries. (Norrlin 1871: *P–stfq.) CorallorСТza trТida CСсЭОХ. – R. (Norrlin 1871: *Fq.) *,**Cypripedium calceolus L. – R: KЮгКrКЧНК (GüЧЭСОr 1880); ВЮгСЧвТ OХОЧТв IsХ. (1896 Poppius); LКЦЛКsrЮМСОв (HЮХЭцЧ 1971); ГКРШrsФШО LКФО (1952 Ramenskaya & Zaykova). VКЛХШФ IsХ. (1988 Kuznetsov; KЮгЧОЭsШЯ 1993); KКТЧШs IsХ. (KЮгЧОЭsШЯ & KСШФСХШЯК 1994); B. KХТЦ., IХКТЧКЯШХШФ CКЩО (1997 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К) КЧН KЮrРОЧТЭsв (MКrФШЯsФКвК ОЭ КХ. 2007); RОМСЧШТ IsХ. (2004 PТТrКТЧОЧ, ШЛs.); MОРШsЭrШЯ (2004 Kravchenko H, PTГ); TТЩТЧТЭsв (2004 PТТrКТЧОЧ & UШЭТХК, ШЛs., 2013 SвrУтЧОЧ, ШЛs.); KКsФШsОХРК (2013 TТФФКЧОЧ, ШЛs.); TЮrКsЭКЦШгОrШ (2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013). – RDB EF 4, RDB RF 3, RDB RK 3 (LC→NT). *Dactylorhiza cruenta (O. F. MЮОХХ.) SШя (Dactylorhiza incarnata sЮЛsЩ. cruenta (O. F. MüХХ.) Nyman) – Rr, ШЧХв ШХН rОМШrНs: AгСОЩЧКЯШХШФ (SЩКrrО 1945); TШХЯЮвК (HЮХЭцЧ 1971). – RDB EF 3, RDB RK 3 (NT) Dactylorhiza fuchsii (DrЮМО) SШя – Stfq. Dactylorhiza incarnata (L.) SШя – Str. (Norrlin 1871: *Stfq–fq.) Dactylorhiza maculata (L.) SШя – Fq. (Norrlin 1871: *Fq; ТЧМХ. D. fuchsii.) *Dactylorhiza traunsteineri (SКЮЭ. Об RМСЛ.) SШя s. ХКЭ. – R: V. GЮЛК (1896 Poppius, 2013 Kravchenko); LКЦЛКsrЮМСОв (1907 Bezays & Verdi; BОгКвs 1911); UЧТЭsК (HЮХЭцЧ 1971); PЮЭФШгОrШ (1952 RКЦОЧsФКвК, ШЛs.); PКХЭОРК (1999 Butskih, Kryshen & Timofeeva); OвКЭОЯsЭМСТЧК (KЮгЧОЭsШЯ 1993; KЮгЧОЭsШЯ ОЭ КХ. 1999; 2012 Kravchenko); KЮгКrКЧНК, TТЩТЧТЭsв (2004 Kravchenko); B. KХТЦ., SЭМСЮМСТК BКв (MКrФШЯsФКвК ОЭ. КХ. 2007); TЮrКsЭКЦШгОrШ (2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013); PШХвК (2013 Kravchenko). (Norrlin 1871: *Stfq, as var. curvifolia NвХ.) – RDB RF: 3, RDB RK: 3 (LC→NT) Epipactis helleborine (L.) CrКЧЭг – Str. (Norrlin 1871: Unitsa.) *Epipactis palustris (L.) CrКЧЭг – R: AгСОЩЧКЯШХШФ (SЩКrrО 1945; 1997 Kashtanov); TОХpozero (1952 Ramenskaya & Zaykova; 1979 Ronkonen); LКФО ГКРШrsФШО (1952 Ramenskaya & Zaykova); SСЮЧРК (HЮХЭцЧ 1971); PТРЦК MТrО (1980 Elina, Antipin & Kuzmina PTГ; KЮгЧОЭsШЯ ОЭ КХ. 2013); LКФО PКНЦШгОrШ (1986 Kuznetsov); LКЦЛКsrЮМСОв, KКХОРЮЛsФШО Mire (1991 Dyachkova PTГ); LКФО KКrКsШгОrШ (1999 Kuznetsov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); KЮгКrКЧНК (2004 Kravchenko & Kuznetsov, 2004 Piirainen, 2004 Uotila); GТгСШгОrШ (MКrФШЯsФКвК ОЭ КХ. 2007; 2012 Timofeeva; KrКЯМСОЧФШ & TТЦШПООЯК 2013). – RDB EF: 3, RDB RK: 3 (LC→NT) Goodyera repens (L.) R. Br. – R. (Norrlin 1871: Unitsa (Kullhem).) Gymnadenia conopsea (L.) R. Br. – Stfq. (Norrlin 1871: *Fqq.) Hammarbya paludosa (L.) O. KЮЧЭгО – Str. **Listera cordata (L.) R. Br. – Str. (Norrlin 1871: *Fq.) Listera ovata (L.) R. Br. – Stfq. (Norrlin 1871: *Fq–fqq.) *Malaxis monophyllos (L.) Sа. – Str: ЛОЭаООЧ TКrШЯsФКвК КЧН BШРШЦШХШЯsФКвК (FКРОrsЭröЦ & LЮЭСОr 1946); FОНШЭШЯШ (HЮХЭцЧ 1971); TОХвКЭЧТФШЯШ (1987 Stoykina); LТМСФШЯ IsХ. (1998 Kashtanov); PКХОШsЭrШЯ IsХ. (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); SЯвatukha Bay (1999 Butskih, Kryshen & Timofeeva; KrКЯМСОЧФШ ОЭ КХ. 2000 К); KЮгКrКЧНК (2004 Kravchenko & Kuznetsov, Piirainen); SСЮЧОЯsФТв IsХ. (MКrФШЯsФКвК ОЭ. КХ. 2007); V. GЮЛК (2010 Kravchenko); TЮrКsЭКЦШгОrШ (2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013); ЛОЭаООЧ PШН’ОХЧТФТ КЧН ГЮЛШЯШ (2012 Kravchenko); PШХвК (2013 Kravchenko). (Norrlin 1871: *P.) – RDB EF: 2, RDB RK: 3 (LC→NT) *,**NeottТa nТdus-avТs (L.) RТМС. – Str, only in Kizhi Skerries: Boyarstchina and Zharnikovo (ЛШЭС 1986 Drozdova PГV); TОХвКЭЧТФШЯШ, KЮsСЧКЯШХШФ (KЮгЧОЭsШЯ & KСШФСХШЯК 1994); B. Klim., Klimenitsy (1997 Kashtanov), Pervye Garnitsy (1998 Kashtanov), Gryznavolok Cape (1999 Kravchenko & Kashtanov), Koselga (1999 Kravchenko & Kashtanov) КЧН VШrШЛ’Т 182 Reports of the Finnish Environment Institute 40 | 2014 (2007 Kravchenko); Grвг IsХ. (1999 Kravchenko & Kashtanov); MвКХ’ IsХ. (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); ВЮгСЧвТ OХОЧТв IsХ. (2004 Kravchenko); B. LОХТФ., Radkol’e Cape (2004 Kravchenko & Kuznetsov); DШХРТв IsХ. (MКrФШЯsФКвК ОЭ КХ. 2007); TКЦЛТЭsв (2013 Syrjänen); TТЩТЧТЭвs (2013 SвrУтЧОЧ, ШЛs.). – RDB EF: 3, RDB RK: 3 (LC→NT) Platanthera bifolia (L.) RТМС. – Stfq. (Norrlin 1871: *Fq.) Calla palustris L. – Stfq. (Norrlin 1871: Fq.) Lemna minor L. – Stfq. (Norrlin 1871: Shunga and fq ТЧ V. GЮЛК.) Lemna trisulca L. – Str. (NШrrХТЧ 1871: V. GЮЛК КЧН fq in Shunga.) Spirodela polyrhiza (L.) SМСХОТН. – Rr: MОХШТРЮЛК (2013 Timofeeva). Butomus umbellatus L. – Str. AlТsma plantago-aquatТca L. – Fq. (Norrlin 1871: Fq.) Sagittaria × lunata C. D. Preston & Uotila (S. natans × sagittifolia) – Rr: B. Klim., Pervye Garnitsy (1998 Kashtanov) and KЮЦЮsС GЮЛК (1999 Kravchenko & Kashtanov). Sagittaria natans PКХХ. – Rr: Shunga (1896 Poppius); KШsЦШгОrШ, PКНЦШгОrШ КЧН PЮЭФШгОrШ (Shunga) (Klyukina 1965, no vouchers). Sagittaria sagittifolia L. – Str. (Norrlin 1871: Fqq ТЧ V. GЮЛК.) ᵃElodea canadensТs MТМСб. – Str. HydrocСarТs morsus-ranae L. – Str. (NШrrХТЧ 1871: DТКЧШЯК GШrК (SТЦЦТЧР); UЧТЭгК (KЮХХСОЦ); sООЧ ТЧ sОЯОrКХ ХШМКХТЭТОs ТЧ ЭСО аСШХО ГКЧШЧОгСвО PОЧТЧsЮХК.) Stratiotes aloides L. – Str. (Norrlin 1871: Fq ТЧ ЭСО ЧШrЭСОrЧ ЩКrЭ; V. GЮЛК.) Scheuchzeria palustris L. – R. (Norrlin 1871: *Stfq.) Triglochin palustris L. – R. (Norrlin 1871: Fq.) Potamogeton alpinus BКХЛ. – Fq. (Norrlin 1871: *Many localities.) Potamogeton × angustifolius J. PrОsХ (P. gramineus × lucens) – Rr: Regimatka (2012 Kravchenko). Potamogeton berchtoldii FТОЛОr – Str. (Norrlin 1871: *Stfq; Кs P. pusillus L.) Potamogeton compressus L. – R. (Norrlin 1871: Fq in Shunga.) Potamogeton ilТformТs Pers. (StuckenТa ilТformТs (PОrs.) BörЧОr) – Rr: Putkozero (Klyukina 1965); B. KХТЦ., GКrЧТЭsФКвК GЮЛК BКв (1998 Kashtanov; Kravchenko et al. 2000 a). (Norrlin 1871: SСЮЧРК.) – RDB EF: 4 *Potamogeton friesii RЮЩr. – Rr, only old records, all from Lake Putkozero (Shunga) (1888 Kihlman; Kihlman 1888, 1890; 1896 Poppius; KХвЮФТЧК 1965). – RDB EF: 4, RDB RK: 3 (NT) Potamogeton gramineus L. – Fq. (Norrlin 1871: *Fq.) Potamogeton lucens L. – Fq. (Norrlin 1871: Fqq.) Potamogeton natans L. – Fq. (Norrlin 1871: *Fq.) Potamogeton obtusifolius MОrЭ. & А. D. J. KШМС – R. (NШrrХТЧ 1871: SЮsХШЧШЯ NКЯШХШФ КЧН V. GЮЛК.) Potamogeton perfoliatus L. – Fq. (Norrlin 1871: *Fq.) Potamogeton praelongus АЮХПОЧ – Rr: VКХРШЦШгОrШ, LКФОs KШsЦШгОrШ КЧН PЮЭФШгОrШ (KХвЮФТЧК 1965; ЧШ ЯШЮМСОrs); KШЧНШгОrШ (2012 Timofeeva). *Potamogeton rutilus АШХПР. – Rr: only old records, all from Lake Putkozero (Shunga) (1870 Norrlin; NШrrХТЧ 1871 (fq ТЧ SСЮЧРК); 1888 Kihlman; Kihlman 1888, 1890; 1896 Poppius). – RDB EF: 3, RDB RK: 3 (NT) *CaulТnТa lexТlТs АТХХН. (Najas lexТlТs (АТХХН.) RШsЭФ. & А. L. E. SМСЦТНЭ) – Rr: V. GЮЛК (1870 Norrlin; NШrrХТЧ 1871; GüЧЭСОr 1880; 1943 Luther; LЮЭСОr 1945; FКРОrsЭröЦ & LЮЭСОr 1946); KТгСТ IsХ., НrТПЭОН (KЮгЧОЭsШЯ 1993). TСО sОМШЧН rОМШrН ШП Caulinia from Karelia is also from Kon, ПrШЦ LКФО PвКХШгОrШ (LЮЭСОr 1945). – RDB EF: 1. RDB RF: 2, RDB RK: 1 (CR) Sparganium angustifolium MТМСб. – Str. (Norrlin 1871: Shunga.) Sparganium emersum RОСЦКЧЧ – Str. (NШrrХТЧ 1871: V. GЮЛК КЧН fq in Shunga.) Sparganium glomeratum BОЮrХ. – Rr: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.); TШХЯЮвК КЧН V. NТЯК (HЮХЭцЧ 1971); AгСОЩЧКЯШХШФ (1996 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3 Sparganium gramineum GОШrРТ – Rr, ШЧХв ШХН rОМШrНs: KТгСТ КrОК КЧН B. KХТЦ. (HЮХЭцЧ 1971). Reports of the Finnish Environment Institute 40 | 2014 183 Sparganium microcarpum (NОЮЦ.) ČОХКФ. – Rr: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.); KЮгКrКЧНК (HЮХЭцЧ 1971); TШХЯЮвК (1993 Kravchenko); MвКХ’ IsХ. (1999 Kravchenko & Kashtanov). (Norrlin 1871: Shunga, as S. ramosum HЮНs., ЧШЦ. ТХХОР. = S. erectum L., s. lat.) Sparganium natans L. (S. minimum АКХХr.) – Stfq. (Norrlin 1871: Fq.) Typha angustifolia L. – Rr: SСЮЧРК (GüЧЭСОr 1880); V. GЮЛК (GüЧЭСОr 1880; 1999 Timofeeva & Rudkovskaya; 2010 Kravchenko); VОРШrЮФsК (2013 Kravchenko). (Norrlin 1871: Shunga.) Typha latifolia L. – Str: irsЭ rОМШrНs ПrШЦ GКЯШsЭrШЯ IsХ. ТЧ UЧТЭsК BКв (1988 KrКЯМСОЧФШ, ШЛs.) КЧН AгСОЩЧКЯШХШФ (1996 Kashtanov). Juncus alpinoarticulatus CСКТб – Fq. (Norrlin 1871: *Stfq–fq, as J. nodulosus = J. alpinoarticulatus s.lat.) Juncus articulatus L. – Stfq. (Norrlin 1871: *Fq.) Juncus bufonius L. – Str. (Norrlin 1871: *Fq.) Juncus bulbosus L. – Rr: Rechka (2012). Juncus compressus JКМq. – Stfq. (NШrrХТЧ 1871: V. GЮЛК КЧН fq in Shunga.) Juncus conglomeratus L. – R. Juncus effusus L. – Str. Juncus ilТformТs L. – Fq. (Norrlin 1871: *Fqq.) Juncus iscСerТanus TЮrМг. Об V. I. KrОМг. (J. alpinoarticulatus sЮЛsЩ. iscСerТanus TЮrМг. Об V. I. KrОМг.) HтЦОЭ-AСЭТ) – Rr: VШrШЛ’Т (2007 Kravchenko). Juncus minutulus (AХЛОrЭ & JКСКЧН.) PrКТЧ (J. bufonius sЮЛsЩ. minutulus (AХЛОrЭ & JКСКЧН.) SяШ, ЧШЦ. ТХХОР.) – Rr: VКЧМСШгОrШ (2012 Kravchenko). Juncus nodulosus АКСХОЧЛ. (J. alpinoarticulatus sЮЛsЩ. rarТlorus (HКrЭЦ.) HШХЮЛ) – Str. (Norrlin 1871, see under J. alpinoarticulatus.) Juncus ranarius SШЧРОШЧ & E. P. PОrrТОr – Rr: SОЧЧКвК GЮЛК (1898 Liro & Cajander). Juncus stygius L. – Rr. (Norrlin 1871: Unitsa.) Luzula multТlora (EСrС.) LОУ. – Fq. (Norrlin 1871: *Fq.) Luzula pallescens Sа. – Fq. (Norrlin 1871: *Fqq.) Luzula pilosa (L.) АТХХН. – Fq. (Norrlin 1871: *Fqq.) Carex acuta L. – Fq. (Norrlin 1871: *Fq.) Carex appropinquata Schumach. – Rr: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.); B. KХТЦ., KШsОХРК (1999 Kravchenko & Kashtanov); RОМСЧШв IsХ. (2004 Piirainen H, PTГ); LТЩШЯТЭsв, TКЦЛТЭsв КЧН TТЩТЧТЭsв (2013 SвrУтЧОЧ, ШЛs.). Carex aquatilis АКСХОЧЛ. – R: V. GЮЛК КЧН UsЭ’-ВКЧНШЦК (1942/1943 KЮУКХК, ШЛs.); ШЛsОrЯКЭТШЧs ПrШЦ sОЯОrКХ ЩШТЧЭs, ЛЮЭ ЧШ ЯШЮМСОrs. Carex atherodes Spreng. – Rr: Kosmozero (1896 Poppius; HЮХЭцЧ 1971); ОrrШЧОШЮsХв rОЩШrЭОН ПШr KТгСТ IsХ. (KЮгЧОЭsШЯ 1993; sОО KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3 Carex brunnescens (PОrs.) PШТr. – Str. Carex buxbaumii АКСХОЧЛ. – Str. (Norrlin 1871: Shunga.) Carex canescens L. – Fq. (Norrlin 1871: *Fqq.) Carex capillaris L. – R. (Norrlin 1871: B. Klim. (Simming).) Carex cespitosa L. – Fq. (Norrlin 1871: *Fqq.) Carex chordorrhiza L. П. – Stfq. (Norrlin 1871: *Fqq.) Carex diandra SМСrКЧФ – Stfq. (Norrlin 1871: *Fqq.) Carex digitata L. – Stfq. (NШrrХТЧ 1871: V. GЮЛК.) Carex dioica L. – Stfq. (Norrlin 1871: Fqq.) **Carex disperma DОаОв – Str. (Norrlin 1871: *P.) Carex echinata MЮrrКв – Str. (Norrlin 1871: *Fq.) Carex elongata L. – Fq. (Norrlin 1871: *Fq.) Carex ericetorum PШХХТМС – Rr, ШЧХв ШХН rОМШrНs: SСЮЧРК КЧН VОРШrЮФsК (HЮХЭцЧ 1971). Carex lava L. – Fq. (Norrlin 1871: Fqq.) Carex globularis L. – Str. (Norrlin 1871: Fq.) Carex heleonastes L. f. – Rr: Karasozero (1995 Kuznetsov); ЛОЭаООЧ ГСКrЧТФШЯШ КЧН PШН’ОХniki (1996 Kuznetsov; KЮгЧОЭsШЯ 1997; KЮгЧОЭsШЯ ОЭ КХ. 1999); B. KХТЦ., KШsОХРК (1999 184 Reports of the Finnish Environment Institute 40 | 2014 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); TЮrКsЭКЦШгОrШ (2012 Kravchenko). – RDB EF: 4 Carex juncella (Fr.) TС. Fr. (C. nigra sЮЛsЩ. juncella Fr.) – Stfq. (Norrlin 1871: *Fq.) Carex lasiocarpa EСrС. – Fq. (Norrlin 1871: *Fq.) Carex leporina L. – Fq. (Norrlin 1871: *Fq.) Carex limosa L. – Stfq. (Norrlin 1871: *Fqq.) Carex livida (АКСХОЧЛ.) АТХХН. – Rr: Unitsa (1870 Norrlin: NШrrХТЧ 1871); BШвКrsЭМСТЧК (1986 Stoykina; KЮгЧОЭsШЯ 1993; KЮгЧОЭsШЯ ОЭ КХ. 1999); UгФТО (2005 Antipin); OвКЭОЯsЭМСТЧК КЧН TЮrКsЭКЦШгОrШ (ЛШЭС 2012 Kravchenko). **Carex loliacea L. – Str. (Norrlin 1871: *P–stfq.) *Carex muricata L. – Str: V. GЮЛК, UsЭУКЧЧШУО (1943 KЮУКХК, ШЛs.; HЮХЭцЧ 1971; 2012 Kravchenko); ЧЮЦОrШЮs rОМОЧЭ rОМШrНs ПrШЦ KТгСТ SФОrrТОs (KЮгЧОЭsШЯ 1997; ВЮНТЧК 1999; KrКЯМСОЧФШ ОЭ КХ. 2000 К; MШrШгШЯК ОЭ КХ. 2010), КХsШ TТЩТЧТЭsв (2004 Kravchenko & Piirainen H, PTГ). – RDB EF: 3, RDB RK: 3 (LC→NT) Carex nigra (L.) RОТМСКrН. – Fq. (Norrlin 1871: *Fqq.) Carex omskiana Meinsh. (C. elata AХХ. sЮЛsЩ. omskiana (MОТЧsС.) JКХКs) – Str. (Norrlin 1871: V. GЮЛК КЧН fq in Shunga.) Carex pallescens L. – Fq. (Norrlin 1871: *Fq.) Carex panicea L. – Str. (Norrlin 1871: *Fq.) Carex paucТlora LТРСЭП. – Str. (Norrlin 1871: *Fq.) Carex paupercula Michx. (C. magellanica LКЦ. sЮЛsЩ. irrigua (АКСХОЧЛ.) HТТЭШЧОЧ) – Fq. (Norrlin 1871: *Fqq.) Carex pseudocyperus L. – Rr: SСЮЧОЯsФТв IsХ. (2010 DОЦОЧЭТОЯК, ШЛs.: MШrШгШЯК ОЭ КХ. 2010). – RDB RK: 3 (LC→NT) Carex rhynchophysa FТsМС., C. A. MОв. & AЯц-LКХХ. – Str. (Norrlin 1871: *P.) *Carex riparia CЮrЭТs – Rr: TКЦЛТЭsв (2013 SвrУтЧОЧ, ШЛs.); ЯОrв rКrО sЩОМТОs ТЧ KКrОХТК, аСОrО ФЧШаЧ ШЧХв ТЧ 3 ШЭСОr ХШМКХТЭТОs. – RDB EF: 2, RDB RK: 3 (VU) Carex rostrata SЭШФОs – Fq. (Norrlin 1871: *Fqq.) Carex scandinavica E. А. DКЯТОs (C. viridula Michx. var. pulchella (LöЧЧr.) B. SМСЦТН) – Str. – RDB EF: 3 Carex serotina MцrКЭ (C. viridula var. viridula) – P. (Norrlin 1871: Fq ТЧ SСЮЧРК; ТЧМХ. C. scandinavica.) **Carex tenuТlora АКСХОЧЛ. – Rr: VОФСФШгОrШ (2012 Kravchenko). – RDB EF: 3 Carex vaginata TКЮsМС – Stfq. (Norrlin 1871: Stfq–fq.) Carex vesicaria L. – Fq. (Norrlin 1871: *Fq.) Eleocharis acicularis (L.) RШОЦ. & SМСЮХЭ. – P. (Norrlin 1871: *Fq.) Eleocharis mamillata (H. LТЧНЛ.) H. LТЧНЛ. – Rr: TШХЯЮвК КЧН KХТЦ NШs – OФСТsОЯsФКвК (FКРОrsЭröЦ & LЮЭСОr 1946); VШrШЛ’Т (2007 Kravchenko). Eleocharis palustris (L.) R. Br. – Stfq. (Norrlin 1871: *Fq.) EleocСarТs quТnquelora (HКrЭЦКЧЧ) O. SМСаКrг – Str. (Norrlin 1871: Fq in Shunga.) Eleocharis uniglumis (LТЧФ.) SМСЮХЭ. – Rr: SСЮЧРК (HЮХЭцЧ 1971). TСТs Тs ЭСО ШЧХв rОМШrН ПrШЦ LКФО OЧОРК, ЛЮЭ ЭСО sЩОМТОs Тs ФЧШаЧ ПrШЦ LКФО VШНХШгОrШ, ОКsЭ ШП LКФО OЧОРК. Eriophorum angustifolium HШЧМФ. (E. polystachyon L. ЧШЦ. rОУ.) – Stfq. (Norrlin 1871: *Fqq.) Eriophorum gracile А. D. J. KШМС Об RШЭС – Str. (Norrlin 1871: Shunga.) Eriophorum latifolium HШЩЩО – Str. (Norrlin 1871: Shunga, fq ЛОЭаООЧ TШХЯЮвК КЧН V. GЮЛК.) Eriophorum vaginatum L. – Stfq. (Norrlin 1871: *Fqq.) Rhynchospora alba (L.) VКСХ – Str. (NШrrХТЧ 1871: ЛОЭаООЧ KШsЦШгОrШ КЧН V. GЮЛК.) Schoenoplectus lacustris (L.) Palla (Scirpus lacustris L.) – Fq. (Norrlin 1871: Fqq.) Scirpus sylvaticus L. – Fq. (Norrlin 1871: *Stfq–fq.) Trichophorum alpinum (L.) PОrs. – Str. (Norrlin 1871: *Fqq.) Trichophorum cespitosum (L.) HКrЭЦ. – R. Agrostis canina L. – Fq. (Norrlin 1871: *Fqq.) Agrostis capillaris L. (A. tenuis SТЛЭС.). – Fq. (Norrlin 1871: *Fqq.) Reports of the Finnish Environment Institute 40 | 2014 185 Agrostis gigantea Roth – Rr: КММШrНТЧР ЭШ KЮгЧОЭsШЯ (1993) ОЯОrваСОrО ТЧ KТгСТ SФОrrТОs, ЭСО ПrОqЮОЧМв ШЛЯТШЮsХв ШЯОrОsЭТЦКЭОН; V. GЮЛК (2012 Kravchenko). Agrostis stolonifera L. – P. (Norrlin 1871: shores of Lake Onega.) Alopecurus aequalis SШЛШХ. – Fq. (Norrlin 1871: *Fq.) Alopecurus geniculatus L. – Fq. (Norrlin 1871: *Stfq.) a Alopecurus pratensis L. – Fq. Anthoxanthum odoratum L. – Fq. (Norrlin 1871: *Fqq.) a Apera spТca-ventТ (L.) P. BОКЮЯ. – OЧХв ШХН rОМШrНs: *fqq Лв NШrrХТЧ (1871), fq Лв KШrШХОЯК (1927–1928), fqq Лв KЮУКХК (1942/1943, Цs.), stfq–fq Лв FКРОrsЭröЦ & LЮЭСОr (1946). a Avena fatua L. – Rr: V. GЮЛК (1999 Timofeeva & Rudkovskaya). Avenella lexuosa (L.) DrОУОr (DescСampsТa lexuosa (L.) TrТЧ., LercСenfeldТa lexuosa (L.) SМСЮr, ЧШЦ. ТХХОР.) – Fq. (Norrlin 1871: *Fqq.) a Briza media L. – Str. a Bromopsis inermis (LОвss.) HШХЮЛ (Bromus inermis LОвss.) – Str. a Bromus arvensis L. – OЧХв ШХН rОМШrНs: LКЦЦКsЩЮrШ (1943 KЮУКХК, ШЛs.); TШХЯЮвК (FКРОrsЭröЦ & Luther 1946). a Bromus secalinus L. – OЧХв ШХН rОМШrНs: SОЧЧКвК GЮЛК (BОгКТs 1911); TШХЯЮвК КЧН KХТЦ NШs (FКРОrsЭröЦ & LЮЭСОr 1946). Calamagrostis arundinacea (L.) Roth – Fq. (NШrrХТЧ 1871: V. GЮЛК.) Calamagrostis canescens (АОЛОr) RШЭС – Fq. (Norrlin 1871: *Fq–fqq.) Calamagrostis epigeios (L.) RШЭС – Fq. (Norrlin 1871: Fqq.) Calamagrostis meinshausenii (TгЯОХОЯ) VТХУКsШШ (C. ОЩТРОТШs sЮЛsЩ. meinshausenii TгЯОХОЯ) – Rr: Megostrov (2004 Kravchenko); V. GЮЛК (2010 Kravchenko). Calamagrostis neglecta (EСrС.) G. GКОrЭЧ., B. MОв. & SМСОrЛ. – Fq. (Norrlin 1871: Fqq.) Calamagrostis phragmitoides HКrЭЦ. (C. purpurea (TrТЧ.) TrТЧ. sЮЛsЩ. phragmitoides (C. HКrЭЦ.) TгЯОХ.) – Fq. (NШrrХТЧ 1871: V. GЮЛК.) a Dactylis glomerata L. – Fq. (Norrlin 1871: Fq ТЧ SСЮЧРК КЧН V. GЮЛК.) Deschampsia cespitosa (L.) P. BОКЮЯ. – Fq. (Norrlin 1871: Fqq.) Elymus caninus (L.) L. (Agropyron caninum (L.) P. BОКЮЯ.) – Fq. (Norrlin 1871: Fq in Shunga КЧН V. GЮЛК.) Elytrigia repens (L.) Nevski (Agropyron repens (L.) P. BОКЮЯ.) – Fq. (Norrlin 1871: *Fq.) Festuca arenaria OsЛОМФ – Rr: Megostrov (2004 Kravchenko). Festuca ovina L. – Fq. (Norrlin 1871: *Fq.) Festuca rubra L. – Fq. (Norrlin 1871: *Fqq.) GlycerТa luТtans (L.) R. Br. – P. (Norrlin 1871: *Fq.) **Glyceria lithuanica (GяrsФТ) GяrsФТ – R: V. GЮЛК (1943 KЮУКХК, ШЛs.); TЮrКsЭКЦШгОrШ (1989 Kravchenko); SСТХЭвК (1999 Timofeeva & Rudkovskaya); LТЩШЯТЭsв КЧН UгФКвК SКХЦК (2013 Kravchenko); OвКЭОЯТЭsК, PШХвК, TКЦЛТЭsв, TТЩТЧТЭsв – KКsФШsОХРК КЧН UгФТв SКХЦв (КХХ 2013 SвrУтЧОЧ, ШЛs.). Glyceria maxima (C. HКrЭЦ.) HШХЦЛ. – Rr: UsЭ’-ВКЧНШЦК (1943 KЮУКХК, ШЛs.); SСЮЧРК (HЮХЭцЧ 1971); KЮгКrКЧНК (HЮХЭцЧ 1971); OrШгС IsХ. (1999 KrКЯМСОЧФШ & Kashtanov); V. GЮЛК (2012 Kravchenko). (Norrlin 1871: Unitsa.) Glyceria notata CСОЯКХХ. – P. a Helictotrichon pubescens (HЮНs.) PТХР. (Avenula pubescens (HЮНs.) DЮЦШrЭ.) – Rr: B. Klim., Kurgenitzy (2007 Kravchenko); VОrФСЧОО MвКРrШгОrШ (2012 ГЧКЦОЧsФТв, ШЛs.). Hierochloë arctica C. Presl (H. hirta (SМСrКЧФ) BШrЛ. sЮЛsЩ. arctica (C. PrОsХ) G. АОТЦ.) – Fq. (Norrlin 1871: *P; Кs H. odorata (L.) P. Beauv.) a Hordeum distichon L. – Rr: Pod’elniki (2012 Kravchenko). Leymus arenarius (L.) HШМСsЭ. – Rr: SСЮЧРК КЧН TШХЯЮвК (HЮХЭцЧ 1971). RКЭСОr МШЦЦШЧ ТЧ ОКsЭОrЧ КЧН sШЮЭСОrЧ ЩКrЭ ШП ЭСО ХКФО КЧН ШЧ HОНШsЭrШЯ IsХКЧН ОКsЭ ШП KЮгКrКЧНК, ЛЮЭ ЯОrв rКrО ТЧ ГКШЧОгСвО, ЦКв ЛО ЛОМКЮsО ШП ХКМФ ШП sЮТЭКЛХО sКЧНв sСШrОs. 186 Reports of the Finnish Environment Institute 40 | 2014 Lolium perenne L. – OЧХв ШХН rОМШrНs: KЮгКrКЧНК (GüЧЭСОr 1880); V. GЮЛК, LКЦЦКsЩЮrШ КЧН UsЭ’-ВКЧНШЦК, КЛЮЧНКЧЭ ТЧ iОХНs, ЩrШЛКЛХв МЮХЭТЯКЭОН (1942/1943 KЮУКХК, ШЛs.); TШХЯЮвК КЧН KХТЦ NШs (FКРОrsЭröЦ & LЮЭСОr 1946). Melica nutans L. – Fq. (Norrlin 1871: *Fqq.) Milium effusum L. – Fq. (NШrrХТЧ 1871: V. GЮЛК.) Molinia caerulea (L.) MШОЧМС – P. (Norrlin 1871: Fq in Shunga.) Nardus stricta L. – P. (Norrlin 1871: *Fqq.) Phalaroides arundinacea (L.) Rauschert (Phalaris arundinacea L.) – Fq. (Norrlin 1871: *Stfq–fq.) Phleum pratense L. – Fq. (Norrlin 1871: *Fq.) Phragmites australis (CКЯ.) TrТЧ. Об SЭОЮН. – Fq. (Norrlin 1871: Fqq.) Poa alpina L. – R. (Norrlin 1871: Azhepnavolok and Shunga.) Poa angustifolia L. – Str. a Poa annua L. – Fq. (Norrlin 1871: *Fqq.) Poa compressa L. – Str. Poa humilis HШППЦ. (P. pratensis sЮЛsЩ. irrigata (LТЧНЦ.) H. LТЧНЛ., P. subcaerulea Smith, P. pratensis sЮЛsЩ. subcaerulea (SЦ.) HТТЭШЧОЧ) – R. Poa nemoralis L. – P. Poa palustris L. – Fq. (Norrlin 1871: *Stfq; ТЧМХ. P. nemoralis.) Poa pratensis L. – Fq. (Norrlin 1871: *Fqq; ЩrШЛКЛХв ТЧМХ. P. angustifolia.) **Poa remota FШrsОХ. – Rr: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.); TКЦЛТЭsв, VКrЧКЯШХШФ (2004 Kravchenko). Poa trivialis L. – Stfq. (Norrlin 1871: *Fq.) a Puccinellia distans (JКМq.) PКrХ. – Rr: Kosmozero (1999 Timofeeva & Rudkovskaya); KЮzaranda (2004 Kravchenko & Kuznetsov, 2004 Uotila); PКХОШsЭrШЯ (2004 Uotila); V. GЮЛК (2010 Kravchenko); KКгСЦК (2012 Kravchenko) ; B. KХТЦ., KШЧНК (2004 Uotila). a Schedonorus arundinaceus (SМСrОЛ.) DЮЦШrЭ. (Festuca arundinacea SМСrОЛ.) – Str. a Schedonorus pratensis (HЮНs.) P. BОКЮЯ. (Festuca pratensis HЮНs.) – Fq. (Norrlin 1871: SСЮЧРК; Кs Festuca elatior L.) Scolochloa festucacea (АТХХН.) LТЧФ – Rr: V. GЮЛК (LЮЭСОr 1945; FКРОrsЭröЦ & LЮЭСОr 1946); B. KХТЦ. КrОК (HЮХЭцЧ 1971); KТгСТ IsХ. (1994 Kuznetsov). a Secale cereale L. – OЧХв ШХН rОМШrНs: KХТЦ NШs (FКРОrsЭröЦ & LЮЭСОr 1946). a Dubious or erroneously recorded species Nymphaea tetragona Georgi (Klyukina 1965) Rumex confertus АТХХН. (BОгКТs 1911) Gentiana pneumonanthe L. (Bezais 1911) Carduus nutans L. (Bezais (1911) Lactuca tatarica (L.) C. A. Mey. (Bezais 1911) Phleum alpinum L. 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Reports of the Finnish Environment Institute 40 | 2014 191 Margarita Fadeeva and Alexei Kravchenko in moist herb-rich forest (spruce swamp) near Lipovitsy village (Photo Jevgeni Jakovlev). 192 Reports of the Finnish Environment Institute 40 | 2014 3.2 Bryophyte lora of Zaonezhye Peninsula Anatoly Maksimov* and Kimmo Syrjänen** *Institute of Biology of Karelian Research Center of Russian Academy of Sciences, Petrozavodsk. 50 Alexandra Nevskogo St., 185003 Petrozavodsk, Karelia, Russia ** The Finnish Environment Institute (SYKE) Corresponding author Kimmo Syrjänen E-mail: kimmo.syrjanen@ymparisto.i Abstract The bryophyte lora of Zaonezhye Peninsula consists of 235 species of mosses and 64 hepatics. The proportion of red listed and indicator species is very high in the area. The establishment of nature monuments and a strictly protected area on Zaonezhye Peninsula will contribute to the conservation of a number of rare Red Data Book species and valuable forest indicator species, growing on forests with pristine and old-growth characteristics, swamp forests and black alder forests, nutrient-rich mesotrophic and eutrophic mires, as well as calcicolous cliffs and rock outcrops. Introduction Floristically, Zaonezhye Peninsula is of great interest. Its distinctive lora and vegetation are due to a distinctive microclimate, different bedrocks and nutrient-rich, sodden lithogenic shungite soils. Shungite (name is according to village Shunga) is black carboniferous rock type which is typical for Zaonezhye. Due to favourable growth conditions, species of southern taiga forests occur here in a middle taiga landscape. According to the biogeographic zonation of Eastern Fennoscandia (Mela & Cajander 1906), the study area is located in the eastern part of the province of Karelia onegensis, or the Zaonezhye loristic province (Ramenskaya 1960). The Zaonezhye loristic province is the second most diverse province in Karelia for mosses after the Priladozhye loristic province. Despite the proximity of Zaonezhye Peninsula to Petrozavodsk and a well-developed road network, the peninsula, especially its western and northeastern parts, has been poorly studied bryoloristically until recently. For a long time the irst moss samples, collected by A.K. Cajander and J.I. Lindroth in the vicinity of Sennaya Guba and on Kizhi Island in 1898, were stored in the cryptogamous plant herbarium at the Reports of the Finnish Environment Institute 40 | 2014 193 Museum of Botany, Helsinki University. These samples have been published only recently (Ahti & Boychuk 2006). In 1921, L.I. Savich-Lyubitskaya collected mosses near the village of Shunga. Between 1987 and 1996, moss samples from Kizhi Island were collected by Oleg Kuznetsov, Anatoly Maksimov, Tatyana Brazovskaya and Natalya Stoikina who studied mire lora and vegetation; by V.A.Bakalin (Bakalin et al. 1999) who undertook a special study of moss species from Kizhi Islands and a part of Bolshoi Klimenetsky Isl.; and by Margarita Boychuk and Jevgenia Markovskaya who studied mosses on the islands of Kizhi Nature Reserve (Boychuk & Markovskaya 2005). The moss lora of Zaonezhye Peninsula (villages Shunga, Tolvuya, Lisitsino and Kosmozero) and the planned Zaonezhye Nature Reserve was studied by Anatoly Maksimov and Tatyana Maksimova in 2000 and by Anatoly Maksimov in 2001 and 2012. Moss samples, collected by Oleg Kuznetsov in 1999 and by Stanislav Kutenkov in 2012 from mires in the study area, have been used for compiling a list of moss species growing in the nature reserve. A list of moss species from Zaonezhye Nature Reserve has been published recently (Maksimov, 2013). This publication contains a list of new mosses from Zaonezhye Peninsula based for the most part on the results of our studies. By 2013, 221 moss species had been reported from Zaonezhye Peninsula (Bakalin et al. 1999; Kuznetsov et al. 2000; Boychuk & Markovskaya 2005; Ahti & Boychuk 2006; Maksimov 2013), although a consolidated list of moss species from the peninsula has not yet been published. In 2013, the Finnish scientists Kimmo Syrjänen and Olli Manninen continued the study of bryophytes from southern and southwestern Zaonezhye Peninsula. They collected and analyzed approximately 200 bryophyte samples, which are stored in the Turku University herbarium (TUR). Anatoly Maksimov re-analyzed the moss samples from Zaonezhye Peninsula, which are stored in the Karelian Research Centre herbarium (PTZ). In 2013, observations of certain indicator species of bryophytes like Neckera pennata were also collected by Jyri Mikkola, Olli-Pekka Tikkanen and Timo Kuuluvainen. As a result, four new moss species, namely Eurhynchium angustirete, Plagiomnium afine, Schistidium platyphyllum and Tayloria lingulata, and one liverwort, Anastrophyllum michauxii, have been reported from the Zaonezhye loristic province. Eurhynchium angustirete, Plagiomnium afine and Tayloria lingulata have been included in the Red Data Book of the Republic of Karelia (2007). Thirteen moss species (Dicranum fragilifolium, Herzogiella seligeri, Mnium lycopodioides, Myurella julacea, Neckera pennata, Plagiomnium drummondii, Plagiothecium latebricola, Polytrichastrum pallidisetum, Rhizomnium magnifolium, Schistidium platyphyllum, Sphagnum quinquefarium, S. rubellum and Tayloria lingulata) have been found for the irst time on Zaonezhye Peninsula. Thus, 235 moss species, making up 65% of the moss lora in the Zaonezhye loristic province (363 species), are now known from Zaonezhye Peninsula (see List of species). A preliminary list of hepatics includes 64 species. Rare and valuable species. Interesting Bryophyte species include Brachythecium rutabulum, Calypogeia suecica, Encalypta brevicolla, Eurhynchium angustirete, Hamatocaulis vernicosus, Harpanthus scutatus, Homomallium incurvatum, Hylocomiastrum pyrenaicum, Isothecium alopecuroides, Jamesomiella autumnalis, Leucodon sciuroides, Liochlaena lanceolata, Lophozia ascendens, Neckera besseri, N. pennata, Orthotrichum gymnostomum, Oxystegus tenuirostris, Plagiomnium afine, P. drummondii, Plagiothecium latebricola, Platygyrium repens, Pylaisia selwynii, Scapania apiculata, Schistidium pulchrum, Sphagnum auriculatum, S. pulchrum, S. lindbergii and Trichocolea tomentella. Fourteen of them, namely Calypogeia suecica, Eurhynchium angustirete, Harpanthus scutatus, Jamesomiella autumnalis, Lophozia ascendens, Neckera besseri, N. pennata, Orthotrichum gymnostomum, Plagiomnium afine, P. drummondii, Scapania apiculata, Sphagnum auriculatum, Tayloria 194 Reports of the Finnish Environment Institute 40 | 2014 lingulata and Trichocolea tomentella, are listed as very rare species in the Red Data Book of Karelia (2007). Some species from Zaonezhye Peninsula, e.g. Pylaisia selwynii and Hamatocaulis vernicosus, are included in the Red Data Book of European Bryophytes (Red.., 1995). Hamatocaulis vernicosus, Herzogiella turfacea and Plagiomnium drummondii are also listed in the EU Habitats Directive. Indicator species. Overall 47 bryophyte species, which according to Andersson et al. (2009) are considered indicator species of valuable forest habitats, are found from Zaonezhye Peninsula. This is a remarkably high number of indicator bryophytes. The list of indicator species includes many of the above-mentioned red-listed species: Anastrophyllum michauxii, Anomodon attenuatus, A. longifolius, Barbilophozia lycopodioides, Calypogeia suecica, Crossocalyx hellerianus, Dicranum drummondii, D. lagellare, D. fragilifolium, Eurhynchium angustirete, Harpanthus scutatus, Herzogiella seligeri, Homalia trichomanoides, Hylocomiastrum pyrenaicum, H. umbratum, Jamesoniella autumnalis, Leucodon sciuroides, Liochlaena lanceolata, Lophozia ascendens, Lophozia longilora, Mnium stellare, Neckera complanata, N. pennata, Orthocaulis attenuatus, Orthotrichum gymnostomum, O. obtusifolium, Oxyrrhynchium hians, Philonotis spp., Plagiochila asplenioides, Plagiomnium afine, P. drummondii, Plagiothecium latebricola, Platygyrium repens, Pseudobryum cinclidioides, Pterigynandrum iliforme, Pylaisia selwynii , Riccardia latifrons, R. palmata, Scapania apiculata, Schistostega pennata, Sphagnum quinquefarium, Sphagnum wulianum, Sphenolobus saxicola, Tayloria lingulata, Trichocolea tomentella and Tritomaria quinquedentata. The most valuable and interesting habitats and sites from the perspective of bryophyte species diversity include old-growth forests, alder swamps, mesotrophic and eutrophic mires and rich-fens as well as carboniferous rock outcrops. Old-growth spruce and mixed forests. Mesic, herb-rich forests with pristine and old-growth characteristics are very important for bryophyte biodiversity on Zaonezhye Peninsula. Often these forests create a long continuum of coarse woody debris and moist microclimates. Windfallen logs include mainly spruce but also aspen and sometimes pine. These forests are mainly located on heatland sites, remote from old villages, although they are sometimes found also on mire margins and along brooks and rivulets. Epixylic liverworts favour logs where the bark has fallen off and the surface is slightly softened. The diversity of epixylic liverworts typical for pristine forests is high in the forests of Zaonezhye. The frequency of indicator species such as Crossocalyx hellerianus, Lophozia longilora and Riccardia spp. as well as red-listed Calypogeia suecica varies from common to very common in these forests. For example, there are 160 observations of indicator species Crossocalyx hellerianus (syn. Anastrophyllum hellerianum) and red-listed Calypogeia suecica were collected from 21 sites in 2013. The early epixylic colonizer, Lophozia ciliata is common in Zaonezhye. More demanding epixylics such as red-listed Lophozia ascendens and Jamesoniella autumnalis are found in several stands, whereas both Scapania apiculata and Anastrophyllum michauxii seem to be rather rare. In the Zaonezhye population, female plants of Jamesoniella autumnalis also bear perianths, which indicates optimal conditions for growth. According to Damsholt (2002), perianths of Jamesoniella autumnalis are rare in Fennoscandia. Reports of the Finnish Environment Institute 40 | 2014 195 Fig. 1. Spruce logs host diverse lora of rare epixylic liverworts in Zaonetshye. Lipovitsy (Photo Kimmo Syrjänen). Swamp forests and other wet forests. The red-listed Harpanthus scutatus and the indicator species Liochlaena lanceolata grow in more moist and wet forests with the presence of black alder (Alnus glutinosa). Also, Plagiothecium latebricola is found on the stumps and at the bases of old alder trees in swamp forests and moist forests along streams. Trichocolea tomentella occurs where the forest bottom is moist and affected by groundwater. It seems to grow occasionally in herb-rich swamp forests affected by springs. On the forest loor of moist spruce and swamp forests, Rhytidiadelphus subpinnatus is commonly found, sometimes together with Hylocomiastrum umbratum and more rarely with Hylocomiastrum pyrenaicum. The last two species are considered indicator species of valuable forest habitats. Fig. 2. Herb-rich swamp forest near Polya (Photo Kimmo Syrjänen). 196 Reports of the Finnish Environment Institute 40 | 2014 Forests with large aspen trees. In addition to old-growth mixed forests, large aspen individuals are also present in the late successional stages of secondary deciduous forests. These forests are common on rich soils close to abandoned villages of southern Zanonezhye Peninsula. Indicator species Neckera pennata is relatively common and a typical epiphyte of large aspens. In sheltered conditions it forms large mats along trunks. In 2013, Neckera pennata was observed in 120 locations. Also Orthotrichum obtusifolium is a common indicator species, growing on Zaonezhye aspens. Orthotrichum gymnostomum is mainly found on aspen trunks in old-growth forests, although it also grows in secondary forests. It is easily overlooked as it typically grows relatively high up on the trunk and is therefore mainly found on recently fallen trees (either by wind or beavers). The same is true of Pylaisia selwynii, which is more rare than the closely related Pylaisia polyantha that is common on aspen trunks. Fig. 3. Base of aspen with Neckera pennata, etc. (Photo Kimmo Syrjänen). Deciduous and mixed herb-rich forests have a diverse bryophyte lora at the bases of aspens and on the forest loor. Both Eurhynchium angustirete and Plagiomnium drummondii grow in these habitats. Also indicator species Homalia trichomanoides and Isothecium alopecuroides can be found at the base of aspen trunks. Plagiomnium medium and Sciuro-hypnum curtum are very common on the forest loor. In addition to many rare liverworts, mosses Herzogiella seligeri and Herzogiella turfacea grow on decaying aspen trunks. The latter is common also in swamp forests. Rare Plagiomnium afine has been found at the base of old Ulmus glabra trunk in one deciduous stand. Bedrock exposures with carbonate rich rocks occur in various places in the area. These outcrops host a rich lora of bryophytes that prefer calcareous substrata. Species include Tortella tortuosa, Distichium capillaceum and Ditrichum lexicaule, which are typical indicators of limestone rocks. Especially worth mentioning are the southern and southeastern slopes of Mount Sypun, where there are rare species such as Encalypta brevicolla, Leucodon sciuroides, Neckera besseri, N. complanata and Oxystegus tenuirostris. Also the bedrock exposures on the south- and southwest-facing slopes of the southern end of Svyatukha Bay are important. The Red Data Book species Orthotrichum gymnostomum and rare nemoral species, including Anomodon attenuatus, Brachythecium rutabulum, Homalia trichomanoides, Isothecium alopecuroides, I. myosuroides, Platygyrium repens and Pseudoleskeella papillosa have been encountered here. Reports of the Finnish Environment Institute 40 | 2014 197 Fig. 4. Spring rich fen close to Kaskoselga with Carex appropinquata, Saxifraga hirculus and Hamatocaulis vernicosus etc. (Photo Kimmo Syrjänen). Valuable mires and fens. Certain mires near the lakes Karasozero and Koibozero, as well as Kalegubskoe Mire in the vicinity of Lambasruchei, are of great scientiic interest. The mosses Sphagnum pulchrum, S. aongstroemii and S. lindbergii, which are uncommon to Zaonezhye, have been found here. These mires also host a number of calciphilous mosses that rely on diverse ground nutrients (Dyachkova et al. 1993; Kuznetsov et al. 2000). In the southern part of the peninsula, there are also several fens that are valuable for conservation, including the fens southwest and northwest of the village of Tambitsy. These fens have a rich lora of bryophytes and vascular plants, including Hamatocaulis vernicosus. Conclusions The moss lora of the Zaonezhye Peninsula generally comprises the basic species that grow in Zaonezhye, where impoverished south-taiga forests occur in mid-taiga landscapes. The moss lora consists of 235 species that account for about 65% of the lora in the Zaonezhye loristic province. Altogether 14 bryophyte species of Karelian Red List have been found, but the amount of indicator species of valuable forest habitat is much higher: 47 mosses and liverworts. The establishment of a strictly protected area on the Zaonezhye Peninsula will contribute to the conservation of the rare Red Data Book species, such as Calypogeia suecica, Eurhynchium angustirete, Harpanthus scutatus, Jamesomiella autumnalis, Lophozia ascendens, Neckera besseri, N. pennata, Orthotrichum gymnostomum, Plagiomnium afine, P. drummondii, Scapania apiculata, Sphagnum auriculatum, Tayloria lingulata and Trichocolea tomentella, and the nemoral moss species Anomodon attenuatus, Brachythecium rutabulum, Leucodon sciuroides, Neckera complanata, Platygyrium repense and Pylaisia selwynii, most bryophytes, which grow on nutrient-rich eutrophic mires, and bryophyte indicators of old-growth forests. 198 Reports of the Finnish Environment Institute 40 | 2014 Zaonezhye has long history of traditional land use and selective cutting of forests, and also recently some forests are used in intensive forestry. However, large pristine-like stands with continuity of dead wood (both windfalls and standing trees) and large deciduous trees e.g. aspen are available in many places. Diverse bryolora of natural forests and mires is present in the peninsula. In addition to coniferous forests Zaonezhye has also many other valuable forest habitat types and mires with intact hydrology those support diverse bryophyte species composition. For example, swamp forests with black alder are such sites as well as deciduous late successional herb-rich stands. Larger pristine-like coniferous and herb rich mixed forest stands can be connected to each other by careful planning of conservation areas. Forests can also be connected to villages with shoreline forests, mires, swamp forests and waterways. Zaonezhye provides unique possibility to make connected network of conservation areas. 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MТrОsЖ. − IЧ: IЧЯОЧЭШrв КЧН ЛТШНТЯОrsТЭв sЭЮНТОs ШП ГКШЧОгСвО PОЧТЧsЮХК КЧН NШrЭСОrЧ sСШrО ШП ЭСО LКНШРК LКФО (ШЩОrКЭТЯЧШ-ТЧПШrЦКМТШЧЧвО ЦКЭОrТКХв). KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 71–83. (IЧ RЮssТКЧ). MКФsТЦШЯ, A.I. 2012. . . « » ДBrвШЭСвЭОs ШП ЭСО KТЯКМС NКЭЮrО RОsОrЯОЖ. – IЧ: PrТrШНЧвО ЩrШМОssв Т вКЯХОЧТвК Я ЮЧТФКХ’ЧвС ЮsХШЯТвКС srОНЧОЭКОгСЧШРШ гКЩШЯОЧНЧТФК. MКЭОrТКХв ЧКЮМСЧШ-ЩrКФЭТМСОsФШТ ФШЧПОrОЧМТТ, ЩШsЯвКsСОЧЧШТ 80-ХОЭТвЮ FGBU «GШsЮНКrsЭЯОЧЧвТ ЩrТrШНЧвТ гКЩШЯОНЧТФ “KТЯКМС”. PОЭrШгКЯШНsФ. Щ. 122–125. (IЧ RЮssТКЧ). MКФsТЦШЯ, A.I. 2013. . . 4.3. Д 4.3. MШssОsЖ. − IЧ: GrШЦЭsОЯ, A.N. (ОН.), SОХФК LКЧНsМКЩОs ШП the Zaonezhskii Peninsula: Natural Characteristics, Land Use, Conservation. Petrozavodsk: Karelian Research CОЧЭrО ШП RAS, Щ. 132–136. (IЧ RЮssТКЧ). MОХК, A.J. & CКУКЧНОr, A.K. 1906. SЮШЦОЧ ФКsЯТШ. – HОХsТЧФТ, Б+68+764 Щ. RКЦОЧsФКвК, M. L. 1960. . . ДHКЧНЛШШФ VКsМЮХКr PХКЧЭs ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ. 400 Щ. (IЧ RЮssТКЧ). RОН DКЭК BШШФ ШП EЮrШЩОКЧ BrвШЩСвЭОs. 1995. – TrШЧНСОТЦ. 291 Щ. RОН DКЭК BШШФ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК. 2007. IЯКЧЭОr, E. V. & KЮгЧОЭsШЯ, O. L. (ОНs.), . . ., . . ( .). – PОЭrШгКЯШНsФ, 368 Щ. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 199 Appendix List of mosses from Zaonezhye Peninsula Nomenclature according to Ignatov et al. (2006), with some changes. Fam. Sphagnaceae Sphagnum angustifolium (C. E. O.Jensen ex Russow) C. E. O. Jensen S. aongstroemii C. Hartm. S. auriculatum Schimp. S. balticum (Russow) C. E. O.Jensen S. capillifolium (Ehrh.) Hedw. S. centrale C. E. O. Jensen S. compactum Lam. & DC. S. contortum Schultz S. cuspidatum Ehrh. ex Hoffm. S. fallax (H. Klinggr.) H. Klinggr. S. imbriatum Wilson S. lexuosum Dozy & Molk. S. fuscum (Schimp.) H. Klinggr. S. girgensohnii Russow S. inundatum Russow S. jensenii H. Lindb. S. lindbergii Schimp. S. magellanicum Brid. S. majus (Russow) C. E. O. Jensen S. obtusum Warnst. S. papillosum Lindb. S. platyphyllum (Lindb. ex Braithw.) Warnst. S. pulchrum (Lindb. ex Braithw.) Warnst. S. quinquefarium (Lindb. ex Braithw.) Warnst. S. riparium Ångstr. S. rubellum Wilson S. russowii Warnst. S. squarrosum Crome S. subfulvum Sjörs S. subsecundum Nees S. teres (Schimp.) Ångstr. S. warnstorii Russow S. wulianum Girg. Fam. Andreaeaceae Andreaea rupestris Hedw. Fam. Polytrichaceae Atrichum tenellum (Röhl.) Bruch et al. A. undulatum (Hedw.) P. Beauv. Pogonatum urnigerum (Hedw.) P. Beauv. Polytrichastrum longisetum (Sw. ex Brid.) G. L. Smith P. pallidisetum (Funck) G. L. Smith Polytrichum commune Hedw. P. juniperinum Hedw. P. piliferum Hedw. 200 Reports of the Finnish Environment Institute 40 | 2014 P. strictum Brid. Fam. Tetraphidaceae Tetraphis pellucida Hedw. Fam. Funariaceae Funaria hygrometrica Hedw. Fam. Encalyptaceae Encalypta brevicolla (Bruch et al.) Ångstr. E. ciliata Hedw. E. rhaptocarpa Schwägr. E. vulgaris Hedw. Fam. Grimmiaceae Bucklandiella microcarpa (Hedw.) Bednarek-Ochyra & Ochyra Grimmia longirostris Hook. G. muehlenbeckii Schimp. Niphotrichum canescens (Hedw.) Bednarek-Ochyra & Ochyra Schistidium apocarpum (Hedw.) Bruch et al. S. dupretii (Thér.) W. A. Weber S. papillosum Culm. S. platyphyllum (Mitt.) H.Perss. S. pulchrum H. H. Blom S. rivulare (Brid.) Podp. Fam. Dicranaceae Dicranella cerviculata (Hedw.) Schimp. D. heteromalla (Hedw.) Schimp. D. schreberiana (Hedw.) Dixon Dicranum bonjeanii De Not. D. brevifolium (Lindb.) Lindb. D. drummondii Müll. Hal. D. lagellare Hedw. D. lexicaule Brid. D. fragilifolium Lindb. D. fuscescens Turner D. majus Turner D. montanum Hedw. D. polysetum Sw. D. scoparium Hedw. D. undulatum Schrad. ex Brid. Paraleucobryum longifolium (Hedw.) Loeske Fam. Rhabdoweisiaceae Amphidium lapponicum (Hedw.) Schimp. Cnestrum schisti (F. Weber & D. Mohr) I. Hagen Cynodontium strumiferum (Hedw.) Lindb. C. tenellum (Schimp.) Limpr. Hymenoloma crispulum (Hedw.) Ochyra Fam. Ditrichaceae Ceratodon purpureus (Hedw.) Brid. Distichium capillaceum (Hedw.) Bruch et al. Ditrichum lexicaule (Schwägr.) Hampe Saelania glaucescens (Hedw.) Broth. Fam. Pottiaceae Barbula convoluta Hedw. Bryoerythrophyllum recurvirostrum (Hedw.) P.C. Chen Reports of the Finnish Environment Institute 40 | 2014 201 Didymodon ferrugineus (Schimp. ex Besch.) M.O. Hill D. rigidulus Hedw. Oxystegus tenuirostris (Hook. & Tayl.) A. J. E. Smith Syntrichia ruralis (Hedw.) F. Weber & D. Mohr Tortella fragilis (Hook. & Wilson) Limpr. T. tortuosa (Hedw.) Schimp. Fam. Fissidentaceae Fissidens adianthoides Hedw. F. osmundoides Hedw. Fam. Schistostegaceae Schistostega pennata (Hedw.) F. Weber & D. Mohr Fam. Meesiaceae Leptobryum pyriforme (Hedw.) Wilson Meesia triquetra (Jolycl.) Ångstr. Paludella squarrosa (Hedw.) Brid. Fam. Splachnaceae Splachnum luteum Hedw. S. rubrum Hedw. Tayloria lingulata (Dicks.) Lindb. Tetraplodon angustatus (Hedw.) Bruch et al. Fam. Orthotrichaceae Orthotrichum gymnostomum Bruch ex Brid. O. obtusifolium Brid. O. rupestre Schleich. ex Schwägr. O. speciosum Nees Fam. Hedwigiaceae Hedwigia ciliata (Hedw.) P. Beauv. Fam. Bryaceae Bryum argenteum Hedw. B. bimum (Schreb.) Turner B. caespiticium Hedw. B. capillare Hedw. B. creberrimum Tayl. B. lonchocaulon Müll. Hal. B. moravicum Podp. B. pallescens Schleich. ex Schwägr. B. pseudotriquetrum (Hedw.) P. Gaertn., B. Mey. & Schreb. B. weigelii Spreng. Rhodobryum roseum (Hedw.) Limpr. Fam. Mielichhoferiaceae Pohlia bulbifera (Warnst.) Warnst. P. cruda (Hedw.) Lindb. P. nutans (Hedw.) Lindb. Fam. Mniaceae Cinclidium stygium Sw. Mnium lycopodioides Schwägr. M. stellare Hedw. Plagiomnium afine (Bland.) T. J. Kop. P. cuspidatum (Hedw.) T. J. Kop. P. drummondii (Bruch & Schimp.) T.J. Kop. Plagiomnium elatum (B.S.G.) T.J. Kop. P. ellipticum (Brid.) T. J. Kop. 202 Reports of the Finnish Environment Institute 40 | 2014 P. medium (Bruch et al.) T. J. Kop. Pseudobryum cinclidioides (Huebener) T. J. Kop. Rhizomnium magnifolium (Horik.) T.J.Kop. R. pseudopunctatum (Bruch & Schimp.) T. J. Kop. R. punctatum (Hedw.) T. J. Kop. Rhodobryum roseum (Hedw.) Limpr. Fam. Bartramiaceae Bartramia pomiformis Hedw. Philonotis fontana (Hedw.) Brid. Fam. Aulacomniaceae Aulacomnium palustre (Hedw.) Schwägr. Fam. Fontinalaceae Dichelyma falcatum (Hedw.) Myrin Fontinalis antipyretica Hedw. Fam. Plagiotheciaceae Herzogiella seligeri (Brid.) Z. Iwats. Herzogiella turfacea (Lindb.) Z. Iwats. Isopterygiopsis pulchella (Hedw.) Z. Iwats. Myurella julacea (Schwägr.) Schimp. Plagiothecium cavifolium (Brid.) Z. Iwats. P. denticulatum (Hedw.) Bruch et al. P. laetum Bruch et al. P. latebricola Bruch et al. P. piliferum (Sw.) Bruch et al. Fam. Pterigynandraceae Pterigynandrum iliforme Hedw. Fam. Leucodontaceae Leucodon sciuroides (Hedw.) Schwägr. Fam. Hypnaceae Hypnum cupressiforme Hedw. Fam. Pylaisiadelphaceae Platygyrium repens (Brid.) Bruch et al. Fam. Pseudoleskeaceae Lescuraea incurvata (Hedw.) Lawt. Fam. Anomodontaceae Anomodon attenuatus (Hedw.) Huebener A. longifolius (Brid.) Hartm. Fam. Heterocladiaceae Heterocladium dimorphum (Brid.) Bruch et al. Fam. Neckeraceae Homalia trichomanoides (Hedw.) Bruch et al. Neckera besseri (Lobarz.) Jur. N. complanata (Hedw.) Huebener N. oligocarpa Bruch N. pennata Hedw. Fam. Climaciaceae Climacium dendroides (Hedw.) F. Weber & D. Mohr Fam. Hylocomiaceae Hylocomiastrum pyrenaicum (Spruce) M. Fleisch. H. umbratum (Hedw.) M. Fleisch. Hylocomium splendens (Hedw.) Bruch et al. Pleurozium schreberi (Brid.) Mitt. Reports of the Finnish Environment Institute 40 | 2014 203 Rhytidiadelphus squarrosus (Hedw.) Warnst. R. subpinnatus (Lindb.) T. J. Kop. R. triquetrus (Hedw.) Warnst. Fam. Lembophyllaceae Isothecium alopecuroides (Lam. ex Dubois) Isov. I. myosuroides Brid. Fam. Brachytheciaceae Brachytheciastrum velutinum (Hedw.) Ignatov & Huttunen Brachythecium albicans (Hedw.) Bruch et al. B. erythrorrhizon Bruch et al. B. mildeanum (Schimp.) Schimp. B. rivulare Bruch et al. B. rutabulum (Hedw.) Bruch et al. B. salebrosum (F. Weber & D. Mohr) Bruch et al. Cirriphyllum piliferum (Hedw.) Grout Eurhynchiastrum pulchellum (Hedw.) Ignatov & Huttunen Eurhynchium angustirete (Broth.) T.J. Kop. Oxyrrhynchium hians (Hedw.) Loeske Sciuro-hypnum curtum (Lindb.) Ignatov S. populeum (Hedw.) Ignatov & Huttunen S. relexum (Starke) Ignatov & Huttunen S. starkei (Brid.) Ignatov & Huttunen Fam. Calliergonaceae Calliergon cordifolium (Hedw.) Kindb. C. giganteum (Schimp.) Kindb. C. megalophyllum Mikut. C. richardsonii (Mitt.) Kindb. Loeskypnum badium (Hartm.) H. K. G. Paul Straminergon stramineum (Dicks. ex Brid.) Hedenäs Warnstoria exannulata (Bruch et al.) Loeske W. luitans (Hedw.) Loeske W. procera (Renauld & Arnell) Tuom. W. tundrae (Arnell) Loeske Fam. Scorpidiaceae Hamatocaulis vernicosus (Mitt.) Hedenäs Hygrohypnella ochracea (Turner ex Wilson) Ignatov & Ignatova Sanionia uncinata (Hedw.) Loeske Scorpidium cossonii (Schimp.) Hdenäs S. revolvens (Sw. ex anon.) Rubers S. scorpioides (Hedw.) Limpr. Fam. Pylaisiaceae Breidleria pratensis (W. D. J. Koch ex Spruce) Loeske Calliergonella cuspidata (Hedw.) Loeske C. lindbergii (Mitt.) Hedenäs Homomallium incurvatum (Schrad. ex Brid.) Loeske Ptilium crista-castrensis (Hedw.) De Not. Pylaisia polyantha (Hedw.) Bruch et al. P. selwynii Kindb. Stereodon pallescens (Hedw.) Mitt. Fam. Rhytidiaceae Rhytidium rugosum (Hedw.) Kindb. Fam. Pseudoleskeellaceae 204 Reports of the Finnish Environment Institute 40 | 2014 Pseudoleskeella nervosa (Brid.) Nyh. P. papillosa (Lindb.) Kindb. P. tectorum (Funck ex Brid.) Kindb. Fam. Thuidiaceae Abietinella abietina (Hedw.) M. Fleisch. Helodium blandowii (F. Weber & D. Mohr) Warnst. Thuidium assimile (Mitt.) A. Jaeger T. recognitum (Hedw.) Lindb. Fam. Amblystegiaceae Amblystegium serpens (Hedw.) Bruch et al. Campyliadelphus chrysophyllus (Brid.) Kanda C. elodes (Lindb.) Kanda Campylidium sommerfeltii (Myrin) Ochyra Campylium protensum (Brid.) Kindb. Campylium stellatum (Hedw.) C. E. O. Jensen Cratoneuron ilicinum (Hedw.) Spruce Drepanocladus aduncus (Hedw.) Warnst. D. polygamus (Bruch et al.) Hedenäs Drepanocladus sendtneri (Schimp. ex H. Müll.) Warnst. Hygroamblystegium luviatile (Hedw.) Loeske Leptodictyum riparium (Hedw.) Warnst. Palustriella falcata (Brid.) Hedenäs Pseudocalliergon trifarium (F. Weber & D. Mohr) Loeske Serpoleskea subtilis (Hedw.) Loeske Tomentypnum nitens (Hedw.) Loeske Fig. 5. Neckera pennata (Photo: Kimmo Syrjänen). Reports of the Finnish Environment Institute 40 | 2014 205 Fig. 6. Rhytidiadelphus subpinnatus (Photo: Kimmo Syrjänen). Fig. 7. Trichocolea tomentella (Photo: Kimmo Syrjänen). 206 Reports of the Finnish Environment Institute 40 | 2014 3.3 List of lichens and allied fungi collected on Zaonezhye Peninsula Margarita A. Fadeeva*, Olli Manninen** and Kimmo Syrjänen*** *Forest Research Institute of Karelian Research Center of Russian Academy of Sciences, 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia Corresponding author Margarita Fadeeva E-mail: fadeeva@krc.karelia.ru ** Luonto-Liitto, Annankatu 26 A, 00100 Helsinki, Finland *** The Finnish Environment Institute (SYKE), P.O.Box 140, 00251 Helsinki, Finland. History of the studies of lichens in Zaonezhye Peninsula and adjacent islands The pioneer study of the lichen lora on Zaonezhye Peninsula was undertaken in 1863 by two Finnish naturalists: student Th. Simming and lecturer A. Kullhem. They collected a large number of lichen specimens, which are now in the herbarium of the Botanical Museum of the Finnish Museum of Natural History, University of Helsinki (H). The collection was analyzed and partly published by W. Nylander (1866 a, c), the greatest lichen classiier at that time. In the same time (1863) Alexander K. Günther was travelling, presumably together with Th. Simming and A. Kullhem, on Zaonezhye Peninsula. A. K. Günther, an Alexander Plant staff healer in the Olonets Province, who later collected lichens actively near Petrozavodsk, visited the northeastern part of the territory and Kizhi Island. The results of his trip are reported in his work “On lora of the Obonega Region Province» (Günther 1880), where lichens are not mentioned. In 1870, Finnish botanist and phytogeographer J.P. Norrlin visited the biogeographic province Karelia onegensis (Kon) (it is Norrlin was the irst scientist who recognized Kon province he interpreted it in a broader sense than modern authors do). Norrlin described many of the samples he collected near the villages of Velikaya Guba, Tolvuja and Shunga, together with the samples collected by Th. Simming and A. Kullhem, in the second part of his classical work «Flora Kareliae Onegensis. II. Lichenes» (Norrlin 1876). The collections of Th. Simming, A. Kullhem and J. P. Norrlin are referred to by E. A. Vainio in his fundamental work «Lichenographia Fennica. I–IV» (Vainio 1921, 1922, 1927, 1934). Norrlin’s collections are stored in H. Reports of the Finnish Environment Institute 40 | 2014 207 In 1898 and 1899, Finnish botanists A.K. Cajander and J. I. Lindroth (subsequently Liro) toured Russian Karelia and the Onega River area. They visited many places such as Kizhi Island, Bolshoi Klimenetsky Island, Bolshoi Lelikovsky Island (Point Radkolye), Yuzhny Oleny Island and other smaller islands. Their routes have been described and lists of the moss species, liverworts and lichens collected by Cajander and Lindroth have been published by T. Ahti and M. Boychuk (Ahti & Boychuk 2006). The list of lichens, which consists of 68 species, does not comprise samples from the Zaonezhye Peninsula. In 1907, Russian agronomist and botanist E.K. Bezais took a 2-month ield trip to Karelia. His goal was to study and describe the coastal and insular vegetation of Lake Onega. While travelling, he collected and described both plants and lichens. He submitted a detailed report on his trip (Bezais 1911), in which he mentioned Cladonia rangiferina (L.) F. H. Wigg. found on Paleostrov Island. The herbarium of Botanical Institute (LE) comprises at least two lichen samples collected by E.K. Bezais and A. Verdi «on north shore of Lake Onega»: Rhizocarpon badioatrum (Flörke ex Spreng.) Th. Fr. and Rhizocarpon distinctum Th. Fr. (Fadeyeva et al. 1997). In 1920–1924, V.P. Savich joined the Olonets Scientiic Expedition led by G.U. Vereshchagin and organized by the State Hydrological Institute together with the Main Botanical Gardens (now the Botanical Institute, RAS) and other scientiic institutions, and collected lichen samples on shores of lakes Sandal, Segozero and Vygozero and near Povenets (west and north shores of Lake Onega). It is well- known that he also visited the Shunga area, because LE has a sample of Ophioparma ventosa (L.) Norman collected by V.P. Savich and L.I. Savich-Lyubitskaya on Gorodok Hill, 9 km southeast of Shunga. Unfortunately, many samples from a huge collection of lichens (several thousand samples) brought by V.P. Savich from Karelia and kept in LE (Vereshchagin 1921, 1924) have not yet been analyzed. In the 1970s, T.P. Sizova and T. Yu. Tolpysheva of Moscow State University studied the species composition of lichens on famous wooden Church of Transiguration on Kizhi Island (Tolpysheva et al. 2001). In 1999–2001 and 2007, M.A. Fadeyeva visited Kizhi Island, Bolshoi Klimenetsky Island, Bolshoi Lelikovsky Island, Severny and Yuzhny Oleny Island, Volkostrov, Krestovy and Belaya Selga village in Zaonezhye. Only a small portion of more than one thousand samples collected chiely in 1999 has been published (Fadeyeva 2000, 2001, 2003, Fadeyeva et al. 2007). In 2004, M.A. Fadeyeva joined a Russian-Finnish expedition to the Zaonezhye Peninsula and Lake Onega islands (3.–8 July, 2004). Russia was represented by E. Gnatjuk, A. Kravchenko, A. Kryshen’ & O. Kuznetsov and Finland by M. Piirainen, T. Lindholm, R. Ruuhijärvi & P. Uotila. She visited Bolshoi Klimenetsky Island (Klimetsky Nos Peninsula and Point Lukovo), Bolshoi Lelikovsky Island (Point Radkolye), Megostrov, Paleostrov, Rechnoi, Shushenevsky and Yuzhny Oleny islands and the continental shore near Kuzaranda and Tipinitsky villages (Point Varnavolok). In 2010, M.A. Fadeyeva, together with A. V. Kravchenko, V.I. Krutov, O.O. Predtechenskaya and A.V. Ruokolainen (Forest Research Institute, KarRC, RAS), studied the area north and south of Velikaya Guba (the environs of the former villages Komlevo, Ryabovo, Lipovitsky and Lakes Palozero and Khmeleozero). In 2012, M.A. Fadeyeva was involved in the integrated study of planned Zaonezhsky Landscape Reserve. The study was conducted by the Forest Research Institute, KarRC, RAS (Fadeyeva 2013). In 2012, A. V. Kravchenko and M.A. Fadeyeva studied the vascular plant and lichen lora of the mainland shores near the Kizhi Skerries from the village of Oyatevshchina to Lake Vekhozero at the request of Kizhi Museum-Reserve (Fadeyeva & Kravchenko 2013). A list of 137 lichens and related fungi was made up, but it was not presented in the above publication. The lichen samples 208 Reports of the Finnish Environment Institute 40 | 2014 collected by A. V. Kravchenko and M.A. Fadeyeva are in the Karelian Research Centre herbarium (PTZ). Finally, in 2013, Olli Manninen, Kimmo Syrjänen and Margarita Fadeeva joined a Finnish-Russian Zaonezhye expedition in the framework of the BPAN project and collected lichen samples on southeastern part of Zaonezhye Peninsula (see Syrjänen et al. 2014, p. 212). Acknowledgements The author Margarita Fadeeva is thankful for professor Soili Stenroos (Head Curator of Fungi at Botanical Museum/Finnish Museum of Natural History University of Helsinki) for the help during her visits in Helsinki University Herbarium in 2011 and 2012, and for professor Teuvo Ahti for the permanent help in her work. REFERENCES AЧНОrssШЧ, L., AХОбООЯК, N.M., & KЮгЧОЭsШЯК, E. S. (ОНs) 2009. ., . ., . . ДSЮrЯОв ШП ЛТШХШРТМКХХв ЯКХЮКЛХО ПШrОsЭs ТЧ NШrЭС-АОsЭОrЧ EЮrШЩОКЧ RЮssТК. VШХ 2. IНОЧЭТiМКЭТШЧ ЦКЧЮКХ ШП sЩОМТОs ЭШ ЛО ЮsОН НЮrТЧР sЮrЯОв КЭ sЭКЧН ХОЯОХЖ. – SЭ-PОЭОrsЛЮrР. 258 Щ. AСЭТ T., BШвМСЮФ M. 2006. TСО ЛШЭКЧТМКХ УШЮrЧОвs ШП A. K. CКУКЧНОr КЧН J. I. LТЧНrШЭС ЭШ KКrОХТК КЧН OЧОРК RТЯОr ТЧ 1898 КЧН 1899, аТЭС К ХТsЭ ШП ЭСОТr ЛrвШЩСвЭО КЧН ХТМСОЧ МШХХОМЭТШЧs. – NШrrХТЧТК 14: 1–65. BОгКТs, E. K. 1911. . . . ДRОЩШrЭ ШЧ ЛШЭКЧТМКХ sЭЮНв ШП LКФО OЧОРК sСШrОs ПrШЦ PОЭrШгКЯШНsФ ЭШ PШЯОЧОЭsЖ. − IЧ: PrШМООНТЧРs ШП ЭСО SЭ.PОЭОrsЛЮrР NКЭЮrКХТsЭs’ SШМТОЭв. BШЭКЧв SОМЭТШЧ. 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VШХ. 2: 17—60. (IЧ RЮssТКЧ). HОrЭОХ, H. 1970. PКrКsТЭТsМСО ХТМСОЧТsТОrЭО ArЭОЧ НОr SКЦЦОХРКЭЭЮЧР LОМТНОК ТЧ EЮrШЩК. − HОrгШРТК. (1): 405–438. MКРЧЮssШЧ, A. H. 1939. SЭЮНТОs ТЧ sЩОМТОs ШП LОМКЧШrК ЦКТЧХв ЭСО AsЩТМТХТК РТЛЛШsК РrШЮЩ. − KЮЧРХТРК SЯОЧsФК VОЭОЧsФКЩsКФКНОЦТОЧs HКЧНХТЧРКr. SОrТОs 3. 17(5): 1–182. NШrНТЧ, I. 1972. CКХШЩХКМК, sОМЭ. GКsЩКrrТЧТК ТЧ NШrНОЮrШЩК. – TКбШЧШЦТsФК ШМС ОФШХШРТsФК SЭЮНТОr. UЩsКХК, 184 Щ. Reports of the Finnish Environment Institute 40 | 2014 209 NШrНТЧ, A., MШЛОrР, R., TøЧsЛОrР, T., VТЭТФКТЧОЧ, O., DКХsтЭЭ, й., MвrНКХ, M., SЧТЭЭТЧР, D. & EФЦКЧ, S. 2011. SКЧЭОssШЧ’s CСОМФХТsЭ ШП FОЧЧШsМКЧНТКЧ LТМСОЧ-ПШrЦТЧР КЧН LТМСОЧТМШХШЮs FЮЧРТ. VОrsТШЧ AЩrТХ 29, 2011 – СЭЭЩ://130.238.83.220/sКЧЭОssШЧ/СШЦО.ЩСЩ (12 NШЯОЦЛОr 2014). NШrrХТЧ, J. P. 1876: FХШrК KКrОХТКО OЧОРОЧsТs. II. LТМСОЧОs. − MОННОХКЧНОЧ SШМ. FКЮЧК FХШrК FОЧЧТМК 1:1–46. NвХКЧНОr, А. 1866 К. LТМСОЧОs LКЩЩШЧТКО ШrТОЧЭКХТs. − NШЭТsОr SтХХsФ. FКЮЧК FХШrК FОЧЧТМК FörСКЧНХ.8: 101–192 (Preprint). NвХКЧНОr, А. 1866 М. AННОЧНК ЧШЯК КН LТМСОЧШРrКЩСТКЦ ОЮrШЩКОКЦ. CШЧЭТЧЮКЭТШ ЭОrЭТК. − FХШrК 49: 417–421. SвrУтЧОЧ, K., MКЧЧТЧОЧ O, & FКНООЯК, M.A. 2014. RОН-ХТsЭОН КЧН ТЧНТМКЭШr ХТМСОЧs ШП ГКШЧОгСвО PОЧТЧsЮХК. − IЧ: LТЧНСШХЦ, T., JКФШЯХОЯ, J. & KrКЯМСОЧФШ, A. (ОНs.), BТШРОШРrКЩСв, ХКЧНsМКЩОs, ОМШsвsЭОЦs КЧН sЩОМТОs ШП ГКШЧОгСвО PОЧТЧsЮХК, ТЧ OЧОРК LКФО, RЮssТКЧ KКrОХТК. RОЩШrЭs ШП ЭСО FТЧЧТsС EЧЯТrШЧЦОЧЭ IЧsЭТЭЮЭО 2014/40: 223-230. TШХЩвsСОЯК, . ВЮ., LвЮЛТЦШЯК . G., GШrsСТЧК . S., SТгШЯК . P. 2001. . ., . ., Г рш а Е. ., ва . П. . 3. ДLТМСОЧ lШrК ШП КЧМТОЧЭ аШШНОЧ КrМСТЭОМЭЮrКХ ЦШЧЮЦОЧЭs. 3. CСЮrМС ШП TrКЧsiРЮrКЭТШЧ ТЧ KТгСТЖ. − IЧ: VОsЭЧТФ MШsФШЯsФШРШ ЮЧТЯОrsТЭОЭК, SОr. 16. BТШХШРв 1: 24–33. (IЧ RЮssТКЧ). VКТЧТШ, E. A. 1923−1934. LТМСОЧШРrКЩСТК FОЧЧТМК. I–IV. − AМЭК SШМ. FКЮЧК FХШrК FОЧЧТМК 1921. 49(2): 1–274 (1921). 53(1): 1–340 (1922). 57(1): 1–138 (1927). 57(2–3): 1–531 (1927). VОrОsСМСКРТЧ, G. ВЮ. 1921. . . . 1920 ДOХШЧОЭs sМТОЧЭТiМ ОбЩОНТЭТШЧ. PrОХТЦТЧКrв rОЩШrЭ ШЧ 1920 sЭЮНвЖ. 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List of lichens and allied fungi of Zaonezhye Peninsula The list is compiled on basis of published data and from recent collections, as well as from specimens in the herbaria of Karelian Scientiic Center of Russian Academy of Sciences, Petrozavodsk (PTZ), Institute of Botany of Russian Academy of Sciences, St. Petersburg PAH (LE), Botanical Museum of the Finnish Museum of Natural History, University of Helsinki (H), and University of Turku (TUR). Bol. Klim.Isl. − Bolshoi Klimenetsky Island * - lichenicolous fungus, + - saprophytic fungus The nomenclature follows Nordin et al. (2011). The list incorporates 298 species and infraspeciic taxa of lichens, 3 species of lichenicolous fungi, and 3 species of saprotrophic fungi 1. 2. 3. 4. 5. 6. 7. 210 Acarospora fuscata (Schrad.) Th. Fr. – Norrlin 1876; Fadeeva 2013; Podyelniki, on stones in the wall around old chapel, 08.07.2012, M.A. Fadeeva, PTZ. Acarospora glaucocarpa (Ach.) Körb. – Norrlin 1876. Adelolecia kolaёnsis (Nyl.) Hertel & Rambold – Norrlin 1876; Vainio 1934. Alectoria sarmentosa (Ach.) Ach. – Polya village -S, herb-rich spruce mire, on twigs of spruce, 25.08.2013, K. Syrjänen, TUR; Velikaya Guba -SW, Zubovo -N, NE of the Lake Pužej, siliceous east facing cliff, on rock wall, 24.08.2013, K.Syrjänen, TUR. Alyxoria varia (Pers.) Ertz & Tehler – Shunga, 1870, J. P. Norrlin, . Amandinea coniops (Wahlenb.) M.Choisy ex Scheid. & H. Mayrhofer – Norrlin 1876. Amandinea punctata (Hoffm.) Coppins & Scheid. – Fadeeva 2000. Reports of the Finnish Environment Institute 40 | 2014 8. 9. 10. 11. 12. 13. 14. 15. 16. 17. 18. 19. 20. 21. 22. 23. 24. 25. 26. 27. 28. 29. 30. 31. 32. 33. 34. 35. 36. Arctoparmelia centrifuga (L.) Hale – Fadeeva 2013; NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. Arctoparmelia incurva (Pers.) Hale – Fadeeva 2013. Arthonia cinereopruinosa Schaer. – Nylander 1866 a; Norrlin 1876. Arthonia mediella Nyl.– Norrlin 1876. Arthonia radiata (Pers.) Ach. – Norrlin 1876. Arthonia spadicea Leight. – Norrlin 1876. Aspicilia cinerea (L.) Körb. – Norrlin 1876. Aspicilia verrucigera Hue – Bol. Klim.Isl., 1863, A. Kullhem, H: Magnusson 1939. Bacidia bagliettoana (A. Massal. & De Not.) Jatta – Norrlin 1876; Vainio 1922; Fadeeva 2013; Kizhi Island, on Ulmus laevis, 27.05.1999, M.A. Fadeeva, PTZ. Bacidia rubella (Hoffm.) A. Massal. – Norrlin 1876; Vainio 1922. Bacidia subincompta (Nyl.) Arnold – Norrlin 1876; Vainio 1922. Baeomyces carneus Flörke – Fadeeva 2013. Bellemerea cinereorufescens (Ach.) Clauzade & Cl. Roux – Norrlin 1876. Bellemerea diamarta (Ach.) Hafellner & Cl. – Norrlin 1876. Biatora pallens (Kullh.) Printzen – Zubovo village, on Sorbus aucuparia, 03.07.2012, M.A. Fadeeva, PTZ. Biatora vernalis (L.) Fr. – Tolpysheva et al. 2001. Blastenia crenularia (With.) Arup et al. – Norrlin 1876. Botryolepraria lesdainii (Hue) Canals & al. – Fadeeva 2013. Bryoria capillaris (Ach.) Brodo & D. Hawksw. – Fadeeva 2013; NW shore of Lake Vekhkozero, on twigs of spruce 11.07.2012, M.A. Fadeeva, PTZ. Bryoria fremontii (Tuck.) Brodo & D. Hawksw. – Vegoruksy Village, ca. 1.5 km SE, forest-side edge of dry grassland on sandy ground, A.V. Kravchenko, 19.08.2010, PTZ. Bryoria furcellata (Fr.) Brodo & D. Hawksw. – Fadeeva 2000; Tolpysheva et al. 2001; Zubovo village, on trunk and twigs of pine, 03.07.2012, M.A. Fadeeva, PTZ; Podyelniki, on trunk and twigs of pine, 10.07.2012, M.A. Fadeeva, PTZ. Bryoria fuscescens (Gyeln.) Brodo & D. Hawksw. – Surroundings of Zubovo village, on trunks and twigs of pine, 03.07.2012, M.A. Fadeeva, PTZ; Podyelniki, on pine, 10.07.2012, M.A. Fadeeva, PTZ; Zubovo –N, on twigs of spruce, 24.08. 2013, K. Syrjänen, TUR. Bryoria implexa (Hoffm.) Brodo & D.Hawksw. – Fadeeva 2013. Bryoria nadvornikiana (Gyeln.) Brodo & D. Hawksw. – Tolpysheva et al. 2001; Fadeeva 2013; North to Zubovo village, on dry Juniperus communis, 04.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013, Podyelniki, on dry Juniperus communis, 10.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on twigs of spruce, 11.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Polya village, on Betula, 26.06.2013, M.A. Fadeeva, PTZ; Tambitsy village NW, Kaskoselga E, spruce bog at border of a fen, on birch and spruce, 28.08.2014 K. Syrjänen, TUR. Bryoria simplicior (Vain.) Brodo & D. Hawksw. – Tolpysheva et al. 2001. Buellia disciformis (Fr.) Mudd – Fadeeva, 2000; Zubovo village, on bark of Sorbus aucuparia, 03.07.2012, M.A. Fadeeva, PTZ. Calicium salicinum Pers. – Norrlin 1876; Zubovo village, on stump of Salix caprea, 04.07.2012, M.A. Fadeeva, PTZ. Calicium trabinellum (Ach.) Ach. – Podyelniki, on wood of pine, 10.07.2012, M.A. Fadeeva, PTZ. Calicium viride Pers. – On bark of spruce, Podyelniki, 07.07.2012, western shore of Lake Vekhkozero, 11.07.2012, M.A. Fadeeva, PTZ. Reports of the Finnish Environment Institute 40 | 2014 211 37. Caloplaca cerina (Hedw.) Th.Fr. – Tolpysheva et al. 2001; Zubovo village, on Prunus padus, 03.07.2012, M.A. Fadeeva, PTZ. 38. Caloplaca saxicola (Hoffm.) Nordin – Norrlin 1876; Nordin 1972. 39. Candelaria concolor (Dicks.) Stein – Tolpysheva et al. 2001; probably this is Candelaria paciica M. Westb. & Arup, see: Westberg & Arup 2010. 40. Candelariella aurella (Hoffm.) Zahlbr. – Tolpysheva et al. 2001; Kizhi Island, on Ulmus laevis, 28.05.1999, M.A. Fadeeva, PTZ. 41. Candelariella coralliza (Nyl.) H. Magn. – Ersenevo village, abandoned ield, on stones, 05.07.2012, M.A. Fadeeva, PTZ. 42. Candelariella vitellina (Hoffm.) Müll. Arg. – Tolpysheva et al., 2001; Fadeeva 2013; 43. Candelariella xanthostigma (Ach.) Lettau – Fadeeva, 2000, Pustoy Bereg, abandoned village, on Ulmus laevis, 04.07.2012, M.A. Fadeeva, PTZ. 44. Catillaria erysiboides (Nyl.) Th. Fr. – Nylander 1866 a; Norrlin 1876; Vainio 1934; 45. Cetraria aculeata (Schreb.) Fr. – Bol. Klim. Isl., Lukovo Bay, on rock, 05.07.2004, M.A. Fadeeva PTZ. 46. Cetraria ericetorum Opiz – Fadeeva 2000. 47. Cetraria islandica (L.) Ach. subsp. islandica – Fadeeva 2000, 2013; Podyelniki, on ground, 10.07.2012, M.A. Fadeeva, PTZ. 48. Cetraria odontella (Ach.) Ach. – Norrlin 1876; Fadeeva 2013. 49. Cetraria sepincola (Ehrh.) Ach. – Tolpysheva et al. 2001; Fadeeva 2000; Podyelniki, on stones in the wall around old chapel, 08.07.2012, M.A. Fadeeva, PTZ. 50. Cetrelia cetrarioides (Delise & Duby) W. L. Culb. & C. F. Culb. – on rocks, Paleostrov Island, 03.07.2004, M.A. Fadeeva, PTZ; Bolshoi Lelikovsky Island, Radkolye Cape, 06.07.2004, M.A. Fadeeva, PTZ. 51. Chaenotheca brachypoda (Ach.) Tibell – Fadeeva 2013; Fadeeva & Kravchenko 2013; Zubovo village, stump of Salix caprea, 04.07.2012, M.A. Fadeeva, PTZ; Polya village, stump of Salix caprea, 26.06.2013, M.A. Fadeeva, PTZ; surroundings of Lake Rugozero, stump of birch, 27.06.2013, M.A. Fadeeva, PTZ. 52. Chaenotheca brunneola (Ach.) Müll. Arg. – Western shore of Lake Vekhkozero, on bark of spruce, 11.07.2012, M.A. Fadeeva, PTZ. 53. Chaenotheca chlorella (Ach.) Müll. Arg. – Tambitsy-NW towards Kaskoselga, herbrich - grassy swamp forest, on birch snag, 28.08. 2013, K. Syrjänen, TUR; Tambitsy-SW, mires NW of Kurnejnavolok cape, on old Salix pentandra, 27.08. 2013, K. Syrjänen, TUR; Polya village – S, on old birch, 25.08.2013, K. Syrjänen, TUR. 54. Chaenotheca chrysocephala (Turner ex Ach.) Th. Fr. – Vainio 1927; Fadeeva 2013; Podyelniki, on spruce, 07.07.2012, M.A. Fadeeva, PTZ. 55. Chaenotheca ferruginea (Turner ex Sm.) Mig. – Norrlin 1876; Vainio 1927; Fadeeva 2013; western shore of Lake Vekhkozero, on bark of spruce, 11.07.2012, M.A. Fadeeva, PTZ. 56. Chaenotheca furfuracea (L.) Tibell – Vainio 1927; Fadeeva 2000; Fadeeva & Kravchenko 2013; south-eastern shore of Lake Vekhkozero, on spruce along brook, 11.07.2012, M.A. Fadeeva, PTZ. 57. Chaenotheca gracilenta (Ach.) Mattsson & Middelb. – Polya village, on roots of fallen spruce, 26.06.2013, M.A. Fadeeva, PTZ; Polya village -S, decaying stump, 25.08. 2013, K. Syrjänen, TUR. 58. Chaenotheca laevigata Nádv. – Surroundings of Zubovo village, on stump of Salix caprea, 04.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013. 59. Chaenotheca subroscida (Eitner) Zahlbr. – Lipovitsy, along a brook, on stump of birch, 25.06.2013, M.A. Fadeeva, PTZ. 60. Chaenotheca trichialis (Ach.) Th. Fr. – Vainio 1927; surroundings of Zubovo village, on stump of pine, 04.07.2012, M.A. Fadeeva, PTZ. 212 Reports of the Finnish Environment Institute 40 | 2014 61. Chaenotheca xyloxena Nádv. – Surroundings of Zubovo village, on stump of Salix caprea, 04.07.2012, M.A. Fadeeva, PTZ. 62. *Chaenothecopsis hospitans (Th. Fr.) Tibell – “Ad Dianova-gora, saxicola, Simming, 1863”: Norrlin 1876; Vainio 1927; Zhurbenko & Ahti 2005. 63. Chrysothrix chlorina (Ach.) J. R. Laundon – Fadeeva 2013; Podyelniki, on stones in the wall around old chapel, 10.07.2012, M.A. Fadeeva, PTZ. 64. Circinaria caesiocinerea (Nyl. ex Malbr.) A. Nordin et al. – Fadeeva 2000. 65. Cladonia amaurocraea (Flörke) Schaer. – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ; northern shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 66. Cladonia arbuscula (Wallr.) Flot. – Fadeeva 2000; Tolpysheva et al. 2001; Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ; northern shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 67. Cladonia mitis Sandst. – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, northern shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 68. Cladonia bacilliformis (Nyl.) Glück – Podyelniki, on dry Juniperus communis, 10.07.2012, M.A. Fadeeva, PTZ. 69. Cladonia botrytes (K. G. Hagen) Willd. – Tolpysheva et al. 2001; Podyelniki, on roots of fallen spruce, 07.07.2012, M.A. Fadeeva, PTZ. 70. Cladonia cenotea (Ach.) Schaer. – Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ. 71. Cladonia chlorophaea (Flörke ex Sommerf.) Spreng. – Fadeeva 2013; Northern end of Kizhi Island, abandoned ield, on stones, 28.05.1999, M.A. Fadeeva, PTZ; Rechka abandoned village, on ground, 04.07.2012, M.A. Fadeeva, PTZ. 72. Cladonia coccifera (L.) Willd. – Fadeeva 2013; northern shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 73. Cladonia coniocraea (Flörke) Spreng. – Fadeeva 2013; surroundings of Zubovo village, on bark of pine, 03.07.2012, M.A. Fadeeva, PTZ. 74. Cladonia cornuta (L.) Hoffm. s.l. – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, northern shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 75. Cladonia crispata (Ach.) Flot. var. crispata – Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ. 76. Cladonia deformis (L.) Hoffm. – Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ. 77. Cladonia decorticata (Flörke) Spreng. – Fadeeva 2013. 78. Cladonia imbriata (L.) Fr. – Tolpysheva et al. 2001; Fadeeva 2013; Zubovo village, on Salix caprea, 03.10.2012, M.A. Fadeeva, PTZ; Podyelniki, on roots of fallen spruce, 07.07.2012, M.A. Fadeeva, PTZ. 79. Cladonia furcata (Huds.) Schrad. – Fadeeva 2000, 2013; NW shore of Lake Vekhkozero, on moss-covered stones in the rock wall (seismic dislocation), 11. 07.2012, M.A. Fadeeva, PTZ 80. Cladonia gracilis (L.) Willd. ssp. turbinata (Ach.) Ahti – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 08.07.2012, NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11. 07.2012, M.A. Fadeeva, PTZ. 81. Cladonia macilenta Hoffm. – Fadeeva 2013. 82. Cladonia phyllophora Hoffm. – Volkostrov Island, on soil, 31.05.1999, M.A. Fadeeva, PTZ; Podyelniki, abandoned ield, on moss-covered stones, 08.07.2012, M.A. Fadeeva, PTZ. Reports of the Finnish Environment Institute 40 | 2014 213 83. Cladonia pleurota (Flörke) Schaer. – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 08.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11. 07.2012, M.A. Fadeeva, PTZ. 84. Cladonia pocillum (Ach.) Grognot – Fadeeva 2013. 85. Cladonia pyxidata (L.) Hoffm. – Tolpysheva et al. 2001; Northern end of Ersenevo village, stone shore of Lake Onega, on ground, 05.07.2012, M.A. Fadeeva, PTZ. 86. Cladonia rangiferina (L.) F. H. Wigg. – Tolpysheva et al. 2001; Fadeeva 2000, 2013; Podyelniki, abandoned ield, on moss-covered stones, 08.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11. 07.2012, M.A. Fadeeva, PTZ. 87. Cladonia squamosa Hoffm. – Fadeeva 2013; NW shore of Lake Vekhkozero, on moss-covered stones in the rock wall (seismic dislocation), 11.07.2012, M.A. Fadeeva, PTZ. 88. Cladonia stellaris (Opiz) Pouzar & Vězda – Fadeeva 2000, 2013; Podyelniki, abandoned ield, on moss-covered stones, 08.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11. 07.2012, M.A. Fadeeva, PTZ. 89. Cladonia stygia (Fr.) Ruoss – Fadeeva 2013. 90. Cladonia subulata (L.) F. H. Wigg. – Fadeeva 2013; Zubovo village, on stones in abandoned ield, 03.10.2012, M.A. Fadeeva, PTZ. 91. Cladonia sulphurina (Michx.) Fr. – Zubovo village, on stones in abandoned ield, 03.10.2012, M.A. Fadeeva, PTZ. 92. Cladonia symphycarpa (Flörke) Fr. – Yuzhny Oleny Island, on dolomites, 20.07.2000, M.A. Fadeeva, PTZ. 93. Cladonia turgida Hoffm. – Fadeeva 2013; NW shore of Lake Vekhkozero on moss-covered stones in the rock wall (seismic dislocation), 11. 07.2012, M.A. Fadeeva, PTZ. 94. Cladonia uncialis (L.) F. H. Wigg. ssp. uncialis – Fadeeva 2000, 2013; NW shore of Lake Vekhkozero, on moss-covered stones in the rock wall (seismic dislocation), 11. 07.2012, M.A. Fadeeva, PTZ. 95. Cladonia verticillata (Hoffm.) Schaer. – Podyelniki, abandoned ield, on mosscovered stones, 10.07.2012, M.A. Fadeeva, 2012 PTZ. 96. Collema laccidum (Ach.) Ach. – Kuzaranda village, on marble, 04.07.2004, M.A. Fadeeva, PTZ. 97. Collema furfuraceum (Arnold) Du Rietz – Fadeeva 2013. 98. Coenogonium luteum (Dicks.) Kalb & Lücking – Nylander 1866 a; Norrlin 1876. 99. Coenogonium pineti (Ach.) Lücking & Lumbsch – Nylander 1866 a; Norrlin 1876; Tambitsy-NW towards Kaskoselga, swamp forest close to the bog, on birch snag, 28.08.2013, K. Syrjänen, TUR. 100. Cyphelium karelicum (Vain.) Räsänen – Nylander 1866 ; Norrlin 1876; Vainio, 1922. 101. Dendriscocaulon umhausense (Auersw.) Degel. – Norrlin 1876. 102. Dermatocarpon luridum (With.) J.R. Laundon – Norrlin 1876. 103. Dermatocarpon miniatum (L.) W. s.l. – Ashepnavolok Cape, 08.1870, J.P. Norrlin, . 104. Diploschistes scruposus (Schreb.) Norman – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ. 105. Enchylium polycarpon (Hoffm.) Otálora et al. – Fadeeva 2013. 106. Epilichen scabrosus (Ach.) Clem. – Dianova Gora, on Baeomyces rufus, A. Kullhem, H: Norrlin 1876; Zhurbenko & Ahti 2005. 107. Evernia divaricata (L.) Ach. – western shore of Bol. Klim. Isl., [Kishi (Vatnavolok)], on spruce twigs, 1863, A. Kullhem, H: Norrlin 1876; Lipovitsy, along the brook, on spruce twigs, 25.06.2013, M.A. Fadeeva, PTZ; Polya village, on spruce twigs, 26.06.2013, M.A. Fadeeva, PTZ; Uzkaya Salma, on spruce twigs, 28.06.2013, M.A. Fadeeva, PTZ; Tambitsy-SW, mires to the NW of the cape Kurnejnavolok, 214 Reports of the Finnish Environment Institute 40 | 2014 herb-rich – grassy swamp forests at border of a pine bog, on twigs of spruces, 27.08.2013, K. Syrjänen, TUR; Polya village –S, herb-rich swamp forest, on old birch, 25.08. 2013, K. Syrjänen, TUR; Velikaya Guba -SW, Zubovo –N, North east from Lake Pužej, open mire below an east facing cliff, on birch, 24.08.2014, K. Syrjänen, TUR; Tambitsy -N. W-NW from the small cape Tolstyj Navolok, swamp forest, on trunk of Alnus glutinosa, 26.8.2013, K. Syrjänen, TUR. 108. Evernia mesomorpha Nyl. – Fadeeva 2013; Fadeeva & Kravchenko 2013; surroundings of Zubovo village, on bark of pine, Salix caprea, Juniperus, birch, 03.07.2013, M.A. Fadeeva, PTZ; on bark of pine, surroundings of Lake Rugozero Lake, 27.06.2013, M.A. Fadeeva, PTZ; Uzkaya Salma, on bark of pine, Juniperus comminis, 28.06.2013, M.A. Fadeeva, PTZ; Velikaya Guba -SW, Zubovo –N, northeast from Lake Pužej, open oligotropic mire, on trunk of birch, 24.08.2013, K. Syrjänen, TUR. 109. Evernia prunastri (L.) Ach. – Tolpysheva et al. 2001; west of Zubovo village, on Sorbus aucuparia, 03.07.2012, M.A. Fadeeva, PTZ. 110. Fuscidea pusilla Tønsberg – Fadeeva 2013. 111. Fuscopannaria praetermissa (Nyl.) P. M. Jørg. – Fadeeva 2013; NW shore of Lake Vekhkozero, on moss-covered stones in the rock wall (seismic dislocation), 11. 07.2012, M.A. Fadeeva, PTZ. 112. Graphis scripta (L.) Ach. – Bol. Klim. Isl., on bark of Salix, 12.06.1863, Th. Simming, H: Nylander 1866 a; Norrlin 1876; NE end of Bol. Klim. Isl., on dry Sorbus aucuparia, 27.05.1999, M.A. Fadeeva, PTZ. 113. Gyalecta fagicola (Hepp ex Arnold) Kremp. – Fadeeva 2001, 2003, s.n. Gyalecta truncigena (Ach.) Hepp; Fadeeva 2013; eastern shore Kizhi Island, north of Yamka village, on old trees of Ulmus laevis, 27.05.1999, M.A. Fadeeva, PTZ; North to Zubovo village, on aspen, 04.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013. 114. Gyalecta truncigena (Ach.) Hepp – 4 km N to Velikaya Guba village, on trunk of old aspen, 26.06.2013, M.A. Fadeeva, PTZ. 115. Gyalecta ulmi (Sw.) Zahlbr. – Dianova Gora, 1863, Th. Simming, H; Lipovitsy village –SW, to the west of Lake Bezdonnoe, brook-side herb-rich deciduous forest, on old Ulmus, 23.08. 2013, K. Syrjänen, TUR. 116. Gyalolechia lavorubescens (Huds.) Søchting et al. – Tolpysheva et al. 2001. 117. *Homostegia piggotii (Berk. et Broome) P. Karst. – Dianova Gora, on Parmelia saxatilis, 1870, J.P. Norrlin, H: Zhurbenko & Ahti 2005. 118. Hypocenomyce scalaris (Ach.) M.Choisy – Fadeeva 2013; NW shore of Lake Vekhkozero, on bark of pine, M.A. Fadeeva, 11.07.2012, PTZ. 119. Hypogymnia physodes (L.) Nyl. – Tolpysheva et al. 2001; Fadeeva 2000, 2013; Zubovo village, on spruce, pine, 03.07.2012, M.A. Fadeeva, PTZ; Zubovo village, on trunk of Alnus glutinosa, 03.07.2012, M.A. Fadeeva, PTZ. 120. Hypogymnia tubulosa (Schaer.) Hav. – Tolpysheva et al. 2001; Fadeeva 2000, 2013; Pustoy Bereg abandoned village, on birch, 04.07.2012, M.A. Fadeeva, PTZ. 121. Hypogymnia vittata (Ach.) Parrique – Norrlin 1876; Komlevo abandoned village, on moss-covered basement rocks, 17.08.2010, M.A. Fadeeva, PTZ. 122. Icmadophila ericetorum (L.) Zahlbr. – Norrlin 1876. 123. Immersaria cupreoatra (Nyl.) Calat. & Rambold – Norrlin 1876. 124. Imshaugia aleurites (Ach.) S. L. F. Mey. – Podyelniki, on bark of pine, 10.07.2012, M.A. Fadeeva, PTZ. 125. Lathagrium fuscovirens (With.) Otálora et al. – Fadeeva 2013. 126. Lasallia pustulata (L.) Mérat – Fadeeva 2013. 127. Lecania cyrtella (Ach.) Th.Fr. – Tolpysheva et al. 2001. 128. Lecanora allophana Nyl. – Fadeeva 2013; surroundings of Zubovo village, on old aspens, 04.07.2012, M.A. Fadeeva, PTZ. Reports of the Finnish Environment Institute 40 | 2014 215 129. Lecanora argopholis (Ach.) Ach. – Norrlin 1876. 130. Lecanora dispersa (Pers.) Sommerf. s.l. – Norrlin 1876. 131. Lecanora fuscescens (Sommerf.) Nyl. – Norrlin 1876. 132. Lecanora hagenii (Ach.) Ach. – Tolpysheva et al. 2001. 133. Lecanora intricata (Ach.) Ach. – Podyelniki, on stones, 08.07.2012, M.A. Fadeeva, PTZ. 134. Lecanora leptyrodes (Nyl.) G.B.F. Nilsson – Fadeeva 2000; North to Oyatevshina village, on aspen, 05.07.2012, M.A. Fadeeva, PTZ. 135. Lecanora muralis (Schreb.) Rabenh. – Fadeeva 2013; North to Ersenevo village, on stones in the abandoned ield, 05.07.2012, M.A. Fadeeva, PTZ. 136. Lecanora pulicaris (Pers.) Ach. – Tolpysheva et al. 2001. 137. Lecanora rupicola (L.) Zahlbr. – Fadeeva 2001; Zhurbenko & Ahti 2005. 138. Lecanora saligna (Schrad.) Zahlbr. – Tolpysheva et al. 2001. 139. Lecanora symmicta (Ach.) Ach. s.l. – Severnye Oleny Island, on birch, 29.05.1999, M.A. Fadeeva, PTZ; Podyelniki, on dry Juniperus communis, 08.07.2012, M.A. Fadeeva, PTZ. 140. Lecanora varia (Hoffm.) Ach. – Tolpysheva et al. 2001. 141. Lecidea conluens (Weber) Ach. – Vainio 1934. 142. Lecidea erythrophaea Flörke ex Sommerf. – Norrlin 1876; Tolpysheva et al. 2001; Fadeeva 2013; Severnye Oleny Island, on aspen, 29.05.1999, M.A. Fadeeva, PTZ. 143. Lecidea leprarioides Tønsberg – Lipovitsy, along the brook, on bark of spruce, 25.06.2013, M.A. Fadeeva, PTZ. 144. Lecidea lapicida (Ach.) Ach. var. pantherina Ach. – Norrlin 1876; Vainio 1934. 145. Lecidea tessellata Flörke – Norrlin 1876. 146. Lepraria membranacea (Dicks.) Vain. – Fadeeva 2013. 147. Leproplaca obliterans (Nyl.) Arup et al. – Norrlin 1876. 148. Leptogium saturninum (Dicks.) Nyl. – Fadeeva 2000, 2013; Fadeeva & Kravchenko 2013; surroundings of Zubovo village, on bark of aspen, 03.07.2012, M.A. Fadeeva, PTZ; Polya village, on bark of aspen, 26.06.2013, M.A. Fadeeva, PTZ; 149. Lichenomphalia umbellifera (L. : Fr.) Redhead & al. – Fadeeva 2013. 150. Lobaria pulmonaria (L.) Hoffm. – Fadeeva 2000, 2013; surroundings of Zubovo village, on Populus tremula, Sorbus aucuparia and Juniperus communis, 03.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; surroundings of Zubovo village, on Salix caprea, 04.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Podyelniki, on old aspens, 10.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on aspen, 11.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; NW shore of Lake Vekhkozero, on Salix caprea, 11.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko, 2013; Lipovitsy, along the brook, on drying Sorbus aucuparia, 25.06.2013, M.A. Fadeeva, PTZ; Polya village, stump of Salix caprea, 26.06.2013, M.A. Fadeeva, PTZ; Tambitsy N, W-NW from the small cape Tolstyj Navolok, mixed herb-rich forest, fallen on ground from a large aspen, with sporophytes, 26.08. 2013, K. Syrjänen, TUR. 151. Lobaria scrobiculata (Scop.) DC. – Fadeeva 2013; Lipovitsy, along the brook, on drying Sorbus aucuparia, 25.06.2013, M.A. Fadeeva, PTZ. 152. Lobothallia melanaspis (Ach.) Hafellner – Bolshoi Lelikovsky Island, Radkolye Cape, on shore rocks, 06.07.2004, M.A. Fadeeva, PTZ. 153. Lopadium coralloideum (Nyl.) Lynge – Norrlin 1876; Vainio 1922. 154. Lopadium disciforme (Flot.) Kullh. – Lipovitsy, along the brook, on bark of spruce, 25.06.2013, M.A. Fadeeva, PTZ. 155. Loxospora elatina (Ach.) A. Massal. – Podyelniki, on bark of Juniperus communis, 10.07.2012, M.A. Fadeeva, PTZ. 216 Reports of the Finnish Environment Institute 40 | 2014 156. Megaspora verrucosa (Ach.) Hafellner & V. Wirth – surroundings of Zubovo village, on old aspens, 03.07.2012, M.A. Fadeeva, PTZ: Fadeev & Kravchenko 2013; 157. Melanelia hepatizon (Ach.) A. Thell. – Fadeeva 2013; Shunga, 1870, J.P. Norrlin, ; Podyelniki, abandoned iels, on stones, 10.07.2012, M.A. Fadeeva, PTZ. 158. Melanelia stygia (L.) Essl. – Fadeeva 2013. 159. Melanelixia fuliginosa (Fr. ex Duby) O.Blanco et al. – Fadeeva 2013. 160. Melanelixia subaurifera (Nyl.) O. Blanco & al. – Dianova Gora, 1863, A. Kullhem, H; between Tipinitsy village and Varnavolok Cape, on aspen, 04.07.2004, M.A. Fadeeva, PTZ; North to Zubovo village, on Sorbus aucuparia, 03.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013. 161. Melanohalea exasperata (De Not.) O. Blanco & al. – Fadeeva 2000; Tolpysheva et al. 2001; Fadeeva & Kravchenko 2013; Paleostrov Island, on Tilia cordata, 03.07.2004, M.A. Fadeeva, PTZ; North to Zubovo village, on Sorbus aucuparia, Prunus padus, Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ. 162. Melanohalea exasperatula (Nyl.) O. Blanco & al. – The northern end of Kizhi Island, on Ulmus laevis, 30.05.1999, M.A. Fadeeva, PTZ. 163. Melanohalea olivacea (L.) O. Blanco & al. – Fadeeva 2000; Tolpysheva et al. 2000; surroundings of Zubovo village, on Salix caprea, on birch, 03.07.2012, M.A. Fadeeva, PTZ. 164. Melanohalea septentrionalis (Lynge) O. Blanco & al. – Tolpysheva et al. 2001. 165. Micarea denigrata (Fr.) Hedl. – North to Zubovo village, on stump of pine, 03.07.2012, M.A. Fadeeva, PTZ. 166. +Microcalicium arenarium (Hampe ex A. Massal.) Tibell – Lipovitsy, along the brook, on roots of fallen spruce, 25.06.2013, M.A. Fadeeva, PTZ. 167. *Microcalicium disseminatum (Ach.) Vain. – Rybya Bay of Lake Onega, on bark of spruce, 11.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Lipovitsy, along the brook, on bark of spruce, on Chaenotheca sp., 25.06.2013, M.A. Fadeeva, PTZ; Polya village, stump of birch, 26.06. 2013, M.A. Fadeeva, PTZ. 168. Montanelia disjuncta (Erichsen) Divakar et al. – Fadeeva 2013; Podyelniki, on stones, 08.07.2012, M.A. Fadeeva, PTZ. 169. Montanelia panniformis (Nyl.) Divakar et al. – Fadeeva 2013. 170. Montanelia sorediata (Ach.) Divakar et al. – Kizhi Island, on Kizhi church wall, 31.05.1999, M.A. Fadeeva, PTZ. 171. Mycobilimbia carneoalbida (Müll. Arg.) S.Ekman & Printzen – Fadeeva 2000, 2013; Rybya Bay of Lake Onega, on bark of aspen, 11.07.2012, M.A. Fadeeva, PTZ. 172. Mycobilimbia epixanthoides (Nyl.) Vitik. et al. ex Hafellner et Türk – Nylander 1866 a, b; Norrlin 1876; Vainio 1922; Fadeeva 2000, 2003, 2013; Zhurbenko & Ahti 2005; North to Zubovo village, on stump of aspen, 03.07.2012, M.A. Fadeeva, PTZ. 173. Mycobilimbia tetramera (De Not.) Vitik. et al. ex Hafellner & Türk – Vainio 1922. 174. Mycoblastus sanguinarius (L.) Norman – Fadeeva 2000, 2013. 175. +Mycocalicium subtile (Pers.) Szatala – Bol. Klim. Isl., 1863, Th. Simming, H. 176. Myriospora heppii (Nägeli ex Körb.) Hue – Norrlin 1876. 177. Myriospora smaragdula (Wahlenb. ex Ach.) Nägeli ex Uloth – Norrlin 1876. 178. Naetrocymbe punctiformis (Pers.) R. C. Harris – Norrlin 1876. 179. Nephroma bellum (Spreng.) Tuck. – North to Zubovo village, on aspen, Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on bark of aspen, 11.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Lipovitsy, along the brook, on drying Sorbus, 25.06.2013, M.A. Fadeeva, PTZ; Polya village -S, herb-rich swamp forest, on large Salix pentandra, 25.08. 2013, K. Syrjänen, TUR. Reports of the Finnish Environment Institute 40 | 2014 217 180. Nephroma parile (Ach.) Ach. – Fadeeva 2000, 2013; Fadeeva & Kravchenko 2013; North to Zubovo village, on aspen, 03.07.2012, M.A. Fadeeva, PTZ; Rybya Bay of Lake Onega, on bark of aspen, 11.07.2012, M.A. Fadeeva, PTZ. 181. Nephroma resupinatum (L.) Ach. – Fadeeva 2013; Fadeeva & Kravchenko 2013; Dianova Gora, 1863, Th. Simming, H; Rybya Bay of Lake Onega, on bark of aspen, 11.07.2012, M.A. Fadeeva, PTZ; Lipovitsy, along the brook, on drying Sorbus aucuparia, 25.06.2013, M.A. Fadeeva, PTZ. 182. Ochrolechia androgyna (Hoffm.) Arnold – Dianova Gora, 26.08.1863, Th. Simming, H. 183. Ophioparma ventosa (L.) Norman – Norrlin 1876; Fadeeva 2013; Gorodok Hill, on diabase, 27.06.1924, V. P. Savich & L. I. Savich-Lyubitskaya, LE. 184. Parmelia fraudans (Nyl.) Nyl. – Norrlin 1876; Fadeeva 2000, 2013; Podyelniki, on stones, 08.07.2012, M.A. Fadeeva, PTZ. 185. Parmelia saxatilis (L.) Ach. – Fadeeva 2000, 2013; Podyelniki, abandoned iels, on stones, 10.07.2012, M.A. Fadeeva, PTZ, NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 186. Parmelia sulcata Taylor – Tolpysheva et al. 2001; Fadeeva 2000, 2013; North to Zubovo village, on Sorbus aucuparia, Prunus padus, 03.07.2012, M.A. Fadeeva, PTZ. 187. Parmeliella triptophylla (Ach.) Müll. Arg – Norrlin 1876; Fadeeva 2013; Ashepnavolok Cape, 1870, J.P. Norrlin, H. 188. Parmelina tiliacea (Hoffm.) Hale – Fadeeva et al. 2007; Paleostrov Island, on Tilia cordata, 03.07.2004, M.A. Fadeeva, PTZ. 189. Parmeliopsis ambigua (Wulfen) Nyl. – Tolpysheva et al. 2001; Fadeeva 2013; North to Zubovo village, on Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ. 190. Parmeliopsis hyperopta (Ach.) Arnold – Tolpysheva et al. 2001; Podyelniki, on bark of pine, 10.07.2012, M.A. Fadeeva, PTZ. 191. Peltigera aphthosa (L.) Willd. – Fadeeva 2000, 2013; Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on moss-covered basement rocks, 11.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on moss-covered basement rocks, 11.07.2012, M.A. Fadeeva, PTZ. 192. Peltigera canina (L.) Willd. – Fadeeva 2000, 2013; Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on base of old aspen, 11.07.2012, M.A. Fadeeva, PTZ; Lipovitsy, on aspen, 27.06.2013, M.A. Fadeeva, PTZ. 193. Peltigera collina (Ach.) Schrad. – Bol. Klim. Isl., on stony shore among mosses, 25.06.2007, M.A. Fadeeva, PTZ. 194. Peltigera didactyla (With.) J. R. Laundon – Fadeeva 2013. 195. Peltigera latiloba Holt.-Hartw. – Fadeeva 2013. 196. Peltigera lepidophora (Nyl. ex Vain.) Bitter – Fadeeva 2000, 2013. 197. Peltigera leucophlebia (Nyl.) Gyeln. – Fadeeva 2000, 2013; Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on moss-covered basement rocks, 11.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on moss-covered stones in the rock wall (seismic dislocation), 11. 07.2012, M.A. Fadeeva, PTZ. 198. Peltigera malacea (Ach.) Funck – Fadeeva 2013. 199. Peltigera membranacea (Ach.) Nyl. – NE end of Bol. Klim. Isl., on moss-covered stones, 27.05.1999, M.A. Fadeeva, PTZ. 200. Peltigera neckeri Hepp ex Müll. Arg. – Fadeeva 2000; Kizhi Island, Yamka village, the shore of Lake Onega, on soil, 27.05.1999, M.A. Fadeeva, PTZ; Bol. Klim. Isl., on base of aspen trunk, 27.05.1999, M.A. Fadeeva, PTZ. 201. Peltigera neopolydactyla (Gyeln.) Gyeln. – Bol. Klim. Isl., on dead wood, 29.05.1999, M.A. Fadeeva, PTZ, Rybya Bay of Lake Onega, on moss-covered basement rocks, 11.07.2012, M.A. Fadeeva, PTZ. 218 Reports of the Finnish Environment Institute 40 | 2014 202. Peltigera occidentalis (Å. E. Dahl) Kristinsson – Bol. Klim. Isl., Lukovo Bay, 05.07.2004, P. Uotila, H; Bolshoi Lelikovsky Island, Radkolye Cape, on moss-covered basement rocks, 06.07.2004, M.A. Fadeeva, PTZ. 203. Peltigera polydactylon (Neck.) Hoffm. – Fadeeva 2000, 2013; south-eastern shore Lake Vekhkozero, on moss-covered basement rocks, 11.07.2012, M.A. Fadeeva, PTZ. 204. Peltigera praetextata (Flörke ex Sommerf.) Zopf – Fadeeva 2000, Fadeeva & Kravchenko 2013; surroundings of Zubovo village, on base of aspen, 03.07.2012, M.A. Fadeeva, PTZ; North to Oyatevshina village, on aspen, 05.07.2012, M.A. Fadeeva, PTZ; Lipovitsy, on aspen, 25.06.2013, M.A. Fadeeva, PTZ; Polya village, on stump of Salix caprea, 26.06.2013, M.A. Fadeeva, PTZ. 205. Peltigera rufescens (Weiss) Humb. – Fadeeva 2000, 2013; Bol. Klim. Isl., dry meadow, abandoned ield, on stones, 27.05.1999, M.A. Fadeeva, PTZ, Bol. Klim. Isl., Konda, 06.07.2004, P. Uotila, H; North to Ersenevo village, stony shore of Lake Onega, 05.07.2012, M.A. Fadeeva, PTZ. 206. Peltigera scabrosa Th. Fr. – Fadeeva 2013. 207. Peltigera venosa (L.) Hoffm. – Fadeeva 2013. 208. Pertusaria albescens (Huds.) M. Choisy & Werner – Podyelniki, 10.07.2012, M.A. Fadeeva, 2012, PTZ. 209. Pertusaria amara (Ach.) Nyl. – Tolpysheva et al. 2001; Fadeeva 2013; North to Zubovo village, on aspen, 04.07.2012, M.A. Fadeeva, PTZ. 210. Pertusaria chiodectonoides Bagl. ex A. Massal. – Norrlin 1876. 211. Phaeophyscia ciliata (Hoffm.) Moberg – Kainos Island (NE fromTolvuya), on aspen, 03.07.2004, P. Uotila, ; North to Oyatevshina village, clear-cut for new road, on aspen, 05.07.2012, M.A. Fadeeva, PTZ. 212. Phaeophyscia orbicularis (Neck.) Moberg – Fadeeva 2000; Shunga, on rock, 1870, J.P. Norrlin, H, Kizhi Island, 2 km to the North from the church, on trunk of Ulmus laevis, 26.05. 1999, M.A. Fadeeva, PTZ. 213. Phaeophyscia sciastra (Ach.) Moberg – Bolshoi Lelikovsky Isl., on stony shore of Lake Onega, 06.07.2004, M.A. Fadeeva, PTZ. 214. Phlyctis argena (Spreng.) Flot. – Fadeeva 2000, 2013; North to Zubovo village, on aspen, 03.07.2012, M.A. Fadeeva, PTZ. 215. Phylliscum demangeonii (Moug. & Mont.) Nyl. – Norrlin 1876. 216. Physcia adscendens (Fr.) H. Olivier – Fadeeva 2000; Shunga, 1870, J.P. Norrlin, H; Kainos Island (NE from Tolvuya), on aspen, 03.07.2004, P. Uotila, ; Pustoy Bereg abandoned village, on Ulmus laevis, 04.07.2012, M.A. Fadeeva, PTZ. 217. Physcia aipolia (Ehrh. ex Humb.) Fürnr. – Fadeeva 2000, 2013; Pustoy Bereg abandoned village, on Ulmus laevis, 04.07.2012, M.A. Fadeeva, PTZ. 218. Physcia alnophila (Vain.) Loht., Moberg, Myllys & Tehler – Fadeeva 2013; West to Zubovo village, 03.07.2012, M.A. Fadeeva, PTZ. 219. Physcia caesia (Hoffm.) Fürnr. – Tolpysheva et al. 2001; Fadeeva 2000; Podyelniki, on stone wall of the chapel, 08.07.2012, M.A. Fadeeva, PTZ. 220. Physcia dubia (Hoffm.) Lettau – Pustoy Bereg abandoned village, on Ulmus laevis, 04.07.2012, M.A. Fadeeva, PTZ. 221. Physcia phaea (Tuck.) J. W. Thomson – Norrlin 1876. 222. Physcia stellaris (L.) Nyl. – Fadeeva 2000. 223. Physcia subalbinea Nyl. – Fadeeva 2013. 224. Physcia tenella (Scop.) DC. – Norrlin 1876; Fadeeva 2000; Pustoy Bereg abandoned village, on Ulmus laevis, 04.07.2012, M.A. Fadeeva, PTZ. 225. Physconia detersa (Nyl.) Poelt – Shunga, on rock, 1870, J.P. Norrlin, ; Podyelniki, on old aspens, 10.07.2012, M.A. Fadeeva, PTZ. Reports of the Finnish Environment Institute 40 | 2014 219 226. Physconia distorta (With.) J. R. Laundon – Eastern shore Kizhi Island, on old Ulmus, 27.05. 1999, M.A. Fadeeva, PTZ. 227. Physconia enteroxantha (Nyl.) Poelt – Eastern shore Kizhi Island, on old Ulmus, 27.05. 1999, M.A. Fadeeva, PTZ. 228. Physconia perisidiosa (Erichsen) Moberg – Fadeeva 2013; eastern shore Kizhi Island, on old Ulmus, 27.05.1999, M.A. Fadeeva, PTZ. 229. Pilophorus cereolus (Ach.) Th. Fr – Nylander 1866 a; Norrlin 1876. 230. Placynthiella icmalea (Ach.) Coppins & P. James – Norrlin 1876; Fadeeva 2013; Podyelniki, on roots of fallen spruce, 06.07.2012, M.A. Fadeeva, PTZ; same place, on fallen pine, 10.07.2012, M.A. Fadeeva, PTZ. 231. Placynthium nigrum (Huds.) Gray – Norrlin 1876. 232. Platismatia glauca (L.) W. L. Culb. & C. F. Culb. – Tolpysheva et al. 2001; Fadeeva 2013; Zubovo village, on spruce, 03.07.2012, M.A. Fadeeva, PTZ. 233. Polycauliona candelaria (L.) Frödén et al. – Tolpysheva et al. 2001; Fadeeva 2000; Pustoy Bereg abandoned village, on birch, 04.07.2012, M.A. Fadeeva, PTZ. 234. Polycauliona polycarpa (Hoffm.) Frödén et al. – Fadeeva 2000. 235. Polychidium muscicola (Sw.) Gray – Fadeeva 2013. 236. Porpidia tuberculosa (Sm.) Hertel & Knoph – Shunga, 1870, J.P. Norrlin, H. 237. Protoblastenia rupestris (Scop.) J. Steiner – Norrlin 1876. 238. Protoparmelia badia (Hoffm.) Hafellner – NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 239. Pseudevernia furfuracea (L.) Zopf – Tolpysheva et al. 2001; Fadeeva 2013; Podyelniki, on pine, 10.07.2012, M.A. Fadeeva, PTZ. 240. Psilolechia clavulifera (Nyl.) Coppins – Lipovitsy, along the brook, on roots of fallen spruce, 25.06.2013, M.A. Fadeeva, PTZ. 241. Psilolechia lucida (Ach.) M. Choisy – Klimenitsky Monastery, 12.06.1863, Th. Simming, H; Podyelniki, on stones, 08.07.2012, M.A. Fadeeva, PTZ. 242. Pyrenopsis pleiobola Nyl. – Norrlin 1876. 243. Ramalina baltica Lettau – Velikaya Guba, 1870, J.P. Norrlin, H: Norrlin 1876; Paleostrov Island, on old Tilia cordata, 03.07.2004, M.A. Fadeeva, PTZ; Lipovitsy, on old aspen, 25.06.2013, M.A. Fadeeva, PTZ. 244. Ramalina dilacerata (Hoffm.) Hoffm. – Fadeeva 2013; North to Zubovo village, on Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Oyatevshina village, on Salix caprea, 05.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Lipovitsy, along the brook, on drying Sorbus aucuparia, 25.06.2013, M.A. Fadeeva, PTZ. 245. Ramalina farinacea (L.) Ach. – Fadeeva 2013; surroundings of Zubovo village, on aspen, 03.07.2012, M.A. Fadeeva, PTZ; Podyelniki, on stone in the wall around old chapel, 10.07.2012, M.A. Fadeeva, PTZ. 246. Ramalina pollinaria (Westr.) Ach. – Fadeeva 2000; Podyelniki, on stone in the wall around old chapel, 10.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on stone wall, 11. 07.2012, M.A. Fadeeva, PTZ. 247. Ramalina sinensis Jatta – Fadeeva 2013; Bol. Klim. Isl., on trunk of Sorbus aucuparia, 19.07.2000, M.A. Fadeeva, PTZ. 248. Ramalina thrausta (Ach.) Nyl. – Norrlin 1876. 249. Ramboldia elabens (Fr.) Kantvilas & Elix – Vainio 1934. 250. Rhizocarpon geographicum (L.) DC. s.l. – Fadeeva 2013; Bolshoi Lelikovsky Island, Radkolye Cape, on shore rocks, 06.07.2004, M.A. Fadeeva, PTZ; 251. Rhizocarpon polycarpum (Hepp) Th. Fr. – Norrlin 1876. 252. Rimularia insularis (Nyl.) Rambold & Hertel (obligate lichenicolous lichen) – Nylander 1866 a; Norrlin 1876; Vainio 1934; Hertel 1970; Fadeeva 2001 a; Zhurbenko & Ahti 2005. 220 Reports of the Finnish Environment Institute 40 | 2014 253. Rinodina archaea (Ach.) Arnold – Norrlin 1876. 254. Rinodina confragosa (Ach.) Körb. – Shunga, on diorites in pock’s crashes, in shadow, 1876, J.P. Norrlin, H: Norrlin 1876. 255. Rinodina pyrina (Ach.) Arnold – Fadeeva 2000. 256. Sclerophora pallida (Pers.) Y. J. Jao & Spooner – Lipovitsy village SW, W of Lake Bezdonnoe, brook-side herb-rich deciduous forest, on old Ulmus, 24.8.2013, K. Syrjänen, TUR. 257. Sclerophora coniophaea (Norman) J. Mattsson & Middelb. – Velikaya Guba – SW, Zubovo –N, NE of Lake Pužej, spruce swamp – mixed herb-rich forest at E-base of siliceous cliff, on birch snag, abundant, 24.8.2013, K. Syrjänen, TUR; Tambitsy NW towards Kaskoselga, herb-rich – grassy swamp forest, on birch snag, 28.08.2013, K. Syrjänen, TUR. 258. Scoliciosporum chlorococcum (Graewe ex Stenh.) Vězda – Eastern shore Kizhi Island, Yamka village, about 0,5 km to the North, on pine, abundant, 28.05.1999, M.A. Fadeeva, PTZ. 259. Scytinium fragrans (Sm.) Otálora et al. – Fadeeva 2013. 260. Scytinium gelatinosum (With.) Otálora et al. – Norrlin 1876; Yuzhny Oleny Island, on dolomites, M.A. Fadeeva, 05.07.2004, PTZ. 261. Scytinium lichenoides (L.) Otálora et al. – Fadeeva 2013. 262. Scytinium plicatile (Ach.) Otálora et al. – Fadeeva 2013. 263. Scytinium teretiusculum (Wallr.) Otálora et al. – Fadeeva 2013; Lipovitsy, along the brook, on bark of aspen, 25.06.2013, M.A. Fadeeva, PTZ. 264. Spilonema paradoxum Bornet – Norrlin 1876. 265. Spilonema revertens Nyl. – Norrlin 1876. 266. Staurothele frustulenta Vain. – Vainio 1921. 267. +Stenocybe pullatula (Ach.) Stein – Fadeeva 2013. 268. Stereocaulon evolutum Graewe – Norrlin 1876. 269. Stereocaulon grande (H. Magn.) H. Magn. – Fadeeva 2013. 270. Stereocaulon saxatile H. Magn. – Fadeeva 2013; Ersenevo village, stony shore of Lake Onega, M.A. Fadeeva, 05.07.2012, PTZ. 271. Stereocaulon subcoralloides (Nyl.) Nyl. – Fadeeva 2013; on stone basement of old main church of Kizhi, 31.05.1999, M.A. Fadeeva, PTZ. 272. Stereocaulon tomentosum Fr. – Fadeeva 2013. 273. Strangospora moriformis (Ach.) Stein – Tolpysheva et al. 2001. 274. Strigula stigmatella (Ach.) R. C. Harris – Nylander 1866 a, Norrlin 1876; Vainio 1921. 275. Tephromela atra (Huds.) Hafellner M.A. – Podyelniki, on stones, 10.07.2012, M.A. Fadeeva, PTZ. 276. Tetramelas insignis (Nägeli ex Hepp) Kalb. – Norrlin 1876. 277. Thamnolia vermicularis (Sw.) Schaer. – Velikaya Guba -SW, Zubovo -N, NE of Lake Pužej. East facing siliceus cliff-wall and boulder scree above an open mire, on many boulders – Locally rather common, 24.08.2013, K. Syrjänen, TUR. 278. Thermutis velutina (Ach.) Flot. – Norrlin 1876. 279. Toninia squalida (Ach.) A. Massal. – Azhepnavolok Cape, on mosses, 1870, J. . Norrlin, H: Norrlin 1876; Vainio 1922. 280. Trapelia glebulosa (Sm.) J. R. Laundon – Velikaya Guba, on schist, 1870, J. . Norrlin, H: Norrlin 1876, s.n. Lecidea coarctata Ach.; Vainio 1934. 281. Trapeliopsis granulosa (Hoffm.) Lumbsch – Norrlin 1876; Podyelniki, on roots of fallen spruce, 06.07.2012, M.A. Fadeeva, PTZ. 282. Tuckermanopsis chlorophylla (Willd.) Hale – Fadeeva 2000; Tolpysheva et al. 2001; Podyelniki, on stones, 10.07. 2012, M.A. Fadeeva, PTZ. Reports of the Finnish Environment Institute 40 | 2014 221 283. Umbilicaria deusta (L.) Baumg. – Fadeeva 2000; 2013; Ersenevo village, stony shore of Lake Onega, 05.07.2012, M.A. Fadeeva, PTZ. 284. Umbilicaria hirsuta (Sw. ex Westr.) Hoffm. – Fadeeva 2013. 285. Umbilicaria hyperborea (Ach.) Hoffm. – Fadeeva 2013; Podyelniki, shore Lake Onega, on stones, 10.07.2012, M.A. Fadeeva, PTZ. 286. Umbilicaria torrefacta (Lightf.) Schrad. – Fadeeva 2013. 287. Umbilicaria vellea (L.) Hoffm. – Fadeeva 2013. 288. Usnea barbata (L.) Weber ex F.H.Wigg. – Lipovitsy, along the brook, on spruce, 25.06.2013, M.A. Fadeeva, PTZ. 289. Usnea dasypoga (Ach.) Röhl. – Tolpysheva et al. 2001; south-western shore of Lake Vekhkozero, on spruce, 11.07.2012, M.A. Fadeeva, PTZ. 290. Usnea glabrescens (Nyl. ex Vain.) Vain. – Tolpysheva et al. 2001. 291. Usnea hirta (L.) F. H. Wigg. – Tolpysheva et al. 2001; Fadeeva 2000, Podyelniki, on bark of pine, 10.07.2012, M.A. Fadeeva, PTZ. 292. Usnea lapponica Vain. – Tolpysheva et al. 2001. 293. Usnea subloridana Stirt. – Fadeeva 2013; Podyelniki, on bark of pine, 10.07.2012, M.A. Fadeeva, PTZ. 294. Vahliella leucophaea (Vahl) P. M. Jørg. – Fadeeva 2013; Ashepnavolok Cape, 1870, J.P. Norrlin, H; Bolshoi Lelikovsky Island, on rock outcrops, 06.07.2004, M.A. Fadeeva, PTZ; Rybya Bay of Lake Onega, eastern slope, on rock outcrops, 11.07.2012, M.A. Fadeeva, PTZ. 295. Vulpicida pinastri (Scop.) J.-E. Mattsson & M. J. Lai – Norrlin 1876; Tolpysheva et al. 2001; Fadeeva 2000, 2013; North to Zubovo village, on Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ. 296. Xanthoparmelia conspersa (Ehrh. exAch.) Hale – Krestovy Isl., abandoned ield, on boulders, 29.05.1999, M.A. Fadeeva, PTZ; Ersenevo village, abandoned ield, on stones, 05.07.2012, M.A. Fadeeva, PTZ; Podyelniki, abandoned ield, on stones and mossy rocks, 10.07.2012, M.A. Fadeeva, PTZ. 297. Xanthoparmelia pulla (Ach.) O.Blanco et al. – Norrlin 1876; Fadeeva 2013. 298. Xanthoparmelia stenophylla (Ach.) Ahti & D. Hawksw. – Fadeeva 2013; Ersenevo village, abandoned ield, on stones, 05.07.2012, M.A. Fadeeva, PTZ; Podyelniki, abandoned ield, on stones and mossy rocks, 10.07.2012, M.A. Fadeeva, PTZ. 299. Xanthoparmelia verruculifera (Nyl.) O.Blanco et al. – Fadeeva 2013. 300. Xylopsora friesii (Ach.) Bendiksby & Timdal – Nylander 1866 a; Norrlin 1876; Fadeeva 2013; NW shore of LakeVekhkozero, on bark of pine, 11.07.2012, M.A. Fadeeva, PTZ. 301. Xanthoria parietina (L.) Th. Fr. – Norrlin 1876; Fadeeva 2000; North to Zubovo village, on Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ. 302. Xanthoria sorediata (Vain.) Poelt – Fadeeva 2013. 303. Xylographa parallela (Ach.) Fr. – Tolpysheva et al. 2001. 304. Xylographa vitiligo (Ach.) J. R. Laundon – Norrlin 1876; Fadeeva 2013; Podyelniki, on wood of pine, 10.07.2012, M.A. Fadeeva, PTZ. 222 Reports of the Finnish Environment Institute 40 | 2014 3.4 Red-listed and indicator lichens of Zaonezhye Peninsula Kimmo Syrjänen*, Olli Manninen** and Margarita A. Fadeeva*** * The Finnish Environment Institute (SYKE), P.O.Box 140, 00251 Helsinki, Finland. Corresponding author Kimmo Syrjänen E-mail: kimmo.syrjanen@ymparisto.i ** Olli Manninen, Luonto-Liitto, Annankatu 26 A, 00100 Helsinki, Finland ***Forest Research Institute of Karelian Research Center of Russian Academy of Sciences, 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia Introduction Some of the lichen collections from Zaonezhye Peninsula date back more than a hundred years, when lichenologists and other botanists of the Imperial Alexander University of Finland made ield excursions to Karelia. Also Zaonezhye Peninsula (Äänisniemi) was visited at that time. The irst lichen lora of Karelia Onegensis (Kon) was published by Johan Petter Norrlin already in 1876 (Norrlin 1876, see also Ahti & Boychuk 2006). At the time, for example, Ramalina obtusata was collected from Zaonezhye near Velikaya Guba and another threatened species of the genus Ramalina, R. thrausta, from Dianova Gora. However, most of the collections and observations of lichens from this area were made in the early 2000’s (2000–2013), mainly by researchers from the Karelian Research Center of the Russian Academy of Sciences (Fadeeva 2013, Fadeeva & Kravchenko 2013). Altogether 1276 species of lichens are found in Karelia (Fadeeva et al. 2007) and about half of them (52 %) are present in Karelia onegensis. Margarita A. Fadeeva has listed 129 lichen species from Zaonezhye Peninsula in 2013. Her article (Fadeeva 2013) includes mainly sites in northern and central parts of the peninsula. Studies by Tolpysheva et al. (2001) and Fadeeva & Kravchenko (2013) have main focus on lichen lora of Kizhi archipelago. All these works include observations of many red-listed and indicator lichen species of pristine forests and other habitat hotspots. In the summers 2012 and 2013, Fadeeva continued inventories of lichens in many parts of Zaonezhye (for example, around the villages of Lipovitsy, Podyelniki, Zubovo and Polya). List of collections is presented in chapter 3.3. Kimmo Syrjänen and Olli Manninen observed lichens in many parts of southern and southwestern Zaonezhye Peninsula during two weeks in late August 2013. As a result of the inventories of the most recent years the number of known lichen species has more than doubled in Za- Reports of the Finnish Environment Institute 40 | 2014 223 onezhye, being now over 304. Lichens specimens collected by Syrjänen and Manninen in 2013 are mainly deposited in the Turku University herbarium (TUR) and materials collected by Fadeeva are available in the Karelian Research Centre herbarium (PTZ) in Petrozavodsk. In chapter 3.3 there is a list of lichen specimens which have been collected from Zaonezhye to different scientiic herbaria in Russia and Finland. All Finnish collections of the year 2013 have not yet been entirely included in the list. Material and methods During the inventory in 2013 by the Finnish group most attention was paid to localities that were selected in earlier inventories (by the non-governmental nature conservation organization SPOK or Karelian Research Centre) or that looked promising in remote sensing images (TM/SPOT satellite imagery). We tried to visit as many forest compartments (kvartal) with pristine-like forests as possible within the study area. However, some of the forest compartments (kvartal), or parts of them, had been recently clear-cut. Nevertheless, we spent most of the time in old-growth forests, swamp forests and brook-side forests. Data were collected especially on indicator lichens, based on Andersson et al. (2009), and red-listed species of Karelia, based on Ivanter & Kuznetsov (2007). Special attention was paid to Calicioid lichens, many of which are used as indicator species of forest habitat quality (Tibell 1999, Andersson et al 2009). Many of the lichen indicator species suggest a continuity of forest habitats, a stable microclimate and an intact hydrology as well as the presence of very old living and dead trees. Although the inventories concentrated on forest habitats, the authors visited also several bogs and mires as well as some rock outcrops with both basic and siliceous bedrock. During the ield trip, we collected data on other species groups as well (vascular plants, fungi, bryophytes). Therefore, the results on lichens are far from complete, although they give a general insight into the importance of Zaonezhye for indicator and red-listed species. Because observation of crustaceous lichens is time consuming, more attention was paid to particularly easily observable species, especially Lobaria pulmonaria. Also other members of the inventory group, especially Jyri Mikkola, Olli-Pekka Tikkanen and Timo Kuuluvainen, informed us about the occurrence of Lobaria pulmonaria and other easily identiiable lichen species. Results The list of observed red-listed and indicator species and frequency of observations are shown in Table 1. Chapter 3.3. contains a more detailed list of lichens specimens collected on Zaonezhye. So far it includes 304 lichen species. Epiphytes of deciduous trees Large aspen trees (Populus tremula) are present throughout the Zaonezhye landscape, both in remote herb-rich old-growth forests and in late-successional deciduous stands close to abandoned old villages. These aspen trees host a rich epiphyte lora. The large, leafy lichen Lobaria pulmonaria is very common in Zaonezhye. Individuals of Lobaria pulmonaria were often healthy, and we observed apothecia in many places. Also, we found the parasite fungus of Lobaria pulmonaria, Plectocarpon lichenum a couple of times in Zaonezhye. In 2013 we recorded Lobaria pulmonaria from 493 sites throughout the southern half of Zaonezhye Peninsula. Another typical epiphyte of aspens in the area is the indicator lichen Leptogium saturninum. Aspen trees also host other foliose lichens that 224 Reports of the Finnish Environment Institute 40 | 2014 live in symbiosis with cyanobacteria. These include species from the genera Nephroma spp. and Peltigera spp. For example, Peltigera praetextata and P. canina are occasionally found at the base of large aspens throughout Zaonezhye. Neproma parile and Nephroma bellum are relatively common epiphyte species, whereas Nephroma resupinatum is more rare. The latter indicator species was found only in a half a dozen locations during the 2013 survey. These folious indicator species are also growing on certain other deciduous trees, mainly on Rowan (Sorbus aucuparia), Goat willow (Salix caprea) and Bay willow (Salix pentandra) and sometimes also on old birches. Old individuals of these tree species are common at the mire margins as well as in swamp forests and herb-rich forests. Other indicator epiphytes of deciduous trees in Zaonezhye include Parmeliella triptophylla, Pannaria pezizoides and Leptogium teretiusculum, which were occasionally found from old herb-rich mixed forests. The presence of these lichens on aspen and other deciduous trees indicates that there is continuity of old deciduous trees and a suitable microclimate and the landscape is connected so that most epiphyte lichen species can disperse and colonize new trees. Peltigera collina was the most rare epiphyte in its genus of folious lichens and was found only twice. Also epiphyte species of the genus Collema seem to be rare in Zaonezhye: Collema subnigrescens/nigrescens was found a few times, Collema fragrans only once. Bay willow (Salix pentandra) is a relatively common tree species in Zaonezhye. It grows regularly at the margins of mires and swamp forests as well as by the side of brooks and rivulets. Trunks of big trees seem to be good substrata for lichen epiphytes. In addition to Loparia pulmonaria and Nephoma spp. they are often colonized by several other species, including Ramalina spp. and Calicioid lichens such as Chaenotheca chlorella and Calicium lichenoides. The commonness of Bay willow is probably due to the fact that most mires have not been drained by ditching. Also beaver activity increases looding dynamics in mire ecosystems and riparian environments. This contributes to the establishment and growth of Salix pentandra. Fig. 1. Salix pentandra swamp forest (Photo: Kimmo Syrjänen). Reports of the Finnish Environment Institute 40 | 2014 225 Also some broadleaf hardwood trees such as Tilia cordata grow in the herb-rich forests of Zaonezhye. Tilia cordata is found occasionally on rich soils. Ulmus laevis grows in many sites at Zaonezhye, especially in Kizhi archipelago. One place worth mentioning is an Ulmus glabra stand southwest of the village of Lipovitsy (whose Russian name refers to a lime tree). In the upper course of a small brook that runs out of Lake Bedzdonnaye, a herb-rich deciduous forest grows about a dozen big elm trees with an interesting lichen epiphyte lora. Bacidia rubella, Gyalecta ulmi and Sclerophora pallida (syn. S. nivea) grow on the elm trunks. The presence of elm trees and these temperate lichen species are a consequence of the favourable climatic conditions and rich soils of Zaonezhye Peninsula. Small swamps forests with Alnus glutinosa occur in many brook valleys and swampy depressions. In one location, we found the crustaceous Arthonia spadicea growing on black alder trunks. It is a red-listed indicator species of black alder swamp-forests. We also found Coenogium pineti growing on trunks of black alder trees in swamp forests. It is a typical species of this habitat. In addition, Arthonia leucopellea has been found as epiphyte of Alnus glutinosa in Zaonezhye. However, most occurrences of this red-listed indicator species in Zaonezhye are on spruce trunks. It typically grows on the bark of old, living spruces in swamp forests and at mire margins. Large old birches (both Betula pendula and B. pubescens) grow in several forest habitats in Zaonezhye, including herb-rich and pristine forests as well as swamp forests and late-successional stands of deciduous forests. Even though Lobaria pulmonaria can occasionally be found also on the trunks of birches, these are not that important for folious species in Zaonezhye. However, birch trees host a wide range of crustaceous lichen species. Especially Chaenotheca brachypoda is a common indicator species on old, partly rotten birches. In swamp forests and old-growth forests, Sclerophora coniophaea is often found by the sides of brooks, on the trunks of very old living birches or dead birch snags. Usnea lichens and other fruticose epiphytes Many hanging fruticose lichens are considered to be indicators of good air quality, moist microclimate and forest continuity. Especially Usnea spp., Bryoria spp., Alectoria sarmentosa, Ramalina thrausta and Evernia divaricata are such species. In Zaonezhye Peninsula, Usnea lichens are most frequently found along bog and mire margins as well as in swamp forests and pristine old-growth forests. These species hang from twigs and trunks of both coniferous and deciduous trees. In the genus Usnea, common species Usnea dasypoga and Usnea subloridana seem to prevail, although this genus was not studied in detail during the ield trip. However, both more rare and threatened species Usnea barbata, U. chaetophora, U. glabrescens and U. lapponica have been collected from few places in Zaonetshye. In the genus Bryoria, widely distributed species like Bryoria capillaris and B. fuscescens (sensu lato) are common and can sometimes completely cover small spruces at the margins of mires. Also Bryoria furcellata, which demands a more natural environment, is generally found at these sites. The large, hanging Bryoria fremontii is not abundant on Zaonezhye Peninsula, although it has been found at a couple of sites. Bryoria nadvornikiana seems to be rare, with only a few individuals found at seven sites. Surprisingly, also Alectoria sarmentosa seems to be a relatively rare or occasional species. Especially larger healthy populations are scarce in Zaonezhye. However, Evernia divaricata was found at 58 sites, typically in transition zones between mires and forests. It can grow on the trunks and twigs of almost all tree species of the region. The size and health of individual lichens varies a lot, but most of the individuals are small and the populations scarce. There are also populations with a large amount of individuals where the length of healthy individuals of hanging 226 Reports of the Finnish Environment Institute 40 | 2014 lichens can reach approximately 20–30 cm. In our inventories there were no sightings of Ramalina thrausta, which has not been found from Zaonezhye for over 100 years. Fig. 2. Healthy hanging Evernia divaricata with Usnea sp. and Bryoria spp. (Photo: Kimmo Syrjänen). Epiphytes of spruce In addition to fruticous species on the branches and trunks of spruces, many crustaceous lichens grow on the bark of old living trees or on the bare wood of dead standing spruces. These include several indicator species of pristine forests, moist microclimate and very old trees. We found Lecanactis abietina in a few places. It is a crustaceous lichen, typically growing on the bark of old spruces. We also found Arthonia leucopellea, which prefers spruces in swamp forests, from a couple of places in the Reports of the Finnish Environment Institute 40 | 2014 227 area. This species was also recorded from Alnus glutinosa. In addition, we observed Chaenotheca subroscida, which is a Calicioid lichen, typically growing on spruce bark in moist pristine forests. We also found Lobadium disciforme from both spruce bark and deciduous trees in Zaonezhye. Lichens on dead wood Tall stumps and snags of spruces and deciduous trees are extremely important for many crustaceous lichens in old-growth pristine forests. Some species, like Chaenotheca chlorella, prefer growing on deciduous trees but are also found from dead wood of spruce and deciduous trees. Others, like Chaenotheca laevigata and Chaenotheca gracillima, grow mainly on bare wood and dead trees but can also grow on the bark of living trees. In Zaonezhye, Sclerophora coniophaea seems to often grow on snags of old birches, but it occasionally grows also on other substrate, including dead wood and bark. It was found at 25 sites in old-growth swamp forests, old herb-rich forests and forests along brooks. However, Chaenotheca gracilenta (syn. Cybebe gracilenta) grows almost exclusively on decaying stumps in the moist conditions of swamp forests and moist old-growth forests. It was observed at more than ten sites in Zaonezhye. Only a few indicator lichens species are typical for downed logs. Cladonia norvegica is common on soft, wind fallen spruce logs in forests with pristine characteristics throughout the peninsula. In places, Icmadophila ericetorum grows on the sides of large, relatively soft spruce and pine logs. Multiclavula mucida is an easy species to identify. It has a permanent green thallus that normally covers several decimeters of large, fallen and decaying aspen trunks. Unlike many other lichens, it belongs to basidiomycota and its fruiting bodies are short-lived, whitish clubs arising from the thallus. Multiclavula mucida grows in various places in Zaonezhye, mainly in herb-rich mixed forests with large aspen trees. Fig. 3. Multiclavula mucida (Photo: Kimmo Syrjänen). 228 Reports of the Finnish Environment Institute 40 | 2014 Cladonia parasitica prefers more sun-exposed conditions than the above species. It is mainly found from downed pine logs and stumps in dry heath pine forests or rocky forests. The ecology of Lecidea botryosa is similar, although it grows also on dry wood of spruce. In suitable habitats, both of these species seem to be relatively common in Zaonezhye. Pyrrhospora elabens is a more rare lichen indicator in Zaonezhye. It prefers snags of large old pines in sun-exposed environments. The species has been found from old, dry pine forests in western parts of Zaonezhye. In Zaonezhye, dead, standing pine trees and snags are common at bogs and mire margins. Shiny black spikes of Calicium denigratum are typically found on dry pinewood in these habitats. In Zaonezhye it is quite often accompanied by Chaenothecopsis fennica, which has a similar ecology to Calicium denigratum but grows also on spruce wood in the same habitats. Both of these indicator species are relatively frequent at bog and mire margins in the area. Bogs are also home for Evernia mesomorpha, аСТМС ЦКТЧХв РrШаs ШЧ ЭаТРs КЧН ЭrЮЧФs ШП sЭЮЧЭОН ЩТЧОs, ЛТrМСОs КЧН sЩrЮМОs ТЧ ШЩОЧ ЛШРs, ЛЮЭ sШЦОЭТЦОs КХsШ ШЧ ЭСО ЛrКЧМСОs ШП НОКН ЭrООs. TСО sЩОМТОs РrШаs ТЧ sОЯОrКХ ЛШРs ТЧ ГКШЧОгСвО, КХЭСШЮРС ТЭ Тs ЧШЭ КЛЮЧНКЧЭ. Basic and siliceous cliffs Carboniferous rocks of Mount Sypun are important for lichens as well as for bryophytes. The site seems to have a very rich lichen lora of basic rocks, including e.g. Collema fuscovirens, Collema polycarpon, Fuscopannaria leucophaea (syn. Vahliella leucophaea), Leptogium plicatile, Neofuscelia verruculifera (syn. Xanthoparmelia verruculifera), Peltigera lepidophora, P. leucophlebia, P. venosa and Xanthoria sorediata. Also Lobaria scrobiculata grows there (Fadeeva 2013). The conservation value of this rocky area is very high. Especially one site on a siliceous rock outcrop in Zaonezhye is worth mentioning. The site is situated east of the village of Lipovitsy, not far from the shores of Lake Onega. It is an east-facing, bare siliceous cliff wall with coarse talus scree beneath it. There is an open oligotrophic mire in front of the cliff. The cliff wall has a typical lichen lora of siliceous oligotrophic rocks, including Chrysothrix chlorina, Ramalina pollinaria, Parmelia fraudans, Alectoria sarmentosa and Hypogymnia vittata. However, there is a more interesting lichen lora on boulder scree, including Cladonia amaurocraea and a large population of Thamnolia vermicularis, which grows on the sides and tops of the boulders. The distribution of this lichen species is mainly Arctic-alpine, although it can be found in some remote locations on lowlands, especially in coastal areas. Nephroma arctica grows towards the southern end of the cliff. Fig. 4. Thamnolia vermicularis (Photo: Kimmo Syrjänen). Reports of the Finnish Environment Institute 40 | 2014 229 Discussion Our inventories revealed several hotspots of pristine-like old-growth forests in larger or smaller patches as well as other types of environments that are important for lichens, including basic and siliceous rock outcrops. These short inventories revealed 1141 locations of red-listed and indicator lichens in Zaonezhye. It is evident that the species composition and the potential for conservation of biodiversity in Zaonezhye are much higher than have previously been thought. The diverse species composition of lichens is probably due to various reasons. There are still quite large old-growth forests, with a continuity of dead wood, remote from old villages. The bogs and mires of Zaonezhye are mostly intact, and drained bogs and mires are an exception. There are often wide transition zones between the margins of peat-forming ecosystems and the forests on mineral soil, which have not been used in active forestry. Swamps forests are common in Zaonezhye. These areas have a large number of tree species, old and dead trees as well as a suitable, moist microclimate. Some of the old traditional landscapes and grazed forests close to the villages, which were more open in the past, now have old deciduous trees. For many epiphyte lichens and species of dead wood, the landscapes form a connected network of suitable habitats. Zaonezhye provides an opportunity to maintain this valuable lora by making forest conservation areas and developing green corridors to connect them. Also peatlands and waterways could be used when building connections between larger conservation areas. REFERENCES AЧНОrssШЧ, L., AХОбООЯК, N.M. & KЮгЧОЭsШЯК, E. S. (ОНs.) 2009. ., . ., . . ДSЮrЯОв ШП ЛТШХШРТМКХХв ЯКХЮКЛХО ПШrОsЭs ТЧ NШrЭС-АОsЭОrЧ EЮrШЩОКЧ RЮssТК. VШХ 2. – IНОЧЭТiМКЭТШЧ ЦКЧЮКХ ШП sЩОМТОs ЭШ ЛО ЮsОН НЮrТЧР sЮrЯОв КЭ sЭКЧН ХОЯОХЖ. SЭ-PОЭОrsЛЮrР. 258 Щ. AСЭТ, T. & BШвМСЮФ, M. 2006. TСО ЛШЭКЧТМКХ УШЮrЧОвs ШП A.K. CКУКЧНОr КЧН J.I. LТЧНrШЭС ЭШ KКrОХТК КЧН OЧОРК RТЯОr ТЧ 1898 КЧН 1899, аТЭС К ХТsЭ ШП ЭСОТr ЛrвШЩСвЭО КЧН ХТМСОЧ МШХХОМЭТШЧs. – NШrrХТЧТК 14:1–65. FКНООЯК, . ., GШХЮЛФШЯК, N. S., VТЭТФКТЧОЧ, . & AСЭТ, . 2007. . ., . ., ., . ДCШЧsЩОМЭЮs ШП ЭСО ХТМСОЧs КЧН ХТМСОЧШЩСвХШЮs ПЮЧРТ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ.194 Щ. (IЧ RЮssТКЧ). FКНООЯК, . . 2013. . . ДLТМСОЧsЖ. −IЧ: GrШЦЭsОЯ, A.N. (ОН.), SОХФК ХКЧНsМКЩОs ШП ЭСО Zaonezhkii Peninsula: Natural characteristics. Land Use. Conservation. (eds.), Karelian Research Center of RЮssТКЧAМКНОЦв ШП SМТОЧМОs.PОЭrШгКЯШНsФ. Щ. 114–121. (IЧ RЮssТКЧ). FКНООЯК, . . & KrКЯМСОЧФШ, A. V. 2013. . ., . . ДSЭЮНв ШП ЭСО ХТМСОЧ lШrК ШП ЭСО МШЧЭТЧОЧЭКХ KТгСТ ArМСТЩОХКРШЖ. − IЧ: MКrЭвКЧШЯ, R. & IОsСФШ, . (ОНs.), BЮХХОЭТЧ ШП ОЧЯТrШЧЦОЧЭКХ sЭЮНТОs ТЧ KТгСТ MЮsОЮЦ-RОsОrЯО PОЭrШгКЯШНsФ: KТгСТ MЮsОЮЦ-RОsОrЯО PЮЛХТsСТЧР CОЧЭrО. Щ. 14−16. (IЧ RЮssТКЧ). IЯКЧЭОr, E. V. & KЮгЧОЭsШЯ, O. L. (ОНs.) 2007. . ., . . ( .) ДRОН НКЭК ЛШШФ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ, 368 Щ. NШrrХТЧ, J.P. 1876: FХШrК KКrОХТКО ШЧОРОЧsТs. II LТМСОЧОs. – MОННОХКЧНОЧ SШМТОЭКЭТs FКЮЧК FХШrК FОЧЧТМК 1:1–46. RКssТ, P., HвЯтrТЧОЧ, E., JЮsХцЧ, A. & MКЧЧОrФШsФТ, I. (ОНs.) 2010. TСО 2010 RОН LТsЭ ШП FТЧЧТsС SЩОМТОs. –ВЦЩтrТsЭöЦТЧТsЭОrТö & SЮШЦОЧ вЦЩтrТsЭöФОsФЮs. HОХsТЧФТ. 685 Щ. TТЛОХХ, L. 1999. CКХТМТШТН ХТМСОЧs КЧН ПЮЧРТ. – NШrНТМ LТМСОЧ FХШrК 1:20–70. UННОЯКХХК. TШХЩвsСОЯК, . ВЮ., LвЮЛТЦШЯК, . G., GШrsСТЧК, . S. & SТгШЯК, . P. 2001. . ., . ., . ., . . . 3. ДLТМСОЧ lШrК ШП КЧМТОЧЭ аШШНОЧ КrМСТЭОМЭЮrКХ ЦШЧЮЦОЧЭs. 3. CСЮrМС ШП TrКЧsiРЮrКЭТШЧ ТЧ KТгСТЖ. – IЧ: VОsЭЧТФ MШsФШЯsФШРШ ЮЧТЯОrsТЭОЭК, SОr. 16. BТШХШРв 1: 24–33. (IЧ RЮssТКЧ). 230 Reports of the Finnish Environment Institute 40 | 2014 Table 1. Red listed and indicator lichens of Zaonezhye. Presence of species in Karelian (KAR) and Finnish (FIN) Red Data Books is shown in the irst column (Ivanter & Kutznetsov 2007, Rassi et al. 2010). Their role as indicator (IND) of valuable forest habitats is shown in the second column (based on Andersson et al. 2009) and number of observations in the third column. Also some other lichen species with indicator characteristics are included in table. Table is based on observations by the authors in 2012–2013 and literature information (Fadeeva 2013, Fadeeva & Kravchenko 2013, Tolpysheva et al. 2001). Table includes only recent observations of valuable species; historical records are available in chapter 3.3. Species name Red Listed Alectoria sarmentosa Anaptychia ciliaris Arthonia leucopellaea Arthonia spadicea Arthonia vinosa Bacidia rubella Bryoria fremontii Bryoria nadvornikiana Calicium denigratum Chaenotheca brachypoda Chaenotheca chlorella Chaenotheca gracilenta Chaenotheca gracillima Chaenotheca laevigata Chaenotheca stemonea Chaenotheca subroscida Chaenothecopsis fennica Cladonia decorticata Cladonia norvegica Cladonia parasitica Coenogium pineti Collema laccidum Collema fragrans Collema furfuracea Collema fuscovirens Collema polycarpon Collema subnigrescens Evernia divaricata Evernia mesomorpha Fuscopannaria leucophaea Graphis scripta Gyalecta truncigena Gyalecta ulmi Hypogymnia vittata Icmadophila ericetorum Lecanactis abietina Lecidea botryosa Leptogium lichenoides Leptogium plicatile Leptogium saturninum Leptogium teretiusculum Lobaria pulmonaria Lobaria scrobiculata Lopadium disciforme Melanelia subaurifera Microcalicium disseminatum Multiclavula mucida Neofuscelia verruculifera KAR, FIN KAR KAR, FIN FIN KAR, FIN FIN KAR, FIN KAR, FIN FIN FIN KAR, FIN KAR, FIN FIN KAR, FIN KAR, FIN FIN KAR FIN FIN Indicator species IND IND IND IND IND IND IND IND IND IND IND IND IND IND IND IND IND FIN FIN FIN FIN KAR, FIN IND IND FIN KAR, FIN KAR FIN FIN FIN KAR, FIN KAR, FIN FIN KAR IND IND IND IND IND IND IND IND IND IND IND IND IND FIN KAR, FIN Number of observations 11 2 6 1 1 1 4 6 17 64 8 14 4 3 1 4 8 1 12 53 2 1 1 1 1 1 2 58 13 1 11 1 2 2 11 3 18 2 1 89 7 518 3 8 1 6 7 1 Reports of the Finnish Environment Institute 40 | 2014 231 Nephroma arcticum Nephroma bellum Nephroma parile Nephroma resupinatum Pannaria pezizoides Parmeliella triptophylla Parmelina tiliacea Peltigera collina Peltigera scabrosa Peltigera venosa Plectocarpon lichenum Pyrrhospora elabens Psilolechia clavulifera Ramalina baltica Ramalina dilacerata Ramalina sinensis Sclerophora coniophaea Sclerophora pallida Thamnolia vermicularis Usnea barbata Usnea chaetophora Usnea glabrescens Usnea lapponica 232 Reports of the Finnish Environment Institute 40 | 2014 KAR, FIN FIN FIN KAR, FIN KAR, FIN KAR, FIN FIN FIN KAR KAR, FIN KAR, FIN FIN KAR, FIN FIN KAR KAR, FIN FIN FIN FIN IND IND IND IND IND IND IND IND IND IND IND IND IND 2 36 36 6 2 12 1 2 1 2 3 3 1 2 3 4 25 1 1 1 1 1 1 3.5 Aphyllophoroid fungi of Zaonezhye Peninsula Anna Ruokolainen* and Olli Manninen** * Forest Research Institute of the Karelian Research Center of Russian Academy of Sciences 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia E-mail: anna.ruokolainen@krc.karelia.ru ** Olli Manninen, Luonto-Liitto, Annankatu 26 A, 00100 Helsinki, Finland Introduction Zaonezhye Peninsula is dominated by green-moss spruce forests. Also nemoral species grow in these forests, and thus the forests have features of southern taiga forests. In the past most of the areas on Zaonezhye Peninsula formerly covered with pristine spruce-dominated forests were cleared for slash-and-burn cultivation to give way to pastures, ploughland and meadows as well as secondary mixed forests (Kuznetsov et al. 1999). Mycological studies in Zaonezhye Peninsula and adjacent areas Mycological studies in Zaonezhye were carried out between 1996 and 1998 by the Forest Research Institute of the Karelian Research Centre of the Russian Academy of Sciences, Petrozavodsk (FRI) and V.L. Komarov Botanical Institute of the Russian Academy of Sciences, St. Petersburg (BIN RAS) (Bondartseva et al. 2000). In 1996 and 1998, Margarita Bondartseva, Vera Kotkova (Lositskaya), Vitaly Krutov and Svetlana Kiviniemi conducted research on the Kizhi and Gogolev islands. In 1997, Anna Ruokolainen carried out studies on Bolshoi Klimenetsky Island Between 2010 and 2013, Anna Ruokolainen continued her studies, in cooperation with the Finnish specialists Olli-Pekka Turunen, Olli Manninen and Jyri Mikkola, on Bolshoi Lelikovsky Island and other parts of Zaonezhye Peninsula (in the vicinity of the villages of Vegoruksa, Velikaya Guba, Velikaya Niva, Kuzaranda, Lipovitsy, Polya, Tambitsy, Tipinitsy and Shun’ga as well as lakes Vanchozero and Kosmozero). In 2012, fungi were studied on Kizhi Island and near the villages of Zharnikovo, Malkovo, Zubovo and Podyelniki with the initiative and support of the Kizhi museum-reserve. Samples from Zaonezhye Peninsula and the Kizhi archipelago are stored in the herbaria of BIN RAS (LE) and FRI (PTZ). Reports of the Finnish Environment Institute 40 | 2014 233 Data from previous decades are very sparse. The herbarium of the University of Helsinki contains two samples from Kizhi Island collected by W. Nyberg in 1863 and three samples taken by Pertti Uotila in 1991 (Bondartseva et al. 1999). According to the geobotanical zonation of Karelia (Mela & Cajander 1906), Zaonezhye Peninsula forms a part of the province of Karelia onegensis (Kon). Administratively, it belongs to the Medvezhyegorsk municipality of the Republic of Karelia. As a result of the mycological studies, a total of 360 aphyllophoroid fungus species have been reported from the province of Kon (which is the greatest number of species reported in any of the provinces in the Republic of Karelia) and 264 aphyllophoroid fungus species from the Medvezhyegorsk District (Bondartseva et al. 1999, Bondartseva et al. 2000, Lositskaya et al. 2001; Ruokolainen 2013 a, b, c). So far a relatively small number of fungus species has been recorded from the Kizhi archipelago. On one hand, this is due to intensive economic activities and the resulting changes in vegetation. On the other hand, the islands have been poorly studied in the past. There are records of 43 species from Bolshoi Klimenetsky Isl. (Bondartseva et al. 2000), 37 species from the Kizhi and Gogolev islands (Ruokolainen 2013 b) and 24 species from Bolshoi Lelikovsky Island (Ruokolainen, unpublished). Fig. 1. Anna Ruokolainen collecting polypores on dead wood. Forest near Lipovitsy village 23.08.2013 (Photo Jevgeni Jakovlev). Results To date, 233 aphyllophoroid fungus species of 113 genera, 38 families and 14 orders have been recorded from Zaonezhye Peninsula and the Kizhi archipelago. The most 234 Reports of the Finnish Environment Institute 40 | 2014 numerous order Polyporales contains 109 species of 49 genera and 7 families. Less numerous orders include Hymenochaetales (41 species of 13 genera and 3 families) and Russulales (21, 14 and 8 species, respectively). The orders Polyporales and Hymenochaetales consist basically of 5 families: Polyporaceae (35 species), Hymenochaetaceae (24), Fomitopsidaceae (30), Meruliaceae (23) and Schizoporaceae (14 species), which in turn consist of 126 species that make up 54% of all the aphyllophoroid fungus species known from the peninsula. The most numerous genera are Phellinus (14 species), Hyphodontia (12 species), Postia (10 species), Antrodia (9 species), Skeletocutis (7 species), Phlebia, Tomentella (6 species each), Polyporus, Trametes (5 species each), Antrodiella, Phanerochaete, Stereum, Trichaptum (4 species each). Nomenclature follows Index Fungorum (2014). Ninety-four species were found on conifers; 70 species were discovered on spruce (Picea abies and P. obovata) and 49 species on pine (Pinus sylvestris). A hundred species were found on deciduous tree species; 61 species were discovered on aspen (Populus tremulae), 40 on birches (Betula pendula and B. pubescens), 28 on alders (Alnus incana A. glutinosa), 22 on willow (Salix caprea), 19 on mountain ash (Sorbus aucuparia) and 5 species on elms (Ulmus laevis, U. glabra). Growing on soil and litter, there were 25 species of the genera Albatrellus, Bankera, Boletopsis, Cantharellus, Clavariadelphus, Clavulina, Coltricia, Craterellus, Hydnellum, Phaeolus, Phellodon, Ramaria, Sarcodon and Thelephora. Sixty-three species found in Zaonezhye are indicators of old-growth forests. These species are conined to the distinctive conditions of forest communities least affected by human activities (Albatrellus conluens, Amylocorticium subincarnatum, Amylocystis lapponica, Anomoporia kamchatica, Antrodia albobrunnea, A. crassa, A. pulvinascens, Antrodiella citrinella, Asterodon ferruginosus, Bankera fuligineoalba, Boletopsis grisea, Chaetoderma luna, Clavariadelphus pistillaris, Climacocystis borealis, Crustoderma corneum, C. dryinum, Dichomitus squalens, Diplomitoporus crustulinus, Fomitopsis rosea, Ganoderma lucidum, Gloeoporus pannocinctus, G. taxicola, Gloiodon strigosus, Haploporus odorus, Hericium coralloides, Junghuhnia collabens, J. luteoalba, J. pseudozilingiana, Kavinia alboviridis, Leptoporus mollis, Onnia leporina, Perenniporia subacida, Phaeolus schweinitzii, Phellinus chrysoloma, Ph. ferrugineofuscus, Ph. lundellii, Ph. nigrolimitatus, Ph. pini, Ph. populicola, Ph. viticola, Phellodon niger, Phlebia centrifuga, Ph. serialis, Piloporia sajanensis, Polyporus badius, P. pseudobetulinus, Postia guttulata, P. lateritia, P. undosa, Pseudomerulius aureus, Pycnoporellus alboluteus, P. fulgens, species of the genus Ramaria, Rhodonia placenta, Rigidoporus crocatus, Serpula himantoides, Sidera lenis, Skeletocutis odora, Sk. stellae, Tomentella crinalis, Trametes suaveolens, Tyromyces issilis). The above species indicate that these ecosystems are valuable and should be protected (Kotiranta & Niemelä 1996; Andersson et al. 2009). Twenty-one species, listed in the Red Data Book of the Republic of Karelia (2007), including Antrodia crassa, A. pulvinascens, Antrodiella citrinella, Aurantiporus issilis, Clavariadelphus pistillaris, Craterellus cornucopioides, Dichomitus squalens, Elmerina caryae, Ganoderma lucidum, Gloiodon strigosus, Haploporus odorus, Hericium coralloides, Junghuhnia collabens, J. pseudozilingiana, Kavinia alboviridis, Leptoporus mollis, Piloporia sajanensis, Polyporus pseudobetulinus, Radulodon erikssonii, Rigidoporus crocatus, Sidera lenis and Tomentella crinalis were reported from the study area. In addition, 40 species, classiied as VU (10 species), NT (25 species) and EN (5 species), were listed in the 2010 Red list of Finnish species (Rassi et al 2010). The species Amylocorticium subincarnatum, Amylocystis lapponica, Boletopsis grisea, Ceriporia excelsa, Crustoderma corneum, C. dryinum, Diplomitoporus crustulinus, D. lavescens, Fomitopsis rosea, Odonticium romellii, Perenniporia subacida, Phlebia centrifuga, Polyporus badius, Postia guttulata, P. lateritia, Pycnoporellus alboluteus, Scytinostroma galactinum, Skeletocutis brevispora, Sk. odora, Sk. stellae, Trametes suaveolens, Trichaptum laricinum Reports of the Finnish Environment Institute 40 | 2014 235 and T. pargamenum have not yet been granted a protected status in Russia, although they are already protected in neighboring countries. Species conined to pine Pine trees provide a number of habitats for fungi that colonize both living and dead trunks, snags, fallen logs and twigs at different stages of decay. In 2013, Phellinus pini was the most abundant fungal species found on pine throughout the southern part of the peninsula (120 records). The second most abundant species (in terms of frequency) was Diplomitoporus lavescens, which was found on standing, dead pine trunks. On fallen dead pines, the most abundant fungal species were Antrodia albobrunnea, Chaetoderma luna, Crustoderma corneum, Postia lateritia, P. undosa (which can colonize spruce as well) and Pseudomerulius aureus. On soil litter, we found Albatrellus conluens, Bankera fuligineoalba, Phaeolus schweinitzii, Phellodon niger, and several species of the genus Ramaria. The species growing on soil and litter include both mycorrhizal and humus saprotrophic fungi. These species are most abundant in old-growth pine forests, whereas in secondary pine forest they are usually rare. Species conined to spruce There are several indicator species of natural forests growing on spruce. Many of them are also red-listed. In 2013, the most abundant of these species were: Fomitopsis rosea (350 sites), Phellinus chrysoloma (more than 90 sites), Pycnoporellus fulgens (more than 80 sites), Phlebia centrifuga (ca. 80 sites), Amylocystis lapponica (more than 70 sites), and Phellinus viticola (more than 50 sites). Less abundant species included Climacocystis borealis, Asterodon ferruginosus, Crustoderma corneum, Gloeoporus pannocinctus, Hericium coralloides, Leptoporus mollis, Onnia leporina, Phellinus nigrolimitatus, Rhodonia placenta, and Skeletocutis odora. Finally, some indicator species and threatened species were found only on a few sites (less than 10 sites), e.g. Anomoporia kamtschatica, Antrodia inirma, A. pulvinascens, Antrodiella citrinella, Clavariadelphus pistillaris, Diplomitoporus crustulinus, Gloeoporus taxicola, Gloiodon strigosus, Haploporus odorus, Junghuhnia collabens, J. luteoalba, Pycnoporellus albolutescens, Sidera lenis, Skeletocutis chrysella, Sk. papyracea, Sk. stellae and Trametes suaveolens. Species conined to aspen Aspen trunks are usually covered with epiphytic lichens, which can in turn be succeeded by various species of fungi. Some of these fungi are parasitoids that colonize other fungal species. For instance, large fruiting bodies of Phellinus tremulae are often colonized by Junghuhnia pseudozilingiana, which is considered an indicator species of old-growth forests and is therefore included in the Red Books of Karelia (2007) and Finland (Rassi et al. 2010). In 2013, this species was recorded from 10 sites in the southern part of Zaonezhye Peninsula. In addition, Tomentella crinalis and Polyporus badius have been found in some sites on fallen aspen logs at different stages of decay. The former is included in the Red Book of Karelia (2007), while the latter has become rare in Finland and Sweden. Phellinus populicola, which is considered rare in Sweden (Artdatabanken 2010), was recorded in 2013 from approximately 90 sites in the southern part of Zaonezhye Peninsula. 236 Reports of the Finnish Environment Institute 40 | 2014 The most noteworthy indings of threatened and rare species of saproxylic fungi Antrodia crassa (P. Karst.) Ryvarden found in the end of Syar peninsula, Comparment 187, old-growth pine-dominated forest (19.08.2013, Olli Manninen leg.). This is maybe the most exclusive species conined the best pine forests preserved in the area. This inding must also be one of the southernmost indings in Fennoscandia. Ceriporia excelsa S. Lundell ex Parmasto was found on a wind-fallen deciduous tree in a small-leaved thicket on Kizhi Island. This is the irst inding of this relatively rare, southern species in the Republic of Karelia. It is also encountered in the adjacent Leningrad and Arkhangelsk Regions as well as in the Komi Republic. Ceriporia excelsa is a common species in Europe and North America. It is classiied as NT in the 2010 Red list of Finnish species (Rassi et al. 2010) and in Sweden (Artdatabanken 2010). Fig. 2. Ceriporia excelsa (Photo Anna Ruokolainen). Ganoderma lucidum (M. A. Curtis : Fr.) P. Karst. was found on a drying birch trunk in a mixed forest in the vicinity of the village of Tipinitsy. In the Republic of Karelia, this is the irst inding of the species in the Medvezhyegorsk District as well as in the Kon province. There have been sparse reports of the species from the Kl province in the Sortavala District (on a larch stump in a plantation on Valaam Island) and the Kton province in the Pudozh District (on a wind-fallen alder tree in the Vodlozero National Park). Ganoderma lucidum is common in southern Russia, but less common in middle latitudes. It occurs widely in Europe (except for northern Scandinavia and Finland), Asia, North Africa and North America. In the Red Data Book of the Republic of Karelia (2007) the species was classiied as VU. It is also included in the Red Data Book of the Russian Federation (2008) as well as regional Red Data Books. Reports of the Finnish Environment Institute 40 | 2014 237 Fig. 3. Ganoderma lucidum (Photo Anna Ruokolainen). Kavinia alboviridis (Mordan) Gilb. et Budington. One inding on old dry pieces of dead spruce (under an old living spruce) northwest of the Vatnavolok village, Syar peninsula (Comparment 134). There are sparse records of the species in the Republic of Karelia and it is only known from the Muezersky District and the environs of the Kostomuksha nature reserve. Kavinia alboviridis is classiied as DD in the Red Data Book of the Republic of Karelia (2007). Junghuhnia pseudozilingiana (Parmasto) Ryvarden was found in several parts of Zaonezhye Peninsula. It grows in mixed forests with old aspen trees, colonized and inhabited by the fungus Phellinus tremulae. The species is classiied as DD in the Red Data Book of the Republic of Karelia (2007) and the Red Nature Data Book of the Leningrad Region (2000), and VU in the 2010 Red list of Finnish species (Rassi et al. 2010). Junghuhnia pseudozilingiana occurs widely in Europe. Fig. 4. Junghuhnia pseudozilingiana (Photo Anna Ruokolainen). 238 Reports of the Finnish Environment Institute 40 | 2014 Piloporia sajanensis (Parmasto) Niemelä found in the vicinity of Uzkaya Salma village, Comparment 26 of Kizhi forestry unit. Moist spruce-dominated forest, 28.06.2013 (Olli Manninen leg.). This must be one of the southernmost indings of this rare species that is dependent on Trichaptum laricinum. Pycnoporellus alboluteus (Ellis et Everh.) Kotl. et Pouzar. Two new records South from Velikaya Guba village, at the western part of peninsula, Comparment 9 of Kizhi forestry unit in old-growth spruce forests with very much dead wood in all stages (Olli Maninen and Timo Kuuluvainen legs). This is the irst inding of the species in the Republic of Karelia. The species is classiied as EN in the 2010 Red list of Finnish species (Rassi et al. 2010) and CR in Sweden (2010). Pycnoporellus alboluteus occurs widely in Europe, Caucasus, Asia and North America. Rigidoporus crocatus (Pat.) Ryvarden was found on wind-fallen trunks of birch, alder and spruce trees in birch, motley grass-spruce and mixed forests near the villages of Zharnikovo, Lipovitsy, Polya and Tambitsy as well as on Bolshoi Klimenetsky Isl.. There are also a few reports of the species from Kondopoga and Pudozh Districts in the Republic of Karelia. The species is classiied as VU in the Red Data Book of the Republic of Karelia (2007). It is also listed in the Red Nature Data Book of the Leningrad Region (2000) and classiied as EN in the 2010 Red list of Finnish species (Rassi et al. 2010). Although Rigidoporus crocatus is rare here, it is common in other parts of Europe and North America. Fig. 5. Rigidoporus crocatus (Photo Anna Ruokolainen). Tomentella crinalis (Fr.) M.J. Larsen was found on a wind-fallen trunk of an aspen tree in a mixed forest near the villages of Tambitsy and Tipinitsy. In the Republic of Karelia, it is also found in Muezersky and Kondopoga Districts. The species is classiied as NT in the Red Data Book of Karelia (2007). Tomentella crinalis also occurs in the Leningrad and Arkhangelsk Regions. The predominance of species growing on deciduous trees indicates that the ecosystems of Zaonezhye have been transformed. However, a large number of species have been found on spruce and pine, which are the main forest-forming species. Further mycological studies and monitoring should be conducted in rocky pine forests, coastal Reports of the Finnish Environment Institute 40 | 2014 239 spruce forests and spruce forest patches along streams, as well as in old aspen forests. The large amount of rare and indicator species testiies to the importance of preserving and restoring ecosystems and habitats of species that need protection. Table 1. List of study sites, 2010–2013. 240 Latitude Longitude Place of collection, compartment, forest type Date 61,5605 35,08295 Bolshoi Lelikovsky Isl., pine forest 09/08/2010 61,560704 35,08214 Bolshoi Lelikovsky Isl., pine forest with spruce 09/08/2010 62,03355 35,03153 Recently fallen spruce trees; Bilberry spruce forest with aspen, south of the village of Uzkaya Salma 13/08/2010 62,03322 35,03274 Thick aspen trees (50-70 cm in diameter) 13/08/2010 62,03282 35,03251 Moist spruce forest with horsetail 13/08/2010 62,0259 35,04143 62,08100 35, 07234 Fallen trees (window dynamics) 11/08/2010 62,08094 35,07096 Lake shore 11/08/2010 62,07580 35,07131 Creek 11/08/2010 62,07576 35, 07101 Rock 11/08/2010 62,20098 35,08238 Rock 17/08/2010 62,23095 35,05072 Mixed forest near a ridge 17/08/2010 62,23077 35,05072 Rocky pine forest 17/08/2010 62,22324 35,05524 Lake shore 17/08/2010 62,04187 35,06582 Compartment 63, unit 20, spruce forest near a logging area 18/08/2010 62,04181 35 ,07116 Compartment 63, unit 20, spruce forest near a logging area 18/08/2010 62,04181 35 ,07116 Pine forest with aspen and spruce 18/08/2010 62,15156 35,00375 Bilberry spruce forest 19/08/2010 62,12589 34,54187 Bilberry motley-grass pine forest 19/08/2010 62,13394 34,58162 Pine forest 19/08/2010 62,17287 35,15553 13/08/2010 05/08/2011 62,10552 35,26476 South of Tambitsy, spruce forest 04/08/2011 62,10547 35,21341 South of Tambitsy, spruce forest 04/08/2011 62, 10393 35,20512 Spruce forest with overmature birch forest nearby 04/08/2011 62,11019 35,19156 Birch forest with spruce undergrowth 04/08/2011 62,16483 35,19158 Mixed forest 05/08/2011 62,20142 35,11240 Overmature motley grass-bilberry-shamrock spruce forest 05/08/2011 62,20091 35,11 010 Overmature aspen forest with spruce and birch 05/08/2011 62,20576 35,12 281 Spruce forest near a logging area 05/08/2011 62,14408 35,33 061 Motley grass birch forest with aspen and spruce 06/08/2011 62,66532 35,34077 Overmature spruce forest with aspen and birch 06/08/2011 62,15192 35,34179 Selective cutting area in green moss spruce forest with aspen 06/08/2011 62,1772 35,34074 East shore, south of Kuzaranda, spruce forest with aspen 07/08/2011 62,17527 35.34392 Aspen forest 07/08/2011 62,17446 35,34180 Spruce forest 07/08/2011 62,1772 35.34074 Pine forest 08/08/2011 62,25191 35,08184 Rocky pine forest 08/08/2011 62,25193 35,07515 Spruce forest with fallen trees (window dynamics) 08/08/2011 62,30067 34,93836 Environs of Velikaya Niva 23/08/2012 Reports of the Finnish Environment Institute 40 | 2014 62,11621 35,030734 A ridge between lakes 23/08/2012 62,62897 34,55234 Lake Vanchezero 22/08/2012 62,238002 34,88029 south of the village of Lambasruchei, Lake Onega shore 24/08/2012 62,497863 34,76967 south of the village of Lambasruchei, Lake Onega shore, a ridge 24/08/2012 62,53639 34,82289 Lake Kosmozero 25/08/2012 62,131327 35,093334 Lipovitsy, spruce forest with aspen and fallen spruce 21/08/2013 62,151863 34,943757 by the lake in pine forest, compartment 13 22/08/2013 62,10509 35,02556 Lipovitsy, spruce forest with aspen and fallen spruce, compartment 41-42 23/08/2013 62,290624 35,309113 trap, Polya, compartment 84, mixed forest with aspen and fallen spruce 24/08/2013 62,29052 35,57008 north of Tambitsy, environs of Tolsty Navolok, mixed and spruce forest, compartment 71 26/08/2013 62,1849 35,31122 Lake Korbozero, Tipinitsy, mixed and spruce forest 27/08/2013 62,17725 35,3571 Tipinitsy, spruce forest 27/08/2013 62,24515 35,49294 Tambitsy, motley grass spruce forest 28/08/2013 62,2418 35,49248 Tambitsy, spruce forest with aspen 28/08/2013 REFERENCES AЧНОrssШЧ, L., AХОбОТОЯК, N. . & KЮгЧОЭsШЯК, . S. (ОНs.) 2009. ., . ., . . . 2. , ДRОЯОКХТЧР КЧН sЭЮНв ШП ЛТШХШРТМКХХв ЯКХЮКЛХО ПШrОsЭs ТЧ ЧШrЭСаОsЭОrЧ EЮrШЩОКЧ RЮssТК. VШХ. 2. MКЧЮКХ ПШr МХКssТiМКЭТШЧ ШП ЭСО sЩОМТОs ЮsОН ПШr ЮЧТЭ-ХОЯОХ ОбКЦТЧКЭТШЧЖ. – SЭ. PОЭОrsЛЮrР. 258 Щ. (IЧ RЮssТКЧ). ArЭНКЭКЛКЧФОЧ 2010. JКЧ-OХШП TОНОЛrКЧН. RöНХТsЭКНО КrЭОr Т SЯОrТРО. SЯКЦЩКr. – TСО 2010 RОН LТsЭ ШП SаОНТsС SЩОМТОs. ArЭНКЭКЛКЧФОЧ, SLU, UЩЩsКХК, 2010. Щ. 247–284. BШЧНКrЭsОЯК, . ., LШsТЭsФКвК, V. . & RЮШФШХКТЧОЧ, . V. 1999. . ., . ., . . ( Aphillophorales) ДАШШН-НОsЭrШвТЧР ПЮЧРТ (ШrНОr Aphyllophorales) ШП ЭСО KТгСТ ArМСТЩОХКРШЖ. – IЧ: KТгСТ ArМСТЩОХКРШ ТsХКЧНs. BТРОШРrКЩСТМ НОsМrТЩЭТШЧ. TrКЧsКМЭТШЧs ШП KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. SОr. BТШРОШРrКЩСв ШП KКrОХТК. IssЮО 1. SОr. B 1: 84−86, 157−158. (IЧ RЮssТКЧ). BШЧНКrЭsОЯК, . ., KrЮЭШЯ, V. I., LШsТЭsФКвК, V. ., KТЯТЧТОЦТ, S. N. & RЮШФШХКТЧОЧ, . V. 2000. . ., . ., . ., . ., . . (AЩСвХХШЩСШrКХОs s. ХКЭШ) (Aphyllophorales s. ХКЭШ) ДAЩСвХХШЩСШrШТН ПЮЧРТ (Aphyllophorales s. ХКЭШ).Ж – IЧ: GrШЦЭsОЯ, A.N. & KrЮЭШЯ, V.I. (ОНs.), IЧЯОЧЭШrв КЧН sЭЮНв ШП ЛТШХШРТМКХ НТЯОrsТЭв ШЧ ЭСО ГКШЧОгСвО PОЧТЧsЮХК КЧН ТЧ NШrЭСОrЧ PrТХКНШгСвО: OЩОrКЭ.–ТЧПШrЦ. ЦКЭОrТКХs. – PОЭrШгКЯШНsФ. Щ. 117–122. (IЧ RЮssТКЧ). ДDШМЮЦОЧЭКЭТШЧ ШП ЭСО МШЦЩХОб ОМШХШРТМКХ ТЧЯОЧЭШrв УЮsЭТПвТЧР ОsЭКЛХТsСЦОЧЭ ШП ЭСО ГКШЧОгСsФв sЭКЭО ЧКЭЮrО ЩКrФЖ. 2013. , « » NGO “SPOK”. – PОЭrШгКЯШНsФ.108 Щ. (IЧ RЮssТКЧ). MОХК, A. J. & CКУКЧНОr, A. K. (ОНs.) 1906. SЮШЦОЧ KКsЯТШ. SЮШЦКХКТsОЧ KТrУКХХТsЮНОЧ sОЮrКЧ ЭШТЦТЭЮФsТК 53, III. – HОХsТЧФТ, Б+ 764 Щ. + 1 ЦКЩ. IЯКЧЭОr, E. V. & KЮгЧОЭsШЯ, O. L. (ОНs.) 2007. .B., . . ( .). . ДRОН DКЭК BШШФ ШП RОЩЮЛХТМ ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ. 368 Щ. (IЧ RЮssТКЧ). IЧНОб FЮЧРШrЮЦ. CABI DКЭКЛКsО. URL: СЭЭЩ://ааа.ТЧНОбПЮЧРШrЮЦ.ШrР, 2013. (КЩЩХТМКЭТШЧ НКЭО: 25 AЩrТХ, 2014). KШЭТrКЧЭК, H. & NТОЦОХт, T. 1996. UСКЧКХКТsОЭ ФттЯтЭ SЮШЦОssК. – HОХsТЧФТ. 184 Щ. KЮгЧОЭsШЯ, . L., BrКгШЯsФКвК, . I. & SЭШТФТЧК, N. V. 1999. . ., . ., . . , « » ДFХШrК, ЯОРОЭКЭТШЧ КЧН РОЧОsТs ШП ЦТrОs ТЧ ЭСО ЩrШЭОМЭТШЧ гШЧО ШП KТгСТ RОsОrЯО MЮsОЮЦЖ. – IЧ: KТгСТ ArМСТЩОХКРШ ТsХКЧНs. BТШРОШРrКЩСТМ НОsМrТЩЭТШЧ. TrКЧsКМЭТШЧs ШП ЭСО KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. SОr. BТШРОШРrКЩСв ШП KКrОХТК. PОЭrШгКЯШНsФ. Щ. 48–54. (IЧ RЮssТКЧ). LШsТЭsФКвК, V. ., KrЮЭШЯ, V. I., KТЯТЧТОЦТ, S. N. & RЮШФШХКТЧОЧ, . V. 2001. . ., . ., . ., . . (Aphyllophorales s. ХКЭШ) ДAЩСвХХШЩСШrШТН fungi (Aphyllophorales s. ХКЭШ)Ж. – IЧ: IЧЯОЧЭШrв КЧН sЭЮНв ШП ЛТШХШРТМКХ НТЯОrsТЭв ТЧ CОЧЭrКХ KКrОХТК (ЧОаsХОЭЭОr). KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 101–105. (IЧ RЮssТКЧ). RКssТ, P. HвЯтrТЧОЧ, E, JЮsХцЧ, A. & MКЧЧОrФШsФТ, I. (ОНs.), 2010. SЮШЦОЧ ХКУТОЧ ЮСКЧКХКТsЮЮs. PЮЧКТЧОЧ ФТrУК. TСО 2010 RОН LТsЭ ШП FТЧЧТsС SЩОМТОs. – HОХsТЧФТ, 2010. Щ. 249–263. RОН DКЭК BШШФ ШП ЧКЭЮrО ШП LОЧТЧРrКН RОРТШЧ. PХКЧЭs КЧН ПЮЧРТ (2000). – SЭ. PОЭОrsЛЮrР. 671 Щ. Reports of the Finnish Environment Institute 40 | 2014 241 RОН DКЭК BШШФ ШП ЭСО RЮssТКЧ FОНОrКЭТШЧ (PХКЧЭs КЧН ПЮЧРТ) (2008). ( ). – MШsМШа. 855 Щ. (IЧ RЮssТКЧ). RЮШФШХКТЧОЧ, . V. 2013 . . . ( ) ДAЩСвХХШЩСШrШТН ПЮЧРТ ШП ЭСО ГКШЧОгСвО PОЧТЧsЮХК, RОЩЮЛХТМ ШП KКrОХТКЖ. - IЧ: MШНОrЧ ЛШЭКЧв ТЧ RЮssТК. – PrШМООНТЧРs ШП ЭСО 13ЭС CШЧРrОss ШП ЭСО RЮssТКЧ BШЭКЧТМКХ SШМТОЭв КЧН ЭСО CШЧПОrОЧМО “SМТОЧЭТiМ ПЮЧНКЦОЧЭКХs ШП ЭСО ЩrШЭОМЭТШЧ КЧН МШЧsОrЯКЭТШЧ ШП ЭСО ЩХКЧЭ МШЯОr ШП ЭСО VШХРК ЛКsТЧ” (TШРХТКЭЭТ, 16–22 SОЩЭОЦЛОr 2013). VШХ. 1: EЦЛrвШХШРв. SЭrЮМЭЮrКХ ЛШЭКЧв. AХРШХШРв. MвМШХШРв. LТМСОЧШХШРв. BrвШХШРв. PКХОШЛШЭКЧв. BТШsвsЭОЦКЭТМs. TШРХТКЭЭТ: CКssКЧНrК. Щ. 173–174. (IЧ RЮssТКЧ). RЮШФШХКТЧОЧ, . V. 2013 Л. . . ДAЩСвХХШЩСШrШТН ПЮЧРЮs ЛТШЭК ШП ЭСО KТгСТ ArМСТЩОХКРШЖ. – IЧ: PrШМ. AХХ-RЮss. CШЧП. “BТШНТЯОrsТЭв ШП FКr NШrЭСОrЧ ОМШsвsЭОЦs: ТЧЯОЧЭШrв, ЦШЧТЭШrТЧР КЧН ЩrШЭОМЭТШЧ” (SвФЭвЯФКr, 3–7 JЮЧО 2013). SвФЭвЯФКr: IЧsЭТЭЮЭО ШП BТШХШРв, KШЦТ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs, UrКХТКЧ BrКЧМС, RAS, Щ. 248–250. (IЧ RЮssТКЧ). RЮШФШХКТЧОЧ, . V. 2013 М. . . ДАШШН-НОsЭrШвТЧР ПЮЧРТЖ. – IЧ: GrШЦЭsОЯ A.N. (ОН.) SОХФт ХКЧНsМКЩОs ШП ЭСО ГКШЧОгвО PОЧТЧsЮХК: NКЭЮrО, НОЯОХШЩЦОЧЭ, LКЧН ЮsО, CШЧsОrЯКЭТШЧ. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 102–108. (IЧ RЮssТКЧ). Table 2. Numbers of wood-growing fungal species recorded on Zaonezhye Peninsula (nomenclature according to Index Fungorum 2014). Order/Family Species Agaricomycetes Incertae sedis Odonticium (1) Agaricales Cyphellaceae Chondrostereum (1) Incertae sedis Plicatura (1) Atheliales Atheliaceae Amphynema (1), Piloderma (1) Auriculariales Auriculariaceae Elmerina (1) Incertae sedis Pseudohydnum (1) Boletales Amylocorticiaceae Amylocorticium (2), Ceraceomyces (2) Coniophoraceae Coniophora (2) Serpulaceae Serpula (1) Tapinellaceae Pseudomerulius (1) Cantharellales Botryobasidiaceae Botryobasidium (3), Botryohypochnus (1) Cantharellaceae Cantharellus (1), Clavulina (1), Craterellus (2) Clavulinaceae Multiclavula (1) Hydnaceae Hydnum (2), Sistotrema (1) Corticiales Corticiaceae Corticium (1), Cytidia (1) Dacrymycetales Dacrymycetaceae Calocera (1) Gloeophyllales Gloeophyllaceae Gloeophyllum (2), Veluticeps (1) Gomphales Clavariadelphaceae Clavariadelphus (2) Gomphaceae Ramaria (3) Lentariaceae Kavinia (1), Lentaria (1) Hymenochaetales 242 Hymenochaetaceae Asterodon (1), Coltricia (1), Hymenochaete (1), Inonotus (3), Onnia (1), Phellinus (14), Pseudochaete (1), Tubulicrinis (2) Repetobasidiaceae Sidera (1), Resinicium (2) Reports of the Finnish Environment Institute 40 | 2014 Schizoporaceae Basidioradulum (1), Hyphodontia (12), Schizopora (1) Polyporales Fomitopsidaceae Amylocystis (1), Anomoporia (1), Antrodia (9), Climacocystis (1), Fomitopsis (2), Ischnoderma (1), Laetiporus (1), Phaeolus (1), Piptoporus (1), Postia (10), Pycnoporellus (2) Ganodermataceae Ganoderma (2) Meripilaceae Oxyporus (2), Physisporinus (1), Rigidoporus (1) Meruliaceae Bjerkandera (1), Crustoderma (2), Gloeoporus (3), Hyphoderma (1), Junghuhnia (4), Merulius (1), Mycoacia (2), Phlebia (6), Radulodon (1), Steccherinum (2) Phanerochaetaceae Antrodiella (4), Ceriporia (2), Ceriporiopsis (2), Phanerochaete (4), Phlebiopsis (1) Polyporaceae Aurantiporus (1), Cerrena (1), Daedaleopsis (3), Datronia (1), Dichomitus (1), Diplomitoporus (2), Fomes (1), Hapalopilus (1), Haploporus (1), Lenzites (1), Leptoporus (1), Perenniporia (1), Piloporia (1), Polyporus (5) Pycnoporus (1), Rhodonia (1), Skeletocutis (7), Trametes (5), Trichaptum (4) Xenasmataceae Phlebiella (1) Russulales Albatrellaceae Albatrellus (2) Amylostereaceae Amylostereum (1) Auriscalpiaceae Auriscalpium (1), Clavicorona (1) Bondarzewiaceae Gloiodon (1), Heterobasidion (1) Hericiaceae Hericium (2), Laxitextum (1) Lachnocladiaceae Dichostereum (1), Scytinostroma (2) Peniophoraceae Peniophora (2) Stereaceae Chaetoderma (1) Gloiothele (1) Stereum (4) Thelephorales Bankeraceae Bankera (1), Boletopsis (1), Hydnellum (3), Phellodon (2), Sarcodon (3) Thelephoraceae Thelephora (1), Tomentella (6) Trechisporales Hydnodontaceae Trechispora (2) Reports of the Finnish Environment Institute 40 | 2014 243 APPENDIX List of fungi recorded from Zaonezhye Peninsula, Syar-Peninsula and adjacent islands NOTES: Each species is provided by an estimation of frequency in Zaonezhye according to the following scale: rr (very rare), r (rare), str (fairly rare), p (here and there), stfq (fairly frequent), fq (frequent and very frequent). Species status: * - Indicator species of old-growth and deciduous forests (Kotiranta & Niemelä 1996); ** - Specialist and indicator species of minimally transformed forest (Andersson et al. 2009). Threat status: EN, NT, VU, DD − species included in the Red Data Book of Karelia, Kar (Ivanter & Kuznetsov 2007) and in the 2010 Red list of Finnish species, Fin (Rassi et al. 2010); 2, 3, 4 - Species included in the Red Data Book of nature of Leningrad Region, Len (Red Data Book…2000). ABBREVIATIONS: Bol. Klim. Isl. − Bolshoi Klimenetsky Island, comp. − forest compartment (kvartal or quartal in Russian). ** Albatrellus conluens (Alb. et Schwein. : Fr.) Kotl. et Pouzar – Syar peninsula, comp. 180, 182, north of Tambitsy, environs of Tolsty Navolok, comp. 71, pine and spruce forest, on litter, 22.08.2013, 26.08.2013, A.V. Ruokolainen; 18–19.08.2013, O. Manninen; str. A. ovinus (Schaeff.) Kotl. et Pouzar – Ruokolainen 2013 c; Lipovitsy, comp. 41, Lake Korbozero, Tipinitsy, spruce-dominated and mixed forest, on litter, 23.08.2013, 27.08.2013, A.V. Ruokolainen; str. Amphynema byssoides (Pers. : Fr.) J. Erikss. – Ruokolainen 2013 c; pine forest, comp. 13, on fallen spruce, 22.08.2013; p. Amylocorticium suaveolens Parmasto – Ruokolainen 2013 a, c; Velikaya Niva, motley grass spruce forest, on fallen spruce, 23.08.2012, A.V. Ruokolainen, PTZ; Tambitsy, Myrtillus spruce forest, on fallen spruce, 28.08.2013, A.V. Ruokolainen, PTZ; str. A. subincarnatum (Peck) Pouzar – Ruokolainen 2013 c; spruce forest, on fallen spruce. Threat status: Fin – VU; str. *, ** Amylocystis lapponica (Romell) Singer – Ruokolainen 2013 a, c; Lipovitsy; Lake Korbozero, Tipinitsy, north of Tambitsy, environs of Tolsty Navolok, comp. 71, Myrtillus spruce forest, on fallen spruce, 21.08.2013, 26.08.2013, 27.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 152–153, 174–176, 180–181, 16–17.08.2013, 19.08.2013, O. Manninen; str. Threat status: Fin – NT. Amylostereum chailletii (Pers.) Boidin – Ruokolainen 2013 a; Lipovitsy, comp. 41, Myrtillus spruce forest, on fallen spruce, 23.08.2013, A.V. Ruokolainen, PTZ; str. *, ** Anomoporia kamtschatica (Parmasto) Bondartseva – old-growth pine-dominated forest, on dead pine, 27.06.2013 and 22.08.2013, O. Manninen; rr. *, ** Antrodia albobrunnea (Romell) Ryvarden – Syar peninsula, comp. 153, 182, 183, old-growth pine-dominated forest, on dead pine, 17.08.2013 and 18.08.2013, O. Manninen; stp. Threat status: Fin – NT. * A. crassa (P. Karst.) Ryvarden – Documentation ... 2013; Syar peninsula, comp. 187, old-growth pine-dominated forest, 19.08.2013, O. Manninen; r. Threat status: Kar – 2 (EN), Len – 2, Fin – EN. A. heteromorpha (Fr. : Fr.) Donk – Syar peninsula, comp. 180, on aspen, 19.08.2013, O. Manninen; r. *A. inirma Rennvall et Niemelä – Syar peninsula, comp. 180, 183, 18–19.08.2013; 24.08.2013, O. Manninen; r. Threat status: Fin – VU. 244 Reports of the Finnish Environment Institute 40 | 2014 *, ** A. pulvinascens (Pilát) Niemelä – Documentation ... 2013; Syar peninsula, comp. 181, 19.08.2013, 24.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Fin – VU. A. serialis (Fr.) Donk – Bondartseva et al. 1999; Ruokolainen 2013 c; southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 03.07.1997, A.V. Ruokolainen, PTZ; fq. A. sinuosa (Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 c; southern part on Bol. Klim. Isl., spruce forest on fallen pine, 06.07.1997, A.V. Ruokolainen, PTZ; fq. A. sitchensis (D.V. Baxter) Gilb. et Ryvarden – 24.08.2013, O. Manninen; r. Threat status: Fin – EN. A. xantha (Fr. : Fr.) Ryvarden – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 06.07.1997, A.V. Ruokolainen, PTZ; fq. *, ** Antrodiella citrinella Niemelä et Ryvarden – Documentation ... 2013; rr. Threat status: Kar – 3 (VU), Fin – NT. A. hoehnelii (Bres.) Niemelä – mixed forest on deadwood of deciduous trees, 23.08.2013, O. Manninen; rr. Threat status: Len – 3. A. pallasii Renvall, Johann. et Stenlid – Tambitsy, Myrtillus spruce forest, on fallen spruce, 27.08.2013, A.V. Ruokolainen, PTZ; r. A. pallescens (Pilát) Niemelä et Miettinen – Ruokolainen 2013 c; Zharnikovo, mixed forest on fallen Sorbus aucuparia, 01.08.2012, A.V. Ruokolainen, PTZ; p. *, **Asterodon ferruginosus Pat. – Ruokolainen 2013 c; Syar peninsula, comp. 178, 186, 18- 19.08.2013, O. Manninen; Lipovitsy, comp. 41, north of Tambitsy, environs of Tolsty Navolok, comp. 71, 23.08.2013, 26.08.2013, 28.08.2013, spruce forest on fallen aspen, pine and spruce, A.V. Ruokolainen; pine forest, comp. 13, on fallen pine, 22.08.2013, A.V. Ruokolainen, PTZ; stp. ** Aurantipoporus issilis (Berk et M.A. Curtis) H. Jahn [= Tyromyces issilis (Berk et M.A. Curtis) Donk] – Documentation ... 2013; on deciduous trees, 24.08.2013, O. Manninen; rr. Threat status: Kar – 3 (VU), Len – 3, Fin – NT. Auriscalpium vulgare Gray – near the road, 28.06.2013, O. Manninen; r. ** Bankera fuligineoalba (J.C. Schmidt) Coker et Beers ex Pouzar – Syar peninsula, comp. 185, pine forest, on litter, 19.08.2013, O. Manninen; r. Basidioradulum radula (Fr.) Nobles – Ruokolainen 2013 c; Zharnikovo, mixed forest on deadwood of Sorbus aucuparia, 01.08.2012, A.V. Ruokolainen; Palozero, mixed forest, on deadwood of deciduous trees, 23.08.2012, A.V. Ruokolainen; p. Bjerkandera adusta (Willd.: Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., H; Kizhi Isl., on deadwood of Sorbus aucuparia, 16.07.1998, V.I. Krutov, PTZ; Tipinitsy, spruce forest, on aspen, 27.08.2013; Tambitsy, spruce forest, on aspen, 28.08.2013, A.V. Ruokolainen; stfq. ** Boletopsis grisea (Peck) Bondartsev et Singer – Ruokolainen 2013 a; south of the village of Lambasruchei, pine forest, on litter, 23.08.2012, A.V. Ruokolainen; r. Threat status: Fin – NT. Botryobasidium laeve (J. Erikss.) Parmasto – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on fallen spruce; p. B. subcoronatum (Höhn. et Litsch.) Donk – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on fallen spruce; stp. B. vagum (Berk. et M.A. Curtis) D.P. Rogers – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., on fallen spruce, 05.07.1997, A.V. Ruokolainen, PTZ; p. Botryohypochnus isabellinus (Fr.) J. Erikss. – Ruokolainen 2013 c; Zharnikovo, mixed forest, on dead Alnus incana, 01.08.2012, A.V. Ruokolainen; p. Calocera viscosa (Pers. : Fr.) Fr. – Ruokolainen 2013 c; environs of Velikaya Niva, mixed spruce-dominated forest, on litter, 23.08.2012, A.V. Ruokolainen; p. Cantharellus cibarius Fr. – Ruokolainen 2013 c; south of the village of Lambasruchei, pine forest, on litter, 23.08.2012, A.V. Ruokolainen; common species, stfq. Reports of the Finnish Environment Institute 40 | 2014 245 Ceraceomyces microsporus K.H. Larss. – Ruokolainen 2013 c; pine forest, near the lake, comp. 13, on fallen pine, 22.08.2013, A.V. Ruokolainen, PTZ; p. C. serpens (Tode : Fr.) Ginns – Ruokolainen 2013 c; Paltega, motley grass birch forest, on fallen birch, 06.08.2011, A.V. Ruokolainen, PTZ; p. Ceriporia excelsa S. Lundell ex Parmasto – Ruokolainen 2013 a, b, c; Kizhi Isl., on fallen Sorbus aucuparia, 04.08.2012, A.V. Ruokolainen, PTZ; rr. Threat status: Fin – NT. C. viridans (Berk. et Broome) Donk – Ruokolainen 2013 a; northeast of Velikaya Guba, on fallen Alnus incana, 17.08.2010, A.V. Ruokolainen, PTZ; rr. Ceriporiopsis aneirina (Sommerf. : Fr.) Domański – on dead aspen, 26.06.2013, O. Manninen; rr. Threat status: Len – 3. C. resinascens (Romell) Domański – Ruokolainen 2013 c; Polya, mixed forest, on fallen aspen, 25.08.2013, A.V. Ruokolainen, PTZ; 27–28.08.2013, O. Manninen; r. Threat status: Len – 3. Cerrena unicolor (Bull.) Murrill – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen birch, 06.07.1997, A.V. Ruokolainen; Zharnikovo, mixed forest, on deadwood of Salix caprea, 01.08.2012, A.V. Ruokolainen, stfq. *, ** Chaetoderma luna (Romell ex Rogers et H.S. Jacks.) Parmasto – Ruokolainen 2013 c; environs of Velikaya Niva, pine forest, on dead pine, 17.08.2010; A.V. Ruokolainen; Syar peninsula, comp. 180, 183, pine forest, on dead pine, 18–19.08.2013, O. Manninen; r. Chondrostereum purpureum (Pers. : Fr.) Pouzar – Bondartseva et al. 1999; Kizhi Isl., on deadwood of alder, 16.07.1998, V.I. Krutov, PTZ; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest, on fallen birch, 26.08.2013, A.V. Ruokolainen; p. Clavariadelphus ligula (Schaeff. : Fr.) Donk – Ruokolainen 2013 c; south of the village of Lambas Ruchei, pine forest, on litter, 23.08.2012, A.V. Ruokolainen; r. ** C. pistillaris (L. : Fr.) Donk – Documentation ... 2013; on litter, 23.08.2013 and 26.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Len – 3. Clavicorona pyxidata (Pers.) Doty – Bondartseva et al. 1999; Ruokolainen 2013 c; Korbozero, Tipinitsy, Lipovitsy, comp. 41, north of Tambitsy, environs of Tolsty Navolok, comp. 71, mixed spruce-dominated forest, on fallen aspen, 23.08.2013, 26–27.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 178, 186, 16.08.2013, 18–19.08.2013, O. Manninen; p. Clavulina cinerea (Bull. : Fr.) J. Schröt. – Ruokolainen 2013 a; Podyelniki, ecological trail, on litter, 03.08.2012, A.V. Ruokolainen, PTZ; Kizhi Isl., on litter, 04.08.2012, A.V. Ruokolainen, PTZ; r. ** Climacocystis borealis (Fr.) Kotl. et Pouzar – Ruokolainen 2013 a, c; Lipovitsy, comp. 41, north of Tambitsy, environs of Tolsty Navolok, comp. 71, Tipinitsy, mixed herb-rich and spruce forest, on dead spruce, 23.08.2013, 26–27.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 153, 178, 181, 16.08.2013, 17–19.08.2013, O. Manninen; stfq. Coltricia perennis (L. : Fr.) Murrill – Ruokolainen 2013 c; near Lake Nizhnee Pigmosero, on dead Salix, 22.08.2012, A.V. Ruokolainen; pine forest, comp. 13, on litter, 22.08.2013, A.V. Ruokolainen; p. Coniophora arida (Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 c; fq. C. olivacea (Pers. : Fr.) P. Karst. – Ruokolainen 2013 c; Ruokolainen 2013 c; fq. Corticium roseum Pers. : Fr. – Ruokolainen 2013 c; north of Tambitsy, environs of Tolsty Navolok, comp. 71, Korbozero, Tipinitsy, spruce and mixed forest, on fallen aspen, A.V. Ruokolainen; p. Craterellus cornucopioides (L. : Fr.) Pers. – Ruokolainen 2013 c; environs of Velikaya Niva, spruce forest, on deadwood of Salix, 23.08.2012, A.V. Ruokolainen; Lipovitsy, comp. 41, Tambitsy, spruce forest on litter, 23.08.2013, 28.08.2013, A.V. Ruokolainen; stp. Threat status: Kar – 3 (NT). C. tubaeformis (Fr.) Quél. – Lipovitsy, spruce forest, on litter, stp. 246 Reports of the Finnish Environment Institute 40 | 2014 *, ** Crustoderma corneum (Bourdot et Galzin) Nakasone – Syar peninsula, comp. 180, 182–183, on fallen pine, 18–19.08.2013; 22.08.2013, O. Manninen; r. Threat status: Fin – NT. *, ** C. dryinum (Berk. et M.A. Curtis) Parmasto – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on fallen spruce, 10.08.2010, A.V. Ruokolainen; Lipovitsy, Myrtillus spruce forest, on fallen spruce, 21.08.2013, A.V. Ruokolainen, PTZ; north of Tambitsy, environs of Tolsty Navolok, comp. 71, 26.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 154, 17.08.2013, O. Manninen; stp. Threat status: Fin – NT. Cytidia salicina (Fr.) Burt – Ruokolainen 2013 c; near Lake Nizhnee Pigmosero, on deadwood of Salix, 22.08.2012, A.V. Ruokolainen; stp. Daedaleopsis confragosa (Bolton) Schröt. – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., on deadwood of Sorbus aucuparia, 16.07.1998, V.I. Krutov, PTZ; Bol. Klim. Isl., LE; like Kopanez, on birch, 15.07.1999, A.V. Polevoi, PTZ; Zharnikovo, mixed and birch forest on fallen Alnus incana and Salix, A.V. Ruokolainen; p. D. septentrionalis (P. Karst.) Niemelä – Ruokolainen 2013 c; environs of Velikaya Niva, pine forest, on dead birch, 23.08.2012; stp. D. tricolor (Bull. : Fr.) Bondartsev et Singer – Bondartseva et al. 1999; Kizhi Isl., LE; like Kopanez, on dead birch, 15.07.1999, A.V. Polevoi, PTZ; stp. Datronia mollis (Sommerf.) Donk – Bondartseva et al. 1999; Ruokolainen 2013 c; north of Tambitsy, environs of Tolsty Navolok, comp. 71, Tambitsy, Kaskoselga, south of Uzkaya Salma, mixed forest, on birch and aspen, 11.08.2010, 13.08.2010, 26.08.2013, 28.08.2013, A.V. Ruokolainen; p. * Dichomitus squalens (P. Karst.) D.A. Reid – Ruokolainen 2013 c; pine-dominated forest, on fallen spruce, 17.08.2010, A.V. Ruokolainen; r. Threat status: Kar – 3 (NT), Fin – VU. Dichostereum boreale (Pouzar) Ginns et M.N.L. Lefebvre – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on fallen spruce, 10.08.2010, A.V. Ruokolainen; stp. *, ** Diplomitoporus crustulinus (Bres.) Domański – Ruokolainen 2013 a, c; south of the village of Uzkaya Salma, moist spruce forest, on fallen spruce, 13.08.2010, A.V. Ruokolainen, PTZ; rr. Threat status: Fin – VU. D. lavescens (Bres.) Ryvarden – Ruokolainen 2013 a; Velikaya Guba, pine forest, on pine, 17.08.2010, A.V. Ruokolainen, PTZ; Ladmozero, old-growth pine forest, on dead pine, 24.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 174, 177, 180, old-growth pine forest, on dead pine, 17–19.08.2013, O. Manninen; stp. Threat status: Fin – NT. Elmerina caryae (Schwein) D.A. Rein [= Protomerulius caryae (Schwein) Ryvarden] – Bondartseva et al. 2000; Documentation ... 2013; Syar peninsula, comp. 180, 19.08.2013, O. Manninen; rr. Threat status: Kar – 3 (VU), Len – 3, Fin – NT. Fomes fomentarius (L.) Fr. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; mixed spruce-dominated forest, on dead birch, fq. Fomitopsis pinicola (Sw. : Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; mixed spruce-dominated forest on deadwood of birch, fq. *, ** F. rosea (Alb. et Schwein. : Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; Lipovitsy, comp. 41, Podyelniki, north of Tambitsy, environs of Tolsty Navolok, comp. 71, Tipinitsy, south of the village of Uzkaya Salma et al., spruce forest on deadwood of spruce, A.V. Ruokolainen; Syar peninsula, comp. 133, 151–154, 174–177, 180–183, 186, 17–19.08.2013, O. Manninen; p. Threat status: Fin – NT. Ganoderma applanatum (Pers.) Pat. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., H; Bol. Klim. Isl., LE; Zharnikovo, mixed forest, on deadwood of Sorbus aucuparia and Salix caprea, 01.08.2012, A.V. Ruokolainen; Lipovitsy, comp. 41, spruce forest on fallen aspen, 23.08.2013, A.V. Ruokolainen; p. ** G. lucidum (M. A. Curtis : Fr.) P. Karst. – Documentation ... 2013; Lake Korbozero, Tipinitsy, mixed forest on old birch, 27.08.2013, A.V. Ruokolainen, PTZ; rr. Threat status: RF – 3, Len – 3, Kar – 3 (VU). Reports of the Finnish Environment Institute 40 | 2014 247 Gloeophyllum odoratum (Wulfen : Fr.) Imazeki – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., H; near Lake Nizhnee Pigmosero, on deadwood of pine, 22.08.2012, A.V. Ruokolainen; Tipinitsy, spruce forest, on deadwood of spruce, 27.08.2013, A.V. Ruokolainen; r. G. sepiarium (Wulfen : Fr.) P. Karst. – Bondartseva et al. 1999; Bol. Klim. Isl., LE; near Lake Nizhnee Pigmosero, on deadwood of spruce, 22.08.2012, A.V. Ruokolainen; p. Gloeoporus dichrous (Fr. : Fr.) Bres. – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., LE; Zharnikovo, Tipinitsy, spruce and mixed forest, on birch, aspen and Sorbus aucuparia; p. ** G. pannocinctus (Romell) J. Erikss. – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; north of Podyelniki, spruce forest on fallen aspen, 11.08.2010, A.V. Ruokolainen, PTZ; stp. Threat status: Len – 3. *, ** G. taxicola (Pers. : Fr.) Gilb. et Ryvarden – Ruokolainen 2013 b, c; Lipovitsy, comp. 43, south of Lipovitsy, comp. 63, Myrtillus spruce forest, on fallen spruce, 18.08.2010, A.V. Ruokolainen, PTZ; Zharnikovo, pine forest on fallen pine, 02.08.2012, A.V. Ruokolainen, PTZ; Podyelniki, pine forest on fallen pine, 03.08.2012, A.V. Ruokolainen; 22–24.08.2013, O. Manninen; stp. Threat status: Len – 3. *, ** Gloiodon strigosus (Schwein. : Fr.) P. Karst. – Documentation ... 2013; mixed forest, on deadwood of deciduous trees (aspen, Salix caprea), 23–24.08.2013, 28.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Fin – NT. Gloeothele citrina (Pers.) Ginns et G.W. Freeman – Ruokolainen 2013 c; Podyelniki, Zubovo, on fallen pine, 03.08.2012, A.V. Ruokolainen, PTZ; stp. Hapalopilus rutilans (Pers.) P. Karst. – Ruokolainen 2013 c; like Kopanez, on dead birch, 15.07.1999, A.V. Polevoi, PTZ; Zharnikovo, mixed forest, on deadwood of birch, 01.08.2012, A.V. Ruokolainen; near Lake Nizhnee Pigmosero, on deadwood of birch, 22.08.2012, A.V. Ruokolainen; p. ** Haploporus odorus (Sommerf. : Fr.) Bondartsev et Singer – Documentation ... 2013; comp. 183, on old Salix caprea, 18.08.2013, O. Manninen; rr. Threat status: Kar – 3 (VU), Len – 3, Fin – NT. Hericium cirrhatum (Pers.) Nikol. – Ruokolainen 2013 c; Zharnikovo, environs of Velikaya Niva, mixed and spruce-dominated forest, on Salix caprea and aspen, 05.08.2012, 23.08.2012, A.V. Ruokolainen; r. Threat status: Len – 3. ** H. coralloides (Scop.) Pers. – Ruokolainen 2013 c; Bol. Klim. Isl., on deadwood of deciduous trees, 09.08.2010; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest on birch and aspen, 26.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 132, 180, 185, 16.08.2013, 19.08.2013, O. Manninen; stp. Threat status: Kar – 3 (NT). Heterobasidion parviporum Niemelä et Korhonen – Bondartseva et al. 1999; Ruokolainen 2013 b; Bol. Klim. Isl., LE; Bol. Klim. Isl., spruce forest, on fallen spruce, 03.07.1997, A.V. Ruokolainen, PTZ; stp. Hydnellum aurantiacum (Batsch) P. Karst. – Ruokolainen 2013 , c; Ladmozero, south of the village of Lambasruchei, Vanchozero, pine forest on litter, 24–25.08.2012, A.V. Ruokolainen; stp. H. caeruleum (Hornem.) P. Karst. – Ruokolainen 2013 c; Vanchozero, pine forest, on litter, 25.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 185, 19.08.2013, O. Manninen; stp. H. ferrugineum (Fr.) P. Karst. – Ruokolainen 2013 c; north of Podyelniki, south of the village of Lambasruchei, Vanchozero, pine forest on litter, 11.08.2010, 24–25.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 154, 177, 180, 182, 185, 17–19.08.2013, O. Manninen; stp. Hydnum repandum L. : Fr. – Ruokolainen 2013 c; environs of Velikaya Niva, spruce forest, on litter, 23.08.2012, A.V. Ruokolainen; stp. 248 Reports of the Finnish Environment Institute 40 | 2014 H. rufescens Schaeff. : Fr. – Ruokolainen 2013 c; environs of Velikaya Niva, spruce forest, on litter, 23.08.2012, A.V. Ruokolainen; stp. Hymenochaete rubiginosa (Fr.) Lév. – Bondartseva et al. 1999; Klimenetsky Isl., LE; southern part of Bol. Klim. Isl., 07.07.1997, A.V. Ruokolainen, PTZ; r. Hyphoderma setigerum (Fr.) Donk – Bondartseva et al. 1999; Kizhi Isl., LE; Kizhi Isl., on Sorbus aucuparia and Alnus incana, 16.07.1998, V.I. Krutov, PTZ; r. Hyphodontia abieticola (Bourdot et Galzin) J. Erikss. – Lake Korbozero, Tipinitsy, mixed forest on fallen pine, 27.08.2013, A.V. Ruokolainen, PTZ; stp. H. alienata (S. Lundell) J. Erikss. – Ruokolainen 2013 c; Lipovitsy, spruce forest, on fallen spruce, 21.08.2013, A.V. Ruokolainen, PTZ; stp. H. alutacea (Fr.) J. Erikss. – Ruokolainen 2013 c; north of Podyelniki, on fallen spruce, 11.08.2010, A.V. Ruokolainen; stp. H. alutaria (Burt) J. Erikss. – Ruokolainen 2013 c; 1,5 km southwestern of Velikaya Guba, Myrtillus pine forest on fallen pine, 19.08.2010, A.V. Ruokolainen, PTZ; north of Podyelniki, on fallen spruce, 10.08.2010, A.V. Ruokolainen; stp. H. arguta (Fr.) J. Erikss. – Ruokolainen 2013 c; Zharnikovo, mixed forest, on deadwood of Salix caprea and Sorbus aucuparia, 05.08.2012, A.V. Ruokolainen; stp. H. aspera (Fr.) J. Erikss. – Ruokolainen 2013 c; north of Podyelniki, on fallen pine and spruce, 10–11.08.2010, A.V. Ruokolainen; p. H. barba-jovis (Bull. : Fr.) J. Erikss. – Ruokolainen 2013 c; south of Tambitsy, birch forest with spruce on fallen birch, 04.08.2011, A.V. Ruokolainen, PTZ; p. H. breviseta (P. Karst.) J. Erikss. – Ruokolainen 2013 c; Zharnikovo, pine forest, on fallen pine; p. H. crustosa (Pers. : Fr.) J. Erikss. – Bondartseva et al. 1999; Kizhi Isl., on Alnus incana, LE; r. H. detritica (Bourdot et Galzin) J. Erikss. – Polya, mixed forest on fallen aspen, 25.08.2013, A.V. Ruokolainen, PTZ; r. H. pruni (Lasch) Svrček – Bondartseva et al. 1999; Kizhi Isl., on deadwood of Ulmus, LE; r. H. subalutacea (P. Karst.) J. Erikss. – Bondartseva et al. 1999; Bol. Klim. Isl., LE; by the lake in pine forest, comp. 13, on fallen pine, 22.08.2013, A.V. Ruokolainen, PTZ; stp. Inonotus obliquus (Pers. : Fr.) Pilát – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., on Alnus incana, 16.07.1998, S.N. Kiviniemi, V.I. Krutov, PTZ; stfq. I. radiatus (Sowerby : Fr.) P. Karst. – Ruokolainen 2013 c; Lipovitsy, comp. 41, environs of Tolsty Navolok, comp. 71, on deadwood of Alnus incana, 23.08.2013, 26.08.2013, A.V. Ruokolainen; stp. I. rheades (Pers.) Bondartsev et Singer – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; north of Podyelniki, mixed forest on deadwood of aspen, 03.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 174, 176, 17.08.2013, O. Manninen; stp. Ischnoderma bensoinum (Wahlenb. : Fr.) P. Karst. – Ruokolainen 2013 c; north of Podyelniki, environs of Tolsty Navolok, comp. 71, Lake Korbozero, Tipinitsy, Polya, comp. 82–83, spruce forest, on deadwood of spruce, 11.08.2010, 05.08.2011, 26–27.08.2013, A.V. Ruokolainen; stp. *, ** Junghuhnia collabens (Fr.) Ryvarden – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 05.07.1997, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 180, 183, 18–19.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Len – 3, Fin – NT. * J. luteoalba (P. Karst.) Ryvarden – Ruokolainen 2013 c; Velikaya Guba, Myrtillus pine forest on fallen pine, 08.08.2011, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 154, 17.08.2013, O. Manninen; r. Reports of the Finnish Environment Institute 40 | 2014 249 J. nitida (Pers. : Fr.) Ryvarden – on deadwood of deciduous trees, 24.08.2013, O. Manninen; rr. ** J. pseudozilingiana (Parmasto) Ryvarden – Ruokolainen 2013 c; Bolshoi Lelikovskiy Isl., pine forest with spruce on old birch, 09.08.2010, A.V. Ruokolainen, PTZ; Lipovitsy, spruce forest on deadwood of aspen, 21.08.2013, A.V. Ruokolainen, PTZ; Tambitsy, spruce forest with aspen, on fallen aspen, 28.08.2013, A.V. Ruokolainen, PTZ; stp. Threat status: Kar – 4 (DD), Len – 4, Fin – VU. ** Kavinia alboviridis (Mordan) Gilb. et Budington – Documentation ... 2013; Syar peninsula, comp. 134, south of Tambitsy, spruce forest on deadwood, 28.08.2013, O. Manninen; rr. Threat status: Kar – 4 (DD). Laetiporus sulphureus (Bull. : Fr.) Murrill - Lipovitsy, comp. 41, spruce forest on deadwood of aspen, 23.08.2013, A.V. Ruokolainen; rr. Laxitextum bicolor (Pers.) Lentz – Ruokolainen 2013 c; near Lake Nizhnee Pigmosero, on Alnus incana, 22.08.2012, A.V. Ruokolainen; stp. Lentaria byssiseda (Pers. : Fr.) Corner – Polya, mixed forest on Salix, 25.08.2013, A.V. Ruokolainen, PTZ; rr. Lenzites betulina (L.) Fr. – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., on deadwood of Sorbus aucuparia, LE; stp. *, ** Leptoporus mollis (Pers.) Quél. – Ruokolainen 2013 c; south of Tambitsy, birch forest with spruce on fallen spruce, 04.08.2011, A.V. Ruokolainen, PTZ; Lipovitsy, comp. 41, spruce forest on on deadwood of spruce, 23.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 133, 178, on deadwood of spruce. 16.08.2013, 18.08.2013, O. Manninen; stp. Threat status: Kar – 3 (NT), Len – 3. Merulius tremellosus Schrad. : Fr. – Ruokolainen 2013 c; Zharnikovo, mixed forest, on deadwood of aspen, 05.08.2012, A.V. Ruokolainen; Lipovitsy, spruce forest on fallen aspen, 21.08.2013, A.V. Ruokolainen; Lake Korbozero, Tipinitsy, spruce forest, on deadwood of aspen, 27.08.2013, A.V. Ruokolainen; p. ** Multiclavula mucida (Pers. : Fr.) R.H. Petersen – northwest of the Vatnavolok village, Syar peninsula, comp. 174, on deadwood of aspen, 17.08.2013, O. Manninen; 24.08.2013, O. Manninen; north of Tambitsy, environs of Tolsty Navolok, comp. 71, mixed forest, on deadwood of aspen, 26.08.2013, A.V. Ruokolainen; stp. Mycoacia fuscoatra (Fr. : Fr.) Donk – Lipovitsy, comp. 41, spruce forest on deadwood of aspen, 23.08.2013; stp. Threat status: Len – 3. M. uda (Fr.) Donk – Ruokolainen 2013 c; south of the village of Lambasruchei, Lake Onega shore, pine forest on fallen aspen, 24.08.2012, A.V. Ruokolainen, PTZ; stp. Odonticium romellii (S. Lundell) Parmasto – northwest of the Vatnavolok village, Syar peninsula, comp. 154, 180, 185, on deadwood of pine, 17.08.2013, 19.08.2013; 22.08.2013, 27.08.2013, O. Manninen; r. Threat status: Fin – NT. *, ** Onnia leporina (Fr.) H. Jahn – Ruokolainen 2013 c; Syar peninsula, comp. 154, 176, on deadwood of spruce, 17.08.2013, O. Manninen; north of Tambitsy, environs of Tolsty Navolok, Tambitsy, Lake Korbozero, Tipinitsy, comp. 71, 132, 177, 193, mixed herbrich and spruce forest on old deadwood spruce, 26–28.08.2013, A.V. Ruokolainen; stp. Oxyporus corticola (Fr.) Ryvarden – Bondartseva et al. 1999; southern part on Bol. Klim. Isl., spruce forest on fallen aspen, 04.07.1997, A.V. Ruokolainen, PTZ; Zharnikovo, mixed forest on fallen of Sorbus aucuparia, A.V. Ruokolainen; Syar peninsula, comp. 153, 180, 17.08.2013, 19.08.2013, O. Manninen; p. O. populinus (Schumach. : Fr.) Donk – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., H; Zharnikovo, mixed forest on Salix, A.V. Ruokolainen; Tambitsy, spruce forest on deadwood of aspen, 28.08.2013, A.V. Ruokolainen; p. Peniophora incarnata (Pers.) P. Karst. – Ruokolainen 2013 c; south of the village of Uzkaya Salma, moist spruce forest on fallen aspen, 13.08.2010, A.V. Ruokolainen, PTZ; p. 250 Reports of the Finnish Environment Institute 40 | 2014 P. rufa (Pers. : Fr.) M.P. Christ. – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; r. *, ** Perenniporia subacida (Peck) Donk – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; Polya, Myrtillus spruce forest, on fallen spruce, 25.08.2013, A.V. Ruokolainen, PTZ; r. Threat status: Fin – NT. *, ** Phaeolus schweinitzii (Fr.) Pat. – northwest of the Vatnavolok village, Syar peninsula, comp. 154, 184, in old-growth forest on the roors of pine, 17.08.2013, 19.08.2013, O. Manninen; r. Phanerochaete laevis (Fr.) J. Erikss. et Ryvarden – Ruokolainen 2013 c; environs of Velikaya Niva, spruce forest on deadwood of aspen, 23.08.2012, A.V. Ruokolainen; p. Ph. sanguinea (Fr.) Pouzar – Ruokolainen 2013 c; south of the village of Uzkaya Salma, north of Podyelniki, spruce forest on fallen pine and spruce, 11.08.2010, 13.08.2010, A.V. Ruokolainen; Tambitsy, spruce forest on deadwood of birch, 28.08.2013, A.V. Ruokolainen; p. Ph. sordida (P. Karst.) J. Erikss. et Ryvarden – Ruokolainen 2013 c; Zharnikovo, mixed forest, on Alnus incana, 05.08.2012; p. Ph. velutina (DC. : Fr.) P. Karst. – Tambitsy, Myrtillus spruce forest, on fallen spruce, 28.08.2013, A.V. Ruokolainen, PTZ; stp. Phellinus alni (Bondartsev) Parmasto – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., Zharnikovo, pine and mixed forest, on Alnus incana, A.V. Ruokolainen; p. *, ** Ph. chrysoloma (Fr.) Donk – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 03.07.1997, A.V. Ruokolainen, PTZ; north of Podyelniki, 03.08.2012, A.V. Ruokolainen; Lipovitsy, Polya, north of Tambitsy, environs of Tolsty Navolok, Tambitsy, Lake Korbozero, Tipinitsy, comp. 41, 71, 84, 177, 193 et al., spruce forest on old deadwood spruce, 23– 24.08.2013, 26–27.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 151–154, 177–178, 180–181, 183, 16–19.08.2013, O. Manninen; p. Ph. conchatus (Pers. : Fr.) Quél. – Ruokolainen 2013 b, c; like Kopanez, on deadwood of deciduous trees, 13.07.1999, A.V. Polevoi, PTZ; Lake Korbozero, Tipinitsy, environs of Velikaya Niva, Zharnikovo, north of Podyelniki, Polya, spruce and mixed forest on deadwood of Salix caprea, 23.08.2012, A.V. Ruokolainen; p. *, ** Ph. ferrugineofuscus (P. Karst.) Bourdot – Bondartseva et al. 1999; Ruokolainen 2013 a, c; Bol. Klim. Isl., LE; environs of Velikaya Niva, spruce forest on deadwood of spruce, 23.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 153–154, 174–178, 180, 181, 183, 186, 17–19.08.2013, O. Manninen; Lipovitsy, Polya, Lake Korbozero, north of Podyelniki, Tambitsy, Tipinitsy, comp. 41, 84, 177, 132, et al., A.V. Ruokolainen; p. Ph. igniarius (L. : Fr.) Quél. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., on deadwood of Salix caprea, 16.07.1998, V.I. Krutov, PTZ; Kizhi Isl., LE; southern part on Bol. Klim. Isl., LE; Zharnikovo, A.V. Ruokolainen; p. Ph. laevigatus (P. Karst.) Bourdot et Galzin – Ruokolainen 2013 c; Bolshoi Lelikovskiy Isl., pine forest with spruce on old deadwood birch, 09.08.2010, north of Podyelniki, south of the village of Uzkaya Salma, 10–11.08.2010, 13.08.2010, A.V. Ruokolainen; Syar peninsula, comp. 153, 17.08.2013, O. Manninen; stp. * Ph. lundelii Niemelä – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest on deadwood of birch, 07.07.1997, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 132, 176, 16–17.08.2013, O. Manninen; Lipovitsy, north of Tambitsy, environs of Tolsty Navolok, Tambitsy, A.V. Ruokolainen; stp. Ph. nigricans (Fr.) P. Karst. – Bondartseva et al. 1999 (Ph. igniarius); Ruokolainen 2013 b, c; Bolshoi Lelikovskiy Isl., southern part on Bol. Klim. Isl., Zharnikovo, Polya, Tambitsy, mixed spruce-dominated forest on dead birch; fq. *, ** Ph. nigrolimitatus (Romell) Bourdot et Galzin – Ruokolainen 2013 a, c; north of Podyelniki, Lipovitsy, spruce forest on dead spruce, 11.08.2010, 05–06.08.2011, 23.08.2013, Reports of the Finnish Environment Institute 40 | 2014 251 A.V. Ruokolainen; Syar peninsula, comp. 174, 176, 186, 17.08.2013, 19.08.2013, O. Manninen; stp. *, ** Ph. pini (Brot. : Fr.) A. Ames – Ruokolainen 2013 a, c; south of the village of Lambasruchei, old-growth pine forest, on old pine, 24.08.2012, 22.08.2013, 27.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 134, 152–154, 174–178, 180–184, 186, 16–19.08.2013, O. Manninen; p. ** Ph. populicola Niemelä – Ruokolainen 2013 a, c; south of the village of Lambasruchei, Lake Onega shore, Lipovitsy, Tipinitsy, mixed forest on dead of aspen, 24.08.2012, 23–25.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 133–134, 153–154, 174–175, 177, 180, 182–183, 17–19.08.2013, O. Manninen; stp. Ph. punctatus (P. Karst.) Pilát – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., on deadwood of Salix caprea, 16.07.1998, V.I. Krutov, PTZ; Zharnikovo, Polya, on Alnus incana and Sorbus aucuparia, 01.08.2012, 24.08.2013, A.V. Ruokolainen; p. Ph. tremulae (Bondartsev) Bondartsev et P.N. Borisov – Bondartseva et al. 1999, Ruokolainen 2013 a, b, c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest on dead aspen, 09.07.1997, A.V. Ruokolainen, PTZ; Polya, Zharnikovo, spruce-dominated forest on dead aspen, A.V. Ruokolainen, fq. *, ** Ph. viticola (Schwein. ex Fr.) Donk – Ruokolainen 2013 a, c; Syar peninsula, on deadwood of conifers, comp. 153–154, 176–178, 183, 17–18.08.2013, O. Manninen; environs of Velikaya Niva, spruce forest on dead spruce, 23.08.2012, A.V. Ruokolainen; Lipovitsy, Polya, north of Tambitsy, environs of Tolsty Navolok, Tambitsy, Tipinitsy, comp. 41, 71, 84 et al., A.V. Ruokolainen; stp. ** Phellodon niger (Fr. : Fr.) P. Karst. – Syar peninsula, on litter, 18.08.2013, O. Manninen; pine forest, comp. 13, on litter, 22.08.2013, A.V. Ruokolainen, PTZ; r. Ph. tomentosus (L.) Banker – Ruokolainen 2013 c; Syar peninsula, on litter, 19.08.2013, O. Manninen; Ladmozero, Vanchozero, pine forest, on litter, 24–25.08.2012, A.V. Ruokolainen; pine forest, comp. 13, on litter, 22.08.2013, A.V. Ruokolainen; stp. *, ** Phlebia centrifuga P. Karst. – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest on fallen pine, 07.07.1997, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 177–178, 180, 183, 186, on spruce, 19.08.2013, O. Manninen; Tambitsy, Myrtillus spruce forest, on fallen spruce, 28.08.2013, A.V. Ruokolainen, PTZ; stp. Threat status: Fin – NT. Ph. livida (Pers. : Fr.) Bres. – Ruokolainen 2013 c; north of Podyelniki, pine forest, on fallen pine, 10.08.2010, A.V. Ruokolainen, PTZ; r. Ph. radiata Fr. – Ruokolainen 2013 c; Zharnikovo, mixed forest, on fallen Salix, A.V. Ruokolainen; stp. Ph. rufa (Pers. : Fr.) M.P. Christ. – Ruokolainen 2013 c; Kizhi Isl., LE; Kizhi Isl., on deadwood of Sorbus aucuparia, 16.07.1998, V.I. Krutov, PTZ; stp. Ph. segregata (Bourdot et Galzin) Parmasto – north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest, on old fallen spruce, 26.08.2013, A.V. Ruokolainen, PTZ; r. * Ph. serialis (Fr. : Fr.) Donk – northwest of the Vatnavolok village, Syar peninsula, comp. 183, on deadwood of conifers 18.08.2013; 27.06.2013, 23.08.2013, O. Manninen; r. Phlebiella sulphurea (Pers.) Ginns et M.N.L. Lefebvre – Ruokolainen 2013 c ; spruce, pine and mixed forest on deadwood of coniferous and deciduous trees; p. Phlebiopsis gigantea (Fr.) Jülich – Ruokolainen 2013 c; north of Podyelniki, south of Uzkaya Salma, Tambitsy, spruce forest on dead of spruce, 10.08.2010, 13.08.2010, 28.08.2013, A.V. Ruokolainen; stp. Physisporinus vitreus (Pers. : Fr.) P. Karst. – Lipovitsy, comp. 41–42, spruce forest, on deadwood of coniferous and deciduous trees, 23.08.2013, 24.08.2013, O. Manninen; r. Threat status: Len – 3. Piloderma bicolor (Peck) Jülich – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on deadwood of coniferous and deciduous trees, A.V. Ruokolainen; p. 252 Reports of the Finnish Environment Institute 40 | 2014 ** Piloporia sajanensis (Parmasto) Niemelä – Documentation ... 2013; Uzkaya Salma village, comp. 26, moist spruce forest, on fallen spruce on fruitbody of Trichaptum laricinum, 28.06.2013, O. Manninen, A.V. Kravchenko, PTZ; rr. Threat status: Kar – 3 (VU), Fin – EN. Piptoporus betulinus (Bull. : Fr.) P. Karst. – Ruokolainen 2013 b, c; Bol. Klim. Isl., environs of Lipovitsy, Podyelniki, Polya, Tambitsy, Tipinitsy, Uzkaya Salma, Velikaya Guba, Zharnikovo, pine, spruce and mixed forest,on dead birch, A.V. Ruokolainen; fq. Plicatura nivea (Sommerf. : Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 c; southern part on Bol. Klim. Isl., spruce forest, on fallen Alnus incana, LE; stp. ** Polyporus badius (Pers.) Schwein. – Ruokolainen 2013 c; Bolshoi Lelikovskiy Isl., mixed forest, on fallen aspen, 09.08.2010, A.V. Markovsky, O. Turunen, PTZ; Zharnikovo, mixed forest, on fallen aspen, 05.08.2012, A.V. Ruokolainen, PTZ; Tipinitsy, spruce forest on fallen aspen, 27.08.2013, A.V. Ruokolainen, PTZ; stp. Threat status: Fin – VU. P. leptocephalus (Jacq.) Fr. [= P. varius (Pers.) Fr.] – Bondartseva et al. 1999; Ruokolainen 2013 c; Bolshoi Lelikovskiy Isl., mixed forest, on fallen aspen, 09.08.2010, A.V. Ruokolainen; Zharnikovo, mixed forest, on fallen aspen, 05.08.2012, A.V. Ruokolainen; p. P. melanopus (Pers.) Fr. – Ruokolainen 2013 c; Podyelniki, Zubovo, mixed forest, on old deadwood of birch, 03.08.2012, A.V. Ruokolainen, PTZ; stp. ** P. pseudobetulinus (Pilát) Thorn. Kotir. et Niemelä – Documentation ... 2013; on old aspen, rr. Threat status: Kar – 2 (EN), Fin – VU. P. squamosus (Huds.) Fr. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi and Bolshoi Lelikovskiy Isl.s, north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest mixed forest, on deadwood of Salix caprea and aspen, 09.08.2010, 04.08.2012, 26.08.2013, A.V. Ruokolainen; stp. Postia alni Niemelä et Vampola – Ruokolainen 2013 b, c; Zharnikovo, Lipovitsy, comp. 41, spruce and mixed forest, on deadwood of Salix caprea, Sorbus aucuparia and alder, A.V. Ruokolainen; stp. P. caesia (Schrad. : Fr.) P. Karst. – Bondartseva et al. 2000; Ruokolainen 2013 c; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest on deadwood of spruce, 26.08.2013, A.V. Ruokolainen; stp. P. fragilis (Fr.) Jülich – Ruokolainen 2013 c; spruce forest on fallen pine, 05.08.2011, A.V. Ruokolainen, PTZ; Zharnikovo, pine forest, on dead pine, 02.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 186, 19.08.2013, O. Manninen; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest on fallen pine and spruce, 26.08.2013, A.V. Ruokolainen; Tambitsy, motley grass spruce forest, on fallen spruce, 28.08.2013, A.V. Ruokolainen; p. *, ** P. guttulata (Peck) Jülich – Ruokolainen 2013 b, c; south of the village of Uzkaya Salma, spruce forest, on dead spruce, 13.08.2010, A.V. Ruokolainen; Podyelniki, mixed fores,t on the roots of dry spruce, 03.08.2012, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 181, 186, on deadwood of spruce, 19.08.2013, O. Manninen; stp. Threat status: Fin – NT. *, ** P. lateritia Rennvall – Ruokolainen 2013 a; Syar peninsula, comp. 175, 180, 183, 186, on deadwood of conifers, 17–19.08.2013; 22.08.2013, O. Manninen; stp. Threat status: Fin – NT. ** P. leucomallella (Murrill) Jülich – Zharnikovo, pine forest,on dead pine, 02.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 174, 182, 186, on dead of pine, 17–19.08.2013; 28.08.2013, O. Manninen; stp. Threat status: Len – 3. P. sericeomollis (Romell) Jülich – Syar peninsula, comp. 152, 183, spruce forest, on deadwood of conifers, 16.08.2013, 18.08.2013; 25.06.2013, 27.06.2013, 22.08.2013, O. Manninen; stp. P. stiptica (Pers. : Fr.) Jülich – Ruokolainen 2013 c; Lake Korbozero, Tipinitsy, mixed forest on deadwood of spruce, 27.08.2013, A.V. Ruokolainen; Tambitsy, motley grass spruce forest on deadwood of spruce, 28.08.2013, A.V. Ruokolainen; stp. Reports of the Finnish Environment Institute 40 | 2014 253 P. tephroleuca (Fr.) Jülich – Ruokolainen 2013 c; Bolshoi Lelikovskiy Isl., mixed forest on fallen aspen, 09.08.2010, A.V. Ruokolainen, PTZ; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest, on fallen birch and spruce, 26.08.2013, A.V. Ruokolainen; stp. ** P. undosa (Peck) Jülich [= Spongiporus undosus (Peck) A. David] – north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest on fallen pine and spruce, 26.08.2013, A.V. Ruokolainen, PTZ; r. Threat status: Len – 3. Pseudochaete tabacina (Sowerby) T. Wagner et M. Fisch. [= Hymenochaete tabacina (Sowerby) Lév.] – Ruokolainen 2013 c; Kizhi Isl., mixed forest on fallen aspen, 04.08.2012, A.V. Ruokolainen; Zharnikovo, mixed forest on fallen Sorbus aucuparia, 01.08.2012, A.V. Ruokolainen; stp. Pseudohydnum gelatinosum (Scop. : Fr.) P. Karst. – spruce forest, on fallen spruce, 27.08.2013, O. Manninen; r. * Pseudomerulius aureus (Fr.) Jülich – Syar peninsula, comp. 133, 180, 183, 16.08.2013, 18–19.08.2013, O. Manninen; r. ** Pycnoporellus alboluteus (Ellis et Everh.) Kotl. et Pouzar – south from Velikaya Guba village, at the western part of peninsula, comp. 9 of Kizhi forestry unit in old-growth spruce forests on fallen 24.08.2013, O. Manninen, T. Kuuluvainen; rr. Threat status: Fin – EN. *, ** P. fulgens (Fr.) Donk – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; Bol. Klim. Isl., spruce forest, on fallen spruce, 07.07.1997, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 153–154, 174, 176, 178, 180, 185–186, 17–19.08.2013, O. Manninen; Lipovitsy, north of Tambitsy, environs of Tolsty Navolok, Tambitsy, Kaskoselga, Lake Korbozero, Tipinitsy, comp. 41, 71, 132, 177 et al., spruce forest on old deadwood spruce, 21–23.08.2013, 26–28.08.2013, A.V. Ruokolainen; p. Threat status: Len – 3. Pycnoporus cinnabarinus (Jacq.) P. Karst. – Ruokolainen 2013 c; Zharnikovo, mixed forest, on deadwood of birch, 01.08.2012, A.V. Ruokolainen; stp. Radulodon erikssonii Ryvarden – Ruokolainen 2013 c; spruce forest on old deadwood aspen; rr. Threat status: Kar – 3 (VU), Fin – VU. ** Ramaria aurea (Schaeff.) Quél. – Ruokolainen 2013 c; pine forest, 22.08.2013; rr. ** R. eumorpha (P. Karst.) Corner [= R. invalii (Cotton et Wakef.] – Bondartseva et al. 1999; Kizhi Isl., LE; Podyelniki, spruce forest on litter, 03.08.2012, A.V. Ruokolainen, PTZ; r. R. suecica (Fr. : Fr.) Donk – Kizhi Isl., on litter, 04.08.2012, A.V. Ruokolainen, PTZ; r. Resinicium bicolor (Alb. et Schwein.) Parmasto – Ruokolainen 2013 c; Podyelniki, Zharnikovo, spruce and pine forest on fallen spruce; stp. R. furfuraceum (Bres.) Parmasto – Bondartseva et al. 1999; Bol. Klim. Isl., LE; Bol. Klim. Isl., spruce forest, on fallen spruce, 04.07.1997, A.V. Ruokolainen, PTZ; stp. *, ** Rhodonia placenta (Fr.) Niemelä, K.H. Larss. et Schigel – Ruokolainen 2013 a, c; south of the village of Uzkaya Salma, moist spruce forest, on fallen spruce, 13.08.2010, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 178, 180, 183, 186, 18–19.08.2013, O. Manninen; Lipovitsy, comp. 41, spruce forest on deadwood of spruce, 23.08.2013, A.V. Ruokolainen; stp. ** Rigidoporus crocatus (Pat.) Ryvarden – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 03.07.1997, A.V. Ruokolainen, PTZ; Bol. Klim. Isl., spruce forest on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; Zharnikovo, birch forest on deadwood of deciduous trees, 05.08.2012, A.V. Ruokolainen, PTZ; Tambitsy, motley grass spruce forest, on fallen birch, 28.08.2013, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 180–181, 19.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Len – 3, Fin – EN. Sarcodon fennicus (P. Karst.) P. Karst. – Ruokolainen 2013 c; south of the village of Lambasruchei, Lake Onega shore, pine forest, on litter, 24.08.2012, A.V. Ruokolainen; by the lake in pine forest, comp. 13, on litter, 22.08.2013, A.V. Ruokolainen; r. 254 Reports of the Finnish Environment Institute 40 | 2014 S. glaucopus Maas Geest. et Nannf. – Syar peninsula, comp. 177, 180, 182, 185–186, pine forest on litter, 18–19.08.2013; 27.08.2013, O. Manninen; r. S. imbricatus (L. : Fr.) P. Karst. – north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest on litter, 26.08.2013, A.V. Ruokolainen; r. Schizopora paradoxa (Schrad. : Fr.) Donk – Ruokolainen 2013 c; on deadwood of aspen and birch; r. Scytinostroma galactinum (Fr.) Donk – Ruokolainen 2013 c; Zharnikovo, pine forest, on fallen birch, 02.08.2012, A.V. Ruokolainen, PTZ; r. Threat status: Fin – NT. S. odoratum (Fr.) Donk – Tambitsy, Myrtillus spruce forest, on fallen spruce, 28.08.2013, A.V. Ruokolainen, PTZ; r. ** Serpula himantioides (Fr. : Fr.) P. Karst. – 27.06.2013, O. Manninen; r. *, **, Sidera lenis (P. Karst.) Miettinen [= Skeletocutis lenis (P. Karst.) Niemelä] – Documentation ... 2013; Syar peninsula, comp. 153, 176–177, on fallen pine, 17–18.08.2013, O. Manninen; 22.08.2013 and 25.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Len – 3, Fin – NT. Sistotrema raduloides (P. Karst.) Donk – Velikaya Niva, mixed forest, on fallen aspen, 23.08.2012, A.V. Ruokolainen, PTZ; r. Skeletocutis amorpha (Fr.) Kotl. et Pouzar – Ruokolainen 2013 b, c; Kizhi Isl., on pine wood, 04.08.2012, A.V. Ruokolainen; r. Sk. biguttulata (Romell) Niemelä – Ruokolainen 2013 c; north of Podyelniki, pine forest, on fallen pine, 11.08.2010, A.V. Ruokolainen, PTZ; r. Sk. brevispora Niemelä – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on fallen spruce, 10.08.2010, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 153, 17.08.2013, O. Manninen; r. Threat status: Fin – NT. Sk. chrysella Niemelä – spruce forest, on fallen spruce, 23.08.2013, O. Manninen; rr. Threat status: Fin – NT. *, ** Sk. odora (Sacc.) Ginns – Ruokolainen 2013 a, c; south of the village of Uzkaya Salma, moist spruce forest, on fallen spruce, 13.08.2010, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 180–183, 18–19.08.2013, O. Manninen; r. Threat status: Fin – NT. Sk. papyracea A. David – Ruokolainen 2013 c; Zharnikovo, pine forest, on fallen pine, 02.08.2012, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 177, 182, 18.08.2013; 25.06.2013, 24.08.2013, O. Manninen; r. *, ** Sk. stellae (Pilát) J. Keller – Syar peninsula, comp. 182–183, 18.08.2013; 27.06.2013, 23.08.2013, 26.08.2013, O. Manninen; r. Threat status: Fin – VU. Steccherinum imbriatum (Pers. : Fr.) J. Erikss. – Ruokolainen 2013 c; Tambitsy, spruce forest, on fallen aspen, 28.08.2013, A.V. Ruokolainen; stp. St. ochraceum (Pers.) Gray – Bondartseva et al. 1999; Bol. Klim. Isl., LE; Bol. Klim. Isl., on fallen deadwood of deciduous trees, 06.07.1997, A.V. Ruokolainen, PTZ; stp. Stereum hirsutum (Willd.) Pers. – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen birch, 06.07.1997, A.V. Ruokolainen, PTZ; Kizhi Isl., on deadwood of Sorbus aucuparia and alder, 16.07.1998, V.I. Krutov, PTZ; p. S. rugosum Pers. – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., on deadwood of alder, 16.07.1998, V.I. Krutov, PTZ; p. S. sanguinolentum (Alb. et Schwein.) Fr. – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., on fallen spruce, 06.07.1997, A.V. Ruokolainen, PTZ; stp. S. subtomentosum Pouzar – Bondartseva et al. 1999; Bol. Klim. Isl., LE; Bol. Klim. Isl., on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; stp. Thelephora terrestris Ehrh. – Ruokolainen 2013 c; Lipovitsy, comp. 41, spruce forest, on litter, A.V. Ruokolainen; stp. Reports of the Finnish Environment Institute 40 | 2014 255 Tomentella bryophila (Peck) M.J. Larsen – Lipovitsy, spruce forest, on fallen aspen, 21.08.2013, A.V. Ruokolainen, PTZ; stp. ** T. crinalis (Fr.) M.J. Larsen – Ruokolainen 2013 a, c; south of Uzkaya Salma, spruce forest with aspen, on old fallen aspen, 13.08.2010, A.V. Ruokolainen, PTZ; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest, on old fallen aspen, 26.08.2013, A.V. Ruokolainen, PTZ; Lake Korbozero, Tipinitsy, mixed forest, on old fallen aspen, 27.08.2013, A.V. Ruokolainen, PTZ; Threat status: Kar – 3 (NT); r. T. lateritia Pat. – Ruokolainen 2013 a, c; mixed forest, on fallen aspen; stp. T. stuposa (Link) Stalpers – Ruokolainen 2013 c; Velikaya Niva, motley grass birch forest, 23.08.2012, A.V. Ruokolainen, PTZ; r. T. sublilacina (Ellis et Holw.) Wakef. – Ruokolainen 2013 c; Zharnikovo, mixed forest on deadwood of deciduous trees, 02.08.2012, A.V. Ruokolainen, PTZ; r. T. terrestris (Berk. et Broome) M.J. Larsen – Ruokolainen 2013 c; north of Podyelniki, spruce forest, near fallen aspen, 11.08.2010, A.V. Ruokolainen, PTZ; r. Trametes hirsuta (Wulfen) Lloyd – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., on deadwood of Sorbus aucuparia, 07.08.1998, V.I. Krutov, PTZ; Bol. Klim. Isl., Zharnikovo, mixed forest, on fallen Sorbus aucuparia and birch, 01.08.2012, A.V. Ruokolainen; p. T. ochracea (Pers.) Gilb. et Ryvarden – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; Bol. Klim. Isl., spruce forest, on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; Zharnikovo, mixed forest on fallen aspen and birch, 01.08.2012, A.V. Ruokolainen; fq. T. pubescens (Schumach.) Pilát – Ruokolainen 2013 c; Zharnikovo, mixed forest, on fallen birch and alder, 01.08.2012, A.V. Ruokolainen; p. ** T. suaveolens (L. : Fr.) Fr. – the river Padma, on deadwood of Salix caprea, 04.09.2005, A.V. Ruokolainen, PTZ; 26.06.2013, 27.08.2013, 28.08.2013, O. Manninen; r. Threat status: Len – 3, Fin – NT. T. trogii Berk – Syar peninsula, comp. 153, 17.08.2013; 27-28.08.2013, O. Manninen; r. Threat status: Fin – VU. Trecispora hymenocystis (Berk. et Broome) K.H. Larss. – 27.08.2013, O. Manninen; r. T. mollusca (Pers. : Fr.) Liberta – 25.08.2013 and 27.08.2013, O. Manninen; r. Trichaptum abietinum (Dicks.) Ryvarden – Bondartseva et al. 1999; in the southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 05.07.1997, A.V. Ruokolainen, PTZ; fq. T. fuscoviolaceum (Ehrenb.) Ryvarden – Ruokolainen 2013 c; the river Padma, on fallen pine, 04.09.2005, A.V. Ruokolainen, PTZ; stp. T. laricinum (P. Karst.) Ryvarden – Ruokolainen 2013 c; Syar peninsula, comp. 181, 19.08.2013, O. Manninen; rr. Threat status: Fin – NT. T. pargamenum (Fr.) G. Cunn. – Bondartseva et al. 1999; Syar peninsula, comp. 186, 19.08.2013; Polya, mixed, pine and spruce forest, on fallen birch, 22.08.2013, 24.08.2013, A.V. Ruokolainen; 27.08.2013, O. Manninen; stp. Threat status: Fin – NT. Tubulicrinis calothrix (Pat.) Donk – Bondartseva et al. 1999; Bol. Klim. Isl., LE; Bol. Klim. Isl., spruce forest on fallen pine, 06.07.1997, A.V. Ruokolainen, PTZ; pine forest, comp. 13, on fallen pine, 22.08.2013, A.V. Ruokolainen, PTZ; stp. T. effugiens (Bourdot et Galzin) Liberta – Bondartseva et al. 1999; Bol. Klim. Isl., LE; r. Veluticeps abietina (Pers. : Fr.) Hjortstam et Tellería – Ruokolainen 2013 a, c; near Lake Nizhnee Pigmosero, 22.08.2012; Polya, spruce forest, on dead spruce, 25.08.2012, A.V. Ruokolainen; stp. 256 Reports of the Finnish Environment Institute 40 | 2014 3.6 Insect fauna of Zaonezhye Peninsula and adjacent islands Jevgeni Jakovlev*#, Alexei Polevoi** and Andrei Humala** * The Finnish Environment Institute (SYKE) Mechelininkatu 34a. P.O. Box 140, FIN-00251 Helsinki, Finland ** Forest Research Institute of Karelian Research Center of Russian Academy of Sciences 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia # - Corresponding author E-mail: jevgeni.jakovlev@ymparisto.i Introduction Zaonezhye Peninsula is situated on the northwestern coast of Lake Onega, in the eastern part of the biogeographical province of Karelia onegensis. In the east its shores are washed by Zaonezhye Gulf, while in the west the peninsula is bordered by Lizhma Bay and Bolshoye Onego Gulf of Lake Onega. Zaonezhye Peninsula lies on the basement rocks of Fennoscandia and characterized by underlying basic limestone and carbonate rocks. This, together with highly fertile soils, has contributed to the diversity of habitats and plant species on Zaonezhye Peninsula. For this reason, it is considered a separate vegetation region (Ramenskaya 1983). The same is true of the insect fauna, which has interested entomologists for a long time. History of entomological studies on Zaonezhye Peninsula Entomological studies on Zaonezhye Peninsula began in the second half of the 19 th century. At that time it was one of the most developed agricultural areas in Karelia with good connection to Petrozavodsk by water transport. The earliest records from this area date back to 1859–1899 when the apothecary of Alexandrovsky plant (Petrozavodsk), Alexander Günther, collected insects mainly around Petrozavodsk, covering eastern parts of the provinces Kon and Kol (Pekkarinen & Huldén 1995). The collections of Alexander Günther are not available in Russia. However, he maintained contact with Finnish entomologists and published species lists of Lepidoptera (Günther 1868, 1896 a) and Coleoptera (Günther 1896 b). A large part of his collections have been identiied by Finnish entomologists and subsequently published, e.g. Kaisila (1947) for Lepidoptera, and Poppius (1899) for Coleoptera. Most of the samples are stored in the Zoological Museum of Helsinki. Reports of the Finnish Environment Institute 40 | 2014 257 The irst detailed study of beetles (Coleoptera) around Lake Onega was conducted by the famous Finnish entomologist Bertil Robert Poppius (Poppius 1899). Between June and August 1896, he visited several places on the shores of the lake, including Zaonezhye Peninsula inland areas (locations Dianova Gora, Kosmozero, Unitsa), villages on its eastern and southern shores, Kuzaranda, Shun’ga (Schungu in Poppius’ transcription), Tolvyua (Tolvoja), Velikaya Guba (Velikaja-guba), and the Kizhi archipelago, islands Bolshoi Klimenetsky, Kizhi (Kischi), and Southern Oleny (Yu. Oleny in the species list). Several species are recorded as ‘Saoneshje-halfön’ without indication of certan locality As a result, more than 400 of presently recognized beetle species were reported for the irst time from Zaonezhye area. The next records of insect from Zaonezhye Peninsula were by Finnish entomologists during the Second World War (Kaisila 1947, Valle 1952, Kontuniemi 1965, etc.). After the war, the insect fauna of the area was not studied until the middle of the 1990s when entomologists from the Forest research institute of the Karelian Research Center of the Russian Academy of Sciences started inventories of the Kizhi archipelago, including the islands of Kizhi, Bolshoi Klimenetsky, Volkostrov and Yuzhnyi Oleniy (Jakovlev et al. 1999). Later, faunistic studies have been continued in the same areas as well as on the southern end of the peninsula, adjacent to the Kizhi archipelago, (e.g. Podyelniki and Oyatevschina). Additional materials of Lepidoptera have been collected by Dr. Vyacheslav Gorbach (Petrozavodsk State University) and Finnish entomologists around the village of Sennaya Guba (Gorbach & Saarinen 2002; Gorbach & Kabanen 2010). All these areas are a part of the Kizhi nature reserve (zakaznik). As a result, nearly 2 000 insect species have been recorded from the entire Kizhi archipelago (Humala & Polevoi 2012). Areas north of the Kizhi Nature Reserve remained unstudied from the time of Poppius until 2012 when approximately 1 000 insect species were recorded in the northern part of the peninsula, including the villages of Kosmozero, Myagrozero, Shun’ga and Turastamozero (Polevoi & Humala 2013). These areas are proposed to be included in the planned Zaonezhye landscape reserve (zakaznik). The latest samples were collected outside of the planned landscape reserve in 2013 during the joint Finnish-Russian expedition to the southern lowlands of Zaonezhye Peninsula (Kizhi forestry unit, or lesnichestvo, and a part of the Velikaya Niva forestry unit, compartments (quartals) 46-47, 69-71, 79-83, 97-100, 102-104, 114-117, 123-124,140143, 158-162). Also, Karelian entomologists collected samples during a short visit to the coastal areas of Zaonezhye Peninsula and adjacent islands in 2004, and northern part of the Kizhi Nature Reserve in 2014 (Eglov Island and its vicinities). Study area and methods Materials were collected between 1994 and 2013 in the Medvezhiegorsk and Kondopoga municipalities of the Republic of Karelia, within the biogeographical province of Karelia onegensis. Our samples originated from approximately 74 sites (Fig. 1), which have been grouped into 40 generalised locations in the species list. 258 Reports of the Finnish Environment Institute 40 | 2014 Fig. 1. Study sites in Zaonezhye Peninsula: 1–Vikshezero, 2–Unitsa, 3–Dianova Gora, 4–Nikonova Guba, 5–Shun’ga, 6–Paleostrov Isl., 7–Isl. Kainos and Vavlok, 8–Turastamozero, 9–Kazhma, 10– Verkhnee and Nizhnee Myagrozero, 11–Tolvuya, 12–Lizhma, 13–Kosmozero, 14–Velikaya Niva, 15–Kuzaranda, 16–Tambitsy, 17–Polya, 18–Velikaya Guba, 19–Vegoruksy, 20–Tipinitsy, 21–Uzkaya Salma, 22–Lipovitsy, 23–Khvost Isl., 24–Isl. Eglov and Rogachev, 25–Isl. Shunevskiy, 26–Volkostrov Isl., 27–Pod’elniki, 28–Kizhi Isl., 29–Kurgenitsy, 30–Yuzhnyi Olen Isl., 31–Vorobyi, 32–Oyatevschina, 33–Kopanets Lake, 34–Vertilovo, 35–Myal’ Isl. and Lelikovo, 36–Sennaya Guba, 37–Voinavolok, 38–Isl. Ernitskiy, Lyudskoy and Kuivakhda, 39–Bolshoy Lelikovskiy Isl., 40–Klimenitsy. We used a variety of collecting methods in order to capture different insect groups: sweep netting, portable Malaise traps (Jaschoff & Didham 2002) (Fig 2), yellow pan traps (Masner 1976), polypore traps (Kaila 1993) as well as light trapping with an ultraviolet lamp and a white sheet. In addition, we collected insects on dead wood, fungi and lowers (Fig. 3). In 2013, three Malaise traps were placed in the Kizhi forestry unit (surroundings of the villages Uzkaya Salma and Lipovitsy) and Velikaya Niva forestry unit (near the village Polya) for the period between 26th June and 25th August. Easily distinguishable species were identiied by appearance, or photographed. We concentrated on three large insect orders: Coleoptera, Hymenoptera and Diptera. In the order Lepidoptera we recorded mostly representatives of the suborder Rhopalocera. Some insect groups were excluded due to problems in identiication. Other groups have limited samples due to selective methods used. Original materials are stored at the Forest research institute of Karelian Research Center of the Russian Academy of Sciences (Petrozavodsk), and in Finnish Environment Institute (Helsinki). There are also old insect collections from Zaonezhye area which are now stored in the Zoological Museum of the University of Helsinki (Finland). We could not manage checking of all these materials, but listed only published records. Reports of the Finnish Environment Institute 40 | 2014 259 Fig. 2. Malaise trap in spruce-dominated unmanaged forest with great proportion of aspen. NE of the abandoned Lipovitsy village (Photo Jevgeni Jakovlev). Fig. 3. Handpicking from thin dead branches of windfallen aspen trees of a dark black color – typical larval microhabitat of a rare beetle species, Leiopus punctulatus (Photo Andrei Humala). Results In total, approximately 2453 insect species were recorded from Zaonezhye Peninsula and adjacent archipelagos. Of these: Ephemeroptera–1, Odonata– 27, Orthoptera–14, Blattoptera–2, Mecoptera–2, Raphidioptera–1, Neuroptera–3, Hemiptera–61, Coleoptera–583, Lepidoptera–218, Hymenoptera– 428, and Diptera–1113 species. The characteristics of insect fauna are determined not only by the diversity of natural habitats, but also by the history of landuse on Zaonezhye Peninsula. In addition 260 Reports of the Finnish Environment Institute 40 | 2014 to species typical of old-growth forests, there are species associated with secondary forests with a large amount of dead wood of deciduous trees, as well as meadow insect fauna. Originally the area was covered with high quality coniferous forests, growing in conditions close to optimal. At present, intact coniferous forests are preserved only in paludiied areas and on steep, rocky slopes. The rest of the forests have been affected by selective cuttings. Especially close to the villages, forests have grown naturally on abandoned ields and hay meadows. According to forest inventory data from 1999 (Gromtsev & Krutov 2000), pine- and spruce-dominated forests occupy nearly 60 percent of the forest cover in approximately equal proportions. The remaining area is covered by forests dominated by birch (ca. 30%), aspen (5%) or grey alder (6 %). The studied forests in the lowland parts of Zaonezhye Peninsula can be divided roughly into three classes. These are (1) high quality primeval forests with negligible human impact, (2) forest of high conservation potential, rapidly restoring natural values after earlier human use, and (3) successional forests, which are developing after the abandonment of ields and forest pastures (see Kuuluvainen and Tikkanen, Reports of the Finnish Environment Institute 40 | 2014). Human impact on the study area has always been signiicant. During our sampling trips in 2012 (northern parts of Zaonezhye Peninsula) and 2013 (southern parts), we found only a few sites of high quality spruce dominated forests and mire-spruce stands that could be characterized as near primeval forest. At least, two threatened beetle species, Pytho kolwensis and Monochamus urussovi seem to be fairly well-preserved here. Forests of the second class which has been used to some extent in the past for selective cutting, slash-and-burn cultivation, etc., and then developed naturally during dozens of years occupy large areas in Zaonezhye Peninsula and in some islands, e.g. Bolshoy Klimenetsky. Although of secondary origin, these forests are rich in coarse woody debris and, therefore, host a series of saproxylic beetle (Coleoptera) species that are typical for intact boreal forests, e.g. Ceruchus chrysomelinus (Lucanidae), Phaenops cyanea, Chrysobothris chrysostigma (Buprestidae), Phryganophilus ruicollis (Melandryidae), Nivellia sanguinosa, Pedostrangalia pubescens and Leptura nigripes (Cerambycidae) as well as their parasitoids, e.g. ichneumonoid wasps Arotes albicinctus and Coleocentrus exareolatus (Hymenoptera). Many of these species have declined dramatically in Western Europe, many are redlisted. Pine-dominated stands usually contain old trees bearing signs of resin extraction which was carried out some tens years ago, however, neither signs of insect epidemics, nor symptoms of forest decline due to insect pests have been observed. The third class of forests - mixed deciduous stands with alder, birch and aspen occupy abandoned ields, slash-and-burn sites and pastures near former villages. In many sites, there is plenty of dead wood of aspen where we found several internationally rare insect species, including lies Symmerus nobilis and Xylomya czekanovskii (Diptera), beetles Hylochares cruentatus, Rhizophagus pincticollis, and Leiopus punctulatus (Coleoptera). In Finland these species are highly threatened, ranging from vulnerable (VU) to regionally extinct (RE). In Karelia they have been recorded only in southern part from limited areas like Kivach Nature Reserve (Ivanter & Kuznetsov 2007). In Zaonezhye they seem to be well-preserved in secondary forests on fertile soils. Grasslands are located mainly in the southern and eastern lowlands where they have been intensively used as hay meadows and pastures. Relatively large areas have been covered with arable land. At present, most of these areas are abandoned, gradually transforming into young secondary deciduous forest. We found and observed only a few intact grasslands on the islands of the Kizhi archipelago and in the eastern shore of Zaonezhye Peninsula. Wet grasslands can be found in the narrow bays along Reports of the Finnish Environment Institute 40 | 2014 261 the shoreline. Formerly, local population used these grasslands for haymaking, whereas presently they are occupied with a combination of mire and meadow vegetation (Kuznetsov 1993). Typical grassland species include Psophus stridulus (Orthoptera) and several species of butterlies, e.g. internationally rare Parnassius mnemosyne and Zygaena osterodensis, which are considered very rare and threatened both in Karelia and the entire Europe. Very interesting is a recent inding of a longhorn beetle species, Aromia moschata at the edge of abandoned ield on Bolshoy Klimenetsky Island. This species develops primarily in willows. Conclusions Zaonezhye Peninsula was one of the most highly developed rural regions in Karelia during the extended period. Long history of traditional agriculture and its general decline in the recent years led to formation of huge variety of habitats in the area including open meadows, secondary stands on abandoned ields and remnants of natural coniferous forests. Such variety together with a set of favorable abiotic conditions provide successful existence of various insect group: saproxylic species, requiring dead wood of certain tree species at different stages of decay; herbivores, trophically associated with certain plant species; aquatic species, which require special water conditions, etc. Many of such species nowadays become very rare or even extinct in other parts of Karelia as well as in whole Fennoscandia. Our indings undoubtedly indicate the uniqueness of Zaonezhye Peninsula territory and its signiicant value in terms of insects’ biodiversity conservation. It is a strong ecological argument to establish protected areas for conservation of the habitats of saproxylic insects and insects conined to intact grasslands which were revealed during the entomological studies. Zaonezhye Peninsula and adjacent islands is an exceptional area in Karelia for which there is a considerable amount of old records of insects made before vast-scale mechanical forest logging was started in Karelia. It allows tracing dynamics of distribution of the threatened insect species in forests and grasslands. The twenty-year studies in 1994-2014, showed that saproxylic insects associated with aspen are well preserved in many places. Also, several threatened Coleoptera species associated with spruce and birch have been rediscovered in suitable habitats. These are, for instance, Pytho kolwensis, Phryganophillys ruicollis, Ceruchus chrysomelinus which are strongly declined throughout Northern Europe. All these species have a special value for nature conservation. On the other hand, we have failed to rediscover many Coleoptera species associated with pine, e.g. a bark beetle Ips sexdentatus which was recorded from the area by Poppius (1899) more than hundred years ago. This species is possibly extinct in Southern Karelia, and can be found only in places of stored barked pine wood (Jakovlev et al. 2000). A buprestid species, Phaenops cyanea which also seems to be declined in southern part of Karelia has been found in the timber store. Among the insects dependent on traditional agriculture landcapes, several species were evidently strongly declined. For instance, we have not found a dung beetle Onthophagus nuchicornis recorded by Poppius (1899). At the same time, several threatened insect inhabiting dry meadows still exist, inspite of the declining of agriculture and overgrowth of their natural habitats. The most interesting inding is the rattle grasshopper, Psophus stridulus which was mentiond by old authors (Ozeretskovsky 1989) as a common species in Southern Karelia. At present, P. stridulus population in Kizhi archipelago seems to be the only one in Russian Karelia. To maintain it, the special measures aimed to restore dry meadows in Zaonezhye are in urgent need. In Finland, the rattle grasshopper is considered as rapidly-declining, endangered species inhabit primarily dry and sunny sandy areas and eskers, 262 Reports of the Finnish Environment Institute 40 | 2014 and gradually moving from its natural biotopes to manmade environments, like the embankments of railroad tracks and roadside verges (Intke & Piirainen 2014). There are ecological groups, e.g. aquatic insects, and many taxonomic groups of insects which were not studied in the area yet. Further research is needed for these groups, as well as for localities which are not covered for entomological research in Zaonezhye Peninsula and adjacent islands. Acknowledgements We thank Mrs. N.N. Kutenkova (Kivach Nature Reserve) for the help in identifying Lepidoptera species, Mr. Juho Paukkunen (Helsinki Zoological Museum, Finland) for the help with identifying of some aculeates (Hymenoptera) and results of his trip in 2010 to Kizhi Nature Reserve. The study was partly supported in 1994–2014 by the Russian Foundation for Basic Research (grant No 13-04-98821), the Presidium of the Russian Academy of Sciences (Prorgamm of Fundamental Research Living Nature: Modern State and Development Problems), Kizhi Nature Reserve (State Zakaznik Kizhsky), and the project Barents Protected Area Network (BPAN) leaded by the Finnish Environment Institute. Annotated list of the insect species included in Red Data Book of the Republic of Karelia (Ivanter & Kuznetsov 2007) and other noteworthy insect species The threat status is given according to the following sources: Karelia (Kar) – Ivanter & Kuznetsov (2007), Leningrad Region (Len) – Noskov (2002), Finland (Fin) – Rassi et al. (2010). Species reported for the irst time in Karelia are marked with asterisks. ODONATA Aeshnidae Aeshna viridis Eversmann, 1836 Material. 5 km N of Nikonova Guba, 1 ♂, under an electric power line, 22/8/2012 (A.Humala). There are old records of the species from northern Ladoga (Valle 1927; Tiensuu 1933). There are also unconirmed indings in the Kondopoga region (S.Uzenbaev, pers. comm.). Larvae of the species develop in thickets of Water soldiers (Stratiotes aloides L.). Due to habitat speciication, the species is scarse and under threat over much of its range (Dijkstra, Lewington, 2006). Threat status: Kar – 4 (DD); Len– 3 (VU). Libellulidae Libellula fulva Müller, 1764 Material. 5 km S of Turastamozero, 1♂, 1♀, on the shore of a small river, 21/7/2012 (A.Polevoi). This is the irst modern record of the species in Karelia. It was previously known only from northern Ladoga (Valle 1927; Tiensuu 1933). The species requires a speciic combination of water quality and habitat structure and is therefore only locally common in Europe (Dijkstra, Lewington 2006). Threat status: Kar – 4 (DD). ORTHOPTERA Acrididae Psophus stridulus (Linnaeus, 1758) (Fig. 4) Material. Bolshoi Klimenetsky Island, Vorob’i, numerous specimens, 18-22/8/2008 (Polevoi, Humala). Reports of the Finnish Environment Institute 40 | 2014 263 An outstanding representative of the order Orthoptera. In adults, the hind wings have a bright red colour, and the males emit a characteristic chatter during light. The species was irst recorded in Karelia, near Konchezero, at the end of the 18th century (Ozeretskovsky 1989). Previously the species seems to have been distributed throughout the southern part of Karelia up to the border of the middle taiga (Albrecht 1979). However, it had not been observed here for over 50 years, and was considered as regionally extinct (Ivanter & Kuznetsov 1995) until it has been rediscovered in Kizhi archipelago. The cause of decline is the overgrowth of its natural habitats. Threat status: Kar – 1(CR); Len – 3 (VU); Fin – VU. Fig. 4. Psophus stridulus (Photo Alexei Polevoi). COLEOPTERA Scarabaeidae Onthophagus nuchicornis (Linnaeus, 1758) The species was recorded from Kizhi Island by Poppius in 1896 (Poppius 1899). It has been formerly distributed in southern parts of Fennoscandia. At present, the species is probably extinct in Russian Karelia, as well as in Finland, where the most recent record are from the years 1946 and 1955, respectively (Muona et al. 1998). In Zaonezhye, well-developed traditional husbandry provided the optimal habitats for O. nuchicornis. However, environmental changes caused by decline of the agricultural ecosystems are suggested as a reason for the decline in the occurrence of this vulnerable species with dung-living larvae. Threat status: Kar – 0 (RE); Fin – RE. Lucanidae Ceruchus chrysomelinus (Hochenwarth, 1785) Material: larvae inside spruce logs: Bolshoi Klimenetsky Island, 18.07.2000 (Jakovlev), Polya, 25/8/2013 (Polevoi). This is typical inhabitant of old-growth forest with big amount of coarse woody debris. Larvae live in well-decayed wood with brown rot fungi. They can colonize different tree species. In Karelia, most records are from spruce. Considered as threatened in all countries on Northern Europe, the threat factor is reduction of the area of old-growth forests. In Karelia has been recorded only from southern part. Common 264 Reports of the Finnish Environment Institute 40 | 2014 in Kivach Nature Reserve (Jakovlev et al. 1986). Threat status: Kar – 3 (Vu); Fin –EN. The risk of extinction of this species is assigned also in the global level – category NT in the global Red List (IUCN 2014). Pythidae Pytho kolwensis Sahlberg, 1833 (Fig. 5) Material: larvae under bark of spruce logs: Bolshoi Klimenetsky Island, July 2000, Lipovitsy, 25/6/2013 (Jakovlev); Polya, 25/8/2013 (Humala), Tambitsy, 27/8/2013 (Polevoi). A species with a narrow ecological specialization. Larvae live under the bark of fallen, old spruce trees, usually in wet places. Sharply declined in Northern Europe due to forest management and drainage of spruce-mire moist forest. It is possible that P. kolwensis became extinct in large parts of southern Finland as early as the 1800s or even earlier, in regions where slash and burn cultivation was intensive at the time (Siitonen & Saaristo 2000). In Zaonezhye peninsula it survived in remains of old-growth forests. Generally, the species is widespread in Karelia, but recorded only in areas of old-grown forests with a lot of dead wood (Jakovlev et al. 2000). Threat status: Kar – 3 (NT); Len – 2 (EN); Fin – EN. Fig. 5. Larva of Pytho kolwensis (Photo Andrei Humala). Eucnemidae Hylochares populi Brüstle & Muona1 Material. Polya, 2 specimens under the bark of an old, dead aspen tree, 26/6/2013 (Humala); Tambitsy, cavities and holes on aspen trunks, 26/8/2013 (Polevoi). This species develops in large, dead aspens in old-growth forests. In Karelia, there are only two known populations in the Kondopoga and Pudozh municipalities (Ivanter & Kuznetsov 2007, Jakovlev 2009). There are also old records from the Olonets municipality (Palmén 1946). Threat status: Kar – 3(VU); Fin – EN. Buprestidae Chrysobothris chrysostigma (Linnaeus, 1758) (Fig. 3) Material. Nizhnee Myagrozero, 1 specimen on a spruce trunk near the road, 22/7/2012 (Polevoi); Vegoruksy, 1 specimen, 25/6/2013 (Kravchenko), 2 specimens on spruce 1 AММШrНТЧР ЭШ BrüsЭХО КЧН MЮШЧК (2009), КХХ KКrОХТКЧ sЩОМТЦОЧs ПШЮЧН ШЧ КsЩОЧs sСШЮХН ЛО МШЧsТНОrОН H.populi. H.cruentatus (GвХХОЧСКХ) НОЯОХШЩs ШЧ аТХХШаs КЧН ЭШ НКЭО Тs ШЧХв ФЧШаЧ ПrШЦ sШЮЭСОrЧ FТЧХКЧН. HШаОЯОr, sШЦО КЮЭСШrs qЮОsЭТШЧ ЭСО ЯКХТНТЭв sЭКЭЮs ШП H.populi (Kovalev 2014). Reports of the Finnish Environment Institute 40 | 2014 265 trunks near the road, 27/6/2013 (Polevoi, Humala); 7 km south of Kosmozero, 1 specimen on a dead spruce at the edge of a clear-cut, 26/6/2013 (Polevoi). This species develops under the bark of dying or dead conifers. In Karelia, the species is conined to old-growth forests. However, it is probably more widely distributed than previously thought. There are a few known old and modern records from southern Karelia (Palmén 1946; Humala & Polevoi 2009). Threat status: Kar – 3 (NT). Phaenops cyanea (Fabricius, 1775) (Fig. 6) Material. Vegoruksy, several specimens on pine trunks near the road, 27/6/2013 (Polevoi, Humala). This species develops inside and under the bark of dead or dying pines, especially of those damaged by ire. In the past it was a common species in southern Karelia (Palmén 1946). The latest records from the vicinities of Petrozavodsk date back to 1954 (Yakovlev et al. 1986). Threat status: Kar – 3 (VU). Nitidulidae Cyllodes ater (Herbst, 1792) Material. Bolshoi Klimenetsky Island 7/06/1995, 17/07/2000 (Jakovlev), Zharnikovo, 12/07/1999 (Polevoi), Lipovitsy 25/6/2013 (Humala), on the fruiting bodies of wood-growing fungi Fomes fomentarius, Piptoporus betulinus and Pleurotus pulmonarius. This species is relatively common in Karelia. It is associated with forests with great amount of dead aspens. Threat status: Kar – 3 (LC); Fin – NT. Monotomidae Rhizophagus puncticollis Sahlberg, 1837 Material. Mixed spruce dominated forest with great proportion of aspen, Kopanets Lake shore. 1 specimen (imago), under bark of dead aspen trunk, 15/07/1999 (Polevoi). This species has been drastically declining in Northern Europe due to eradication of aspen. In Karelia recorded only from southern part: Kivach Strict Nature Reserve, Kotkozero (Olonets municipality) and Gumbaritsa (SE shore of Ladoga Lake) (Siitonen et al. 1996). Threat status: Kar – 3 (NT); Fin – RE. Melandryidae Phryganophilus ruicollis (Fabricus, 1798) Material. Bolshoi Klimenetsky Island, 1 specimen have been collected by window trap, 5-10.06.1995 (Jakovlev). This species develops feeding on fungal mycelia in dead wood rotten by Fomes fomentarius and other white rot fungi. In Northern Europe, most records are from fungus infected trunks of spruce and birch, in Sweden − also from oak (Ehnsröm & Axelsson 2002), and it has been suggested to be favoured by forest ires (Lundberg 1993). Estimated as very rare species in all countries from where it has been recorded. There are only ca. 20 records from Northern Europe, of these three records from southern Karelia: Kivach Strict Nature Reserve, Kizhi Nature Reserve (Ivanter & Kuznetsov 2007) and vicinity of Matrossy village (Kolström & Leinonen 2000) In Karelia, Finland, Sweden and Norway, P.ruicollis has been assessed as threatened species based on a small area of occupancy and a small distribution area due to the reduction in the area of natural forests. Threat status: Kar 2(EN); FIN – VU. 266 Reports of the Finnish Environment Institute 40 | 2014 Fig. 6. Phaenops cyanea (Photo Andrei Humala). Cerambycidae Nivellia sanguinosa (Gyllenhal, 1827) Material. Vikshezero, 1 ♀, on lowers at the edge of an abandoned hayield, 28/6/2007 (Humala). This is a rare species developing in coarse woody debris (thin trunks, stumps and branches), most often – Alnus spp, also birch and some other deciduous trees like Prunus and Corylus (Ehnström & Axelsson 2002). It is known from only a few records in southern Karelia (Jakovlev et al., 1986; Polevoi et al. 2005). Threat status: Kar – 4 (DD); Fin – VU. Pedostrangalia pubescens (Fabricius, 1787) Material. Turastamozero, 1 ♀, on lowers, 24/7/2012 (Polevoi). The species develops in dead wood of pine (also on hardwoods in southern parts of its range). Its earlier records in Karelia are from northern Ladoga (Humala & Polevoi 2011). Threat status: Kar – 4 (DD); Fin – VU. Leptura nigripes DeGeer, 1775 (Fig. 7) Material. Turastamozero, 1 specimen, 20/7/2012 (Humala, Polevoi); Vegoruksy, 1 specimen, 27/6/2013 (Humala). On lowers at the edges of hayields. Larvae develop in dead wood of deciduous trees. The species is found in southern Karelia, although it is relatively rare across its range (Jakovlev et al. 1986). Threat status: Kar – 4 (DD); Fin – EN. Reports of the Finnish Environment Institute 40 | 2014 267 Fig. 7. Leptura nigripes (Photo Andrei Humala). Leiopus punctulatus (Paykull, 1800) Material. Polya, 1 specimen, on a branch of a fallen aspen, 25/8/2013 (Jakovlev). Larvae of this species feed subcortically in relatively thin dead branches of windfallen aspen trees of a dark black color caused by a fungus Encoelia fascicularis (Ascomycota). This species is probably extinct in Finland, and has been viewed as extinct since 1902 also in Sweden, but had been recently rediscovered (Lundberg & Martin 1991). To date only two locations were known in Karelia: Kivach Nature Reserve (Jaakko Mattila leg., 2002, unpubl.) and Pudozh municipality (Humala & Polevoi 2009). Threat status: Fin – RE. Phytoecia cylindrica (Linnaeus, 1758) Material. Vikshezero, 1 ♀, on lowers at the edge of an abandoned hayield, 28/6/2007 (Polevoi); Vegoruksy, 1 ♀, 25/6/2013 (Polevoi). The species develops in the stems of Apiaceae and Asteraceae. There are only a few, mostly old, records from Karelia (Silfverberg & Biström, 1981, Polevoi et al. 2005). Threat status: Kar – 4 (DD). Curculionidae Ips sexdentatus (Börner 1776), or six-toothed bark beetle. Recorded from Kosmozero by Poppius (Poppius 1899) as Tomicus stenographus Duffschmidt. This is the largest species of scolytids in boreal forest zone. Larvae develop under thick bark of recently fallen old pines. Generally, six-toothed bark beetle is known as forest pest which is able to attack healthy trees of Scotch pine under outbreak conditions. However, during last century it has become extremely rare in Northern Europe. In Russian Karelia it has been recorded only in fallen logs in places of long-time storage (Jakovlev et al. 2000). Threat status: Fin – VU. 268 Reports of the Finnish Environment Institute 40 | 2014 LEPIDOPTERA Papilionidae Parnassius mnemosyne (Linnaeus, 1758) (Fig. 8) Material. Velikaya Niva, numerous specimens along the road, 10/6/2000 (Humala, Polevoi). The distribution of Clouded Apollo is limited to southern Karelia (Bolotov et al. 2012). It has irst been reported from Zaonezhye (Velikaya Niva and Bolshoy Klimenetsky Island) in the middle of the 20th century (Kaisila 1947). Recently large but scattered populations have been found on the Kizhi skerries (Jakovlev et al. 1999; Gorbach & Kabanen 2010). However, its distribution on the mainland of Zaonezhye Peninsula needs to be clariied. The species is also recorded from southeastern parts of Karelia and Ladoga area (Humala 1998; Humala & Polevoi 2009; Gorbach & Reznichenko 2009). Threat status: Russia – 2; Kar – 3 (VU); Len – 2 (EN); Fin – VU. Fig. 8. Parnassius mnemosyne (Photo Andrei Humala). Lycaenidae Thecla betulae (Linnaeus, 1758) (Fig. 9) Material. 5 km N of Nikonova Guba, 1 ♀, along the road, 22/8/2012 (Humala). In Karelia the species is known only from old records (Gorbach & Reznichenko 2009). Threat status: Kar - 4 (DD). Reports of the Finnish Environment Institute 40 | 2014 269 Fig. 9. Thecla betulae (Photo Andrei Humala). Lasiocampidae Gastropacha quercifolia (Linnaeus, 1758) Material. Vegoruksy, 1 ♂, light trap, 26/6/2013 (Polevoi, Humala). A rare species; there are a few earlier records from the Kivach nature reserve (Kutenkova 2006). Arctiidae Rhyparia purpurata (Linnaeus, 1758) (Fig. 10) Material. Vegoruksy, 2 specimens, light trap, 26/6/2013 (Polevoi, Humala); Paleostrov Island, 1 specimen, 3/7/2004, (Polevoi); Kuzaranda, 2 specimens, 4/7/2004 (Humala); Eglov island, 1 specimen 29/6/2014 (Polevoi). The species inhabits meadows. The only other place in Fennoscandia where the species occurs is southern Finland (Hydén et al. 2006). Threat status: Fin – NT. Fig. 10. Rhyparia purpurata (Photo Alexei Polevoi). 270 Reports of the Finnish Environment Institute 40 | 2014 Zygaenidae Zygaena osterodensis (Linnaeus, 1758) (Fig. 11) Material. Podyelniki, numerous specimens, 20-25/7/2011 (Polevoi, Humala); Eglov and Rogachev islands, numerous specimens, 26-29/6/2014, (Polevoi, Humala). This species is very endangered in Finland. It is also quite rare in Karelia, although locally abundant in Zaonezhye. Threat status: Kar – 3(NT); Fin – RE. Fig. 11. Zygaena osterodensis (Photo Andrei Humala). HYMENOPTERA Argidae Aprosthema hyalinopterum Conde, 1934 Material. Bukol’nikov Island, 1 ♂, 25/6/2003 (Humala). The irst record from Karelia. Vespidae Discoelius dufourii Lepeletier, 1841 Material. Bolshoi Klimenetsky Isl., 2 km NE of Kurgenitsy, 1 ♀, 19/7/2000 (Humala). A rare species; there are only a few records from Karelia (Polevoi et al. 2005, Polevoi & Humala 2013, Kutenkova 2006). Threat status: Kar - 3(VU); Finland – VU. Pompilidae Dipogon vechti Day, 1979 Material. Nizhnee Myagrozero, meadow, 1 ♀, 20/7/2012 (Humala); Myagrozero, meadow, 1 ♀, 22/7/2012 (Humala). In Karelia, the species has only been recorded from samples from Velikaya Guba (Wolf 1967). Threat status: Fin – VU. Crabronidae *Ectemnius spinipes (A. Morawitz, 1866) Material. Turastamozero, meadow, 1 ♀, 20/7/2012 (Humala). This forest-dwelling digger wasp species has not been reported previously from Karelia. Even though the species occurs in many Central European countries, it is not known from Finland and Scandinavia, west of Zaonezhye (Lomholdt 1984). Reports of the Finnish Environment Institute 40 | 2014 271 Ichneumonidae **Apechtis capulifera (Kriechbaumer, 1887) Material. Turastamozero, 1 ♀, 24/7/2012, (Humala). This is the irst record of the species in Karelia. *Perithous albicinctus (Gravenhorst, 1829) Material. Turastamozero, meadow, 1 ♂, 21/7/2012, (Humala). This is the irst record of the species in Karelia. Zatypota albicoxa (Walker, 1874) Material. Tambitsy, 1 ♂, 26/8/2013 (Humala). In Karelia, cocoons of this parasitoid spider have only been found from the Lake Ladoga area. Threat status: Kar – 3 (LC). Rossemia longithorax Humala1997 Material. Polya, 1 ♀, Malaise trap, 26/6-25/8/2013 (Humala, Polevoi). The species is described from the Kivach nature reserve (Humala 1997 a). It has also been recorded from the Pudozh district (Humala & Polevoi 2009). Coleocentrus exareolatus Kriechbaumer, 1894 Material. 3 km NE of Lipovitsy, 1 ♀, Malaise trap, 25/6-21/8/2013 (Humala, Polevoi). The species is a parasite of larvae of longhorn beetles and horntails from the genus Urocerus, inhabiting coniferous tree trunks. In Karelia, it has previously been known only from the Kivach nature reserve (Humala 1997 b). Threat status: Fin – RE. Arotes albicinctus (Gravenhorst, 1829) Material. Verkhnee Myagrozero, 1 ♀, mixed forest, 27/7/2012 (Polevoi). This ichneumon wasp species is associated with longhorn beetles. This is second record of the species in Karelia. It was irst recorded by Walter Hellén in the surroundings of the Maselgskaya station in 1943. Threat status: Fin – EN; recommended to be included in the Red Data Book of Karelia as “requiring monitoring”. *Lycorina triangulifera Holmgren, 1859 Material. Radkolye Island, 1 ♂, meadow, 25/6/2003 (Humala). The species has not been found in Karelia before. Threat status: Fin – VU. *Tranosemella coxalis (Brischke,1880) Material. Bolshoi Klimenetsky Isl., 2 km NE of Kurgenitsy, 1 ♀, 19/7/2000 (Humala). This is the irst record of the species in Karelia. *Heteropelma amictum Fabricius, 1775 (=capitatum Desvignes, 1856) Material. Tipinitsy, 1 ♂, 27/8/2013 (Humala). This is the irst record of the species in Karelia. DIPTERA Limoniidae Limonia badia (Walker, 1848) Material. Tipinitsy, 5 ♂♂, 1 ♀, 27/8/2013 (Polevoi). This poorly known species has been described from North America and it has only recently been discovered in Fennoscandia (Starý & Salmela 2004). There are few records from Karelia to date (Polevoi & Salmela, 2014). The species is probably an old-growth forest specialist. It is understood that its larvae develop in dead aspens (Starý & Salmela, 2004; Halme et al. 2013). Threat status: Fin – NT. 272 Reports of the Finnish Environment Institute 40 | 2014 Ditomyiidae Symmerus nobilis Lackschewitz, 1937 Material. 7 km S of Kosmozero, 1 ♂, 26/6/2013 (Polevoi). Symmerus nobilis has been found in several Central European countries but is considered a rare species everywhere (Jakovlev et al. 2014). All the records of adults are from broadleaved forests, with the exception of Russian Karelia that lies entirely within the boreal forest zone. In Karelia, there are only two earlier records of female specimens from the Kivach nature reserve (Polevoi 2000). In Finland it has been recorded only once from Ruissalo Strict Nature Reserve, from an herb-rich spruce-dominated forest with aspen, birch, lime and oak (Quercus robur). Both the Finnish and the Karelian sites are old-growth forests, growing on fertile soils. There is a high amount of dead aspen wood, in which larvae of the species most probably develop. Threat status: Fin – VU. Mycetophilidae Boletina kivachiana Polevoi & Hedmark, 2004 Material. Turastamozero, 21 ♂♂, 21-24/7/2012 (Polevoi). In Fennoscandia, this is a characteristic species of old-growth boreal forests. However, its distribution in Karelia is still poorly known. Threat status: Fin – VU. Asilidae Choerades tenebraus Esipenko, 1974 Material. Verkhnee Myagrozero, 1 ♂, edge of a clear-cut, 22/7/2012 (Polevoi). This is the irst record in the European part of Russia. The species has previously been known from Primorye, Sakhalin and Krasnoyarsk Krai in the East (Lehr, 1999). The biology of the species is not known but its larvae probably inhabit dead wood, like other species of the genus Choerades. Two females from the Kivach nature reserve have previously been misidentiied as Choerades marginata (Jakovlev & Polevoi 1991, Polevoi, 1997). However, after inding the male of Ch. tenebraus and re-examinining old samples, it has became clear that the specimens belong to the same species. Rhagionidae Rhagio annulatus DeGeer, 1776 Material. Kainos Island, 1 ♀, 3/7/2004 (Polevoi) In Karelia, this species has previously been known only from the Kivach nature reserve (Polevoi 1997). Threat status: Fin – NT. Syrphidae Ceriana conopsoides (Linnaeus, 1758) (Fig. 12) Material. Turastamozero, 2 ♂♂, abandoned hay meadows 20-21/7/2012 (Polevoi) Larvae of the species develop in wet, decaying wood of deciduous trees. In Karelia, the species has been recorded previously from Petrozavodsk (Polevoi et al. 2009). There are also old and new unpublished indings from different parts of southern Karelia. Threat status: Kar – 4 (DD); Fin – NT. Strongylophthalmidae Strongylophthalmyia pictipes Frey, 1935 Material. Vavlok Island, 7 ♂♂, 2 ♀♀, 3/7/2004 (Polevoi). Larvae of the species develop under the bark of dead aspens. In southern Karelia, the species is relatively common in forests with a large proportion of aspen (Polevoi 1997, Humala & Polevoi 1999; Jakovlev et al. 2001, Polevoi et al. 2005). Threat status: Fin – VU. Reports of the Finnish Environment Institute 40 | 2014 273 Tachnidae Tachina grossa Linnaeus, 1758 (Fig. 13) Material. Turastamozero, 1 ♀, 21/7/2012 (Polevoi) A large and distinctive species. Larvae are parasites in caterpillars of moths of the family Lasiocampidae. It is a relatively rare species, although it may be more abundant in southern areas. In 2013 it was encountered in large numbers in southern Olonets region. Threat status: Len – 3 (NT). Fig. 12. Ceriana conopsoides (Photo Andrei Humala). Fig. 13. Tachina grossa (Photo Andrei Humala). 274 Reports of the Finnish Environment Institute 40 | 2014 List of insect species recorded in Zaonezhye and adjacent islands * – species not present in the collections, is known for the studied territory from literature only ? – doubtful identiication Abbreviations: Bol. Klim.Isl. − Bolshoi Klimenetsky Island EPHEMEROPTERA Ephemeridae Ephemera vulgata L. – Vorobyi, Eglov Isl., Khvost Isl., Rogachev Isl. ODONATA Calopterygidae Calopteryx splendens Harr. – Turastamozero, Oyatevschina, Velikaya Niva (Valle 1952) Calopteryx virgo L. – Kosmozero, Oyatevschina Coenagrionidae Coenagrion armatum Charp. – Kizhi Isl. Coenagrion hastulatum Charp. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kizhi Isl., Kosmozero, Podyelniki, Polya, Vegoruksy, Velikaya Niva (Valle 1952) Ischnura elegans V.d.Lind. – Eglov Isl., Verkhnee Myagrozero Erythromma najas Hans. – Eglov Isl., Kizhi Isl., Podyelniki Enallagma cyathigerum Charp. – Eglov Isl., Khvost Isl., Kizhi Isl., Podyelniki, Rogachev Isl., Turastamozero, Vikshezero, Vorobyi Lestidae Lestes sponsa Hans. – Bol. Klim. Isl., Oyatevschina, Turastamozero Lestes dryas Kirby – Kazhma, Kosmozero, Oyatevschina, Shun’ga, Podyelniki, Turastamozero, Cordulegasteridae Cordulegaster boltoni (Donovan) – Turastamozero, Vikshezero. Gomphidae Gomphus vulgatissimus L. – Bol. Klim. Isl., Myagrozero, Verkhnee Myagrozero Onychogomphus forcipatus L. – Vikshezero Corduliidae Cordulia aenea L. – Bol. Klim. Isl., Eglov Isl., Kazhma, Turastamozero Somatochlora lavomaculata V.d.Lind. – Kizhi Isl., Oyatevschina Somatochlora metallica V.d.Lind. – Bol. Klim. Isl., Eglov Isl., Rogachev Isl., Velikaya Niva (Valla 1952) Libellulidae Sympetrum danae Sulzer – Kazhma, Shun’ga, Turastamozero, Vorobyi, Sympetrum laveolum L. – Bol. Klim. Isl., Kazhma, Kizhi Isl., Kosmozero, Nizhneje Myagrozero, Oyatevschina, Podyelniki, Shun’ga, Turastamozero, Vegoruksy, Vorobyi, o. Yu. Oleniy. Leucorrhinia albifrons Burm. – Podyelniki Leucorrhinia caudalis Charp. – Podyelniki Leucorrhinia dubia V.d.Lind. – Bol. Klim. Isl. Leucorrhinia rubicunda L. – Bol. Klim. Isl., Kizhi Isl., Polya Libellula fulva Müller – Turastamozero Libellula quadrimaculata L. – Bol. Klim. Isl., Eglov Isl., Kizhi Isl., Nizhneje Myagrozero, Polya, Vegoruksy, Velikaya Guba (Valle 1952), Volkostrov Isl. Aeshniidae Aeshna cyanea Müll. – Tambitsy, Uzkaya Salma, Uzkaya Salma l., Tipinitsy. Aeshna grandis L. – Bol. Klim. Isl., Eglov Isl., Kosmozero, Myagrozero, Podyelniki, Polya, Shun’ga, Tambitsy, Turastamozero, Vegoruksy, Vorobyi Reports of the Finnish Environment Institute 40 | 2014 275 Aeshna juncea L. – Kazhma, Nizhneje Myagrozero, Shun’ga, Turastamozero, Vegoruksy, Vorobyi Aeshna viridis Eversmann – Nikonova Guba ORTHOPTERA Tettigoniidae Decticus verrucivorus L. – Bol. Klim. Isl., Kosmozero, Podyelniki, Rogachev Isl., Turastamozero, Vegoruksy Metrioptera brachyptera L. – Bol. Klim. Isl., Podyelniki Metrioptera roeseli Hagenbach – Turastamozero, Vegoruksy Tettigonia cantans Fuessly – Podyelniki Tetrigidae Tetrix bipunctata (L.) – Zaonezhye (Albrecht 1979), Nizhnee Myagrozero, Bol. Klim. Isl. *Tetrix subulata (L.) – Zaonezhye (Albrecht 1979) *Tetrix tenuicornis (Sahlberg) – Zaonezhye (Albrecht 1979) Acrididae Podisma pedestris (L.) – Zaonezhye (Albrecht 1979), Bol. Klim. Isl., Podyelniki, Turastamozero, Vegoruksy, Kosmozero Omocestus viridulus L. – Khvost Isl., Kosmozero, Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Turastamozero ? Chorthippus biguttulus L. – Bol. Klim. Isl. Chorthippus brunneus (Thunb.) – Bol. Klim. Isl., Turastamozero Pseudochorthippus montanus (Charp.) – Zaonezhye (Albrecht 1979), Turastamozero Pseudohorthippus parallelus (Zett.) – Turastamozero Psophus stridulus L. – Vorobyi BLATTOPTERA Blattellidae Ectobius lapponicus L. – Nizhneje Myagrozero E. sylvestris Poda – Eglov Isl., Nizhneje Myagrozero, Vegoruksy MECOPTERA Panorpidae Panorpa alpina Ramb. – Bol. Klim. Isl. P. communis L. – Kizhi Isl., Velikaya Niva, Eglov Isl., Kazhma, Khvost Isl., Kosmozero, Rogachev Isl., Shun’ga, Vegoruksy, Velikaya Niva. RAPHIDIOPTERA Raphidia xanthostigma Schumm. – Zaonezhye NEUROPTERA Chrysopidae Chrysopa perla L. – Kizhi Isl., Eglov Isl., Khvost Isl., Rogachev Isl. Anisochrysa prasina (Burm.) – Kosmozero, Bol. Klim. Isl. Hemerobiidae Drepanopteryx phalaenoides L. – Podyelniki HEMIPTERA Cixiidae Cixius cunicularius L. – Eglov Isl. ? Cixius distinguendus Kirschbaum – Podyelniki 276 Reports of the Finnish Environment Institute 40 | 2014 Membracidae Centrotus cornutus L. – Eglov Isl. Cicadellidae Cicadella viridis L. – Podyelniki Evacanthus interruptus (L.) – Turastamozero Aphrophoridae Aphrophora alni (Fall.) – Velikaya Niva, Nikonova Guba, Podyelniki,Turastamozero Aphrophora pectoralis (Mats.) – Velikaya Niva, Shun’ga, Turastamozero, Velikaya Niva Lepyronia coleoptrata L. – Eglov Isl., Rogachev Isl. Berytidae Berytinus clavipes F. – Vegoruksy Neides tipularius L. – Eglov Isl. Notonectidae Notonecta lutea Mull. – Vorobyi Microphysidae Myrmedobia coleoptrata Fallen – Shun’ga Miridae ? Adelphocoris lineolatus Goeze – Podyelniki Adelphocoris cf. seticornis F. – Podyelniki Adelphocoris quadripunctatus F. – Nizhneje Myagrozero, Podyelniki Adelphocoris seticornis F. – Nizhneje Myagrozero, Podyelniki Atractotomus parvulus Reuter – Uzkaya Salma Capsus ater L. – Vegoruksy Capsus wagneri Rem. – Podyelniki, Rogachev Isl. Closterotomus biclavatus (H-Sch.) – Uzkaya Salma. Closterotomus fulvomaculatus DeGeer – Polya ? Dicyphus constrictus Boheman – Tambitsy Globiceps lavomaculatus Deg. – Podyelniki ? Globiceps juniperi Reuter – Podyelniki Halticus apterus L. – Podyelniki Labops sahlbergii Fallen – Eglov Isl. Leptopterna dolabrata L. – Eglov Isl., Nizhneje Myagrozero, Rogachev Isl., Turastamozero, Vegoruksy Megaloceroea recticornis Geoffr. – Nizhneje Myagrozero ? Monalocoris ilicis L. – Tipinitsy ? Orthops kalmii L. – Nizhneje Myagrozero, Vegoruksy ? Plagiognathus arbustorum F. – Podyelniki Polymerus palustris Reut. – Oyatevschina, Podyelniki Polymerus unifasciatus Fabricius – Rogachev Isl. Stenodema holsata F. – Tambitsy, Tipinitsy Stenotus binotatus F. – Oyatevschina, Podyelniki Nabiidae Dolichonabis limbatus Dhlb. – Podyelniki, Tambitsy, Turastamozero Nabis lavomarginatus Scholtz – Nikonova Guba, Nizhneje Myagrozero, Podyelniki, Shun’ga, Turastamozero Anthocoridae Anthocoris nemorum (L.) – Podyelniki, Turastamozero Coreidae Coreus marginatus L. – Eglov Isl., Podyelniki, Turastamozero Rhopalidae Corizus hyoscyami L. – Eglov Isl., Oyatevschina, Podyelniki, Turastamozero Myrmus miriformis Fallen – Vegoruksy Reports of the Finnish Environment Institute 40 | 2014 277 Stictopleurus punctatonervosus (Goeze) – Oyatevschina, Podyelniki, Tipinitsy Acanthosomatidae Acanthosoma haemorrhoidale L. – Vegoruksy Elasmostethus interstinctus L. – Tipinitsy Elasmucha betulae Deg. – Podyelniki, Velikaya Niva Elasmucha ferrugata F. – Tambitsy Elasmucha grisea L. – Velikaya Niva Aradidae Aradus betulae F. – Lipovitsy Aradus depressus F. – Nizhneje Myagrozero Aradus pictus Baerensprung – Lipovitsy, Vegoruksy Lygaeidae Drymus brunneus R.F. Sahlberg – Uzkaya Salma ? Nysius thymi Wolff – Oyatevschina Pentatomidae Neottiglossa pusilla Gmel. – Eglov Isl., Podyelniki, Tipinitsy ? Carpocoris pudicus Poda – Oyatevschina Carpocoris purpureipennis Deg. – Eglov Isl., Lipovitsy, Nizhneje Myagrozero, Podyelniki, Turastamozero Dolycoris baccarum L. – Eglov Isl., Nikonova Guba, Nizhneje Myagrozero, Oyatevschina, Podyelniki, Rogachev Isl., Shun’ga, Turastamozero, Vegoruksy. Aelia acuminata (L.) – Podyelniki, Tipinitsy, Vegoruksy Chlorochroa pinicola Mulsant & Rey – Kazhma, Nizhneje Myagrozero Eurydema oleracea L. – Nizhneje Myagrozero Picromerus bidens L. – Velikaya Niva, Nikonova Guba, Podyelniki, Shun’ga, Turastamozero, Vegoruksy. Troilus luridus Fabricius – Nikonova Guba, Shun’ga COLEOPTERA (Nomenclature follows Silfverberg 2010. Species’ names within families appear in the alphabetic order) ADEPHAGA Gyrinidae *Gyrinus marinus Gyllenhal – Tolvuya, Shun’ga (Poppius 1899) Haliplidae *Haliplus luviatilus Aubé – Tolvuya (Poppius 1899) * Haliplus fulvus (Fabricius) – Shun’ga (Poppius 1899) *Haliplus furcatus Seidlitz – Tolvuya (Poppius 1899) *Haliplus lineolatus Mannerheim – Shun’ga (Poppius 1899) *Haliplus ruicollis DeGeer – Tolvuya, Kosmozero (Poppius 1899) Dytiscidae *Acathodes fuscipennis Paykull var. obscurior J.Sahlb. – Tolvuya (Poppius 1899) Acilius canaliculatus Nicolai – Podyelniki * Agabus biguttulus Thomson – Zaonezhye (Poppius 1899) * Agabus congener (Thunberg) – Zaonezhye (Poppius 1899) * Agabus setulosus J.Sahlb. – Tolvuya (Poppius 1899) * Agabus uliginosus L. – Tolvuya (Poppius 1899) *Agabus sturmii (Gyllenhal) – Tolvuya (Poppius 1899) *Bidessus unistriatus (Goeze) – Kizhi Isl., Tolvuya, Velikaya Guba (Poppius 1899) *Coelambus impressopunctatus (Schaller) – Tolvuya, Velikaya Guba (Poppius 1899) Colymbetes paykulli Er. – Velikaya Guba (Poppius 1899), Oyatevschina, Podyelniki *Colymbetes striatus L. – Tolvuya (Poppius 1899) 278 Reports of the Finnish Environment Institute 40 | 2014 *Dytiscus marginalis L. – Tolvuya (Poppius 1899) * Graptodytes granularus (L.) – Tolvuya (Poppius 1899) * Graptodytes pictus (Fabricius.) – Tolvuya (Poppius 1899) *Heterocerus fuculus Kiesenwetter – Oleny Island (Poppius 1899) *Hydroporus ruifrons (Müller) – Kosmozero, Tolvuya (Poppius 1899) ? *Hydroporus fennicus Seidlitz – Kosmozero, Velikaya Guba (Poppius 1899) *Hydroporus erythrocephalus (L.) – Kosmozero, Tolvuya (Poppius 1899) *Hydroporus pubescens (Gyllenhal) – Tolvuya (Poppius 1899) *Hydroporus melanarius Sturm – Velikaya Guba (Poppius 1899) *Hydroporus obscurus Sturm – Kizhi Isl., Tolvuya (Poppius 1899) *Hydroporus tristis Paykull – Velikaya Guba (Poppius 1899) *Hydroporus striola (Gyllenhal) – Kosmozero, Tolvuya (Poppius 1899) *Hydrotus inaequalis (Fabricius) – Tolvuya (Poppius 1899) *Ilybius obcurus Marshall – Tolvuya (Poppius 1899) *Ilybius wasastjernae Sahlberg – Velikaya Guba (Poppius 1899) *Nebrioporus depressus (Fabricius) – Kizhi Isl., Tolvuya (Poppius 1899) *Noterus crassicornis Fabricius – Kizhi Isl., Oleny Island (Poppius 1899) *Parnus prolifericornis Fabricius – Kosmozero, Tolvuya, Shun’ga (Poppius 1899) *Rantus bistriatus (Bergsträsser) – Tolvuya (Poppius 1899) Carabidae *Agonum afrum (Duftschmid) – Velikaya Guba, Shun’ga (Poppius 1899) Agonum ericeti (Panzer) – Velikaya Guba (Poppius 1899), Kizhi Isl., B. Klim. Isl. Agonum fuliginosum (Panzer) – Kizhi Isl., B. Klim. Isl. *Agonum gracile Sturm – Shun’ga (Poppius 1899) *Agonum viduum (Panzer) – Shun’ga (Poppius 1899) *Amara apricaria Paykull – Shun’ga (Poppius 1899) *Amara aulica Panz. – Unitsa (Poppius 1899) Amara brunnea (Gyllenhal) – Unitsa (Poppius 1899), Kizhi Isl., Bol. Klim. Isl., Yu. Oleny Isl. *Amara communis Panzer – Tolvuya, Kosmozero (Poppius 1899) *Amara familiaris (Duftschmid) – Tolvuya (Poppius 1899) *Amara plebeja (Gyllenhal) – Tolvuya, Velikaya Guba (Poppius 1899) *Anchomenus sexpunctatus L. – Velikaya Guba, Kosmozero (Poppius 1899) *Badister peltatus (Panzer) – Kosmozero (Poppius 1899) *Bembidion doris (Panzer) –Tolvuya, Lizhmajärvi (Poppius 1899) *Bembidion lampros (Herbst) – Kizhi Isl., Velikaya Guba, Kosmozero, Tolvuya, Shun’ga (Poppius 1899), Vegoruksy *Bembidion obliquum Sturm – Velikaya Guba (Poppius 1899) Bembidion quadrimaculatum L. – Velikaya Guba, Tolvuya, Shun’ga (Poppius 1899), Vegoruksy *Blethisa multipunctata L. – Tolvuya (Poppius 1899) *Calathus erratus Sahlberg – Tolvuya, Kosmozero (Poppius 1899) Calathus micropterus (Duftschmid) – B. Klim. Isl., Yu. Oleny Isl., Lipovitsy Carabus glabratus L. Tolvuya (Poppius 1899), Kosmozero, B. Klim. Island, Vegoruksy, Lipovitsy Carabus violaceus L. – B. Klim. Isl. *Cicindela campestris L. – Kizhi Isl. (Poppius 1899) *Cicindela hybrida L. – Kosmozero (Poppius 1899) *Clivina fossor L. – Shun’ga (Poppius 1899) Cychrus caraboides L. – B. Klim. Isl. (Poppius 1899), Kosmozero Dromius agilis L. – Unitsa (Poppius 1899), B. Klim. Island, Lipovitsy Reports of the Finnish Environment Institute 40 | 2014 279 *Dromius sigma Rossi – Unitsa (Poppius 1899) *Dyschirius aeneus (Dejean) – Tolvuya (Poppius 1899) *Dyschirius globosus (Herbst) – Zaonezhye (Poppius 1899) Elaphrus cupreus Duftschmid – Vikshezero ?*Feronia vitrea Dejean – Unitsa (Poppius 1899) Harpalus afinis (Schrank). – Kosmozero, Tolvuya, Shun’ga (Poppius 1899), B. Klim. Isl. Harpalus latus (L). – Kosmozero (Poppius 1899), Lipovitsy Lebia chlorocephala L. – Kizhi Isl. (Poppius 1899), B. Klim. Isl. * Lebia cruxminor L. – Kizhi Isl. (Poppius 1899) *Nebria gyllenhalii Schönh. – Tolvuya (Poppius 1899) *Oodes helopioides (Fabricius) – Velikaya Guba (Poppius 1899) *Patrobus excavatus Paykull var. assimilis Chaud. – Tolvuya (Poppius 1899) * Poecilus versicolor Sturm – Velikaya Guba (Poppius 1899) Pterostichus diligens (Sturm.) − Bol. Klim. Isl. Pterostichus melanarius (Illiger) − Bol. Klim. Isl. Pterostichus minor (Gyllenhal, 1827) – Shun’ga (Poppius 1899) Pterostichus niger (Schall.) − Bol. Klim. Isl. Pterostichus nigrita (Paykull) − Bol. Klim. Isl. Pterostichus oblongopunctatus (Fabricius) − Bol. Klim. Isl., Yu. Oleny Isl. *Tachys nanus Gyllenhal – Kizhi Isl., Velikaya Guba (Poppius 1899) *Taphria nivalis (Panzer) – Tolvuya, Shun’ga (Poppius 1899) *Trechys rivularis Gyllenhal – Velikaya Guba (Poppius 1899) *Trechys secalis Paykull – Tolvuya (Poppius 1899) POLYPHAGA HYDROPHILOIDEA Hydrophilidae *Berosus luridus L. – Velikaya Guba (Poppius 1899) *Laccobius minutus L. – Kosmozero, Tolvuya, Shun’ga (Poppius 1899) *Philydrus frontalis Er. – Velikaya Guba, Tolvuya (Poppius 1899) *Choetarthria seminulum Paykull – Shun’ga (Poppius 1899) * Coelostoma orbiculare Fabricius – Velikaya Guba (Poppius 1899) *Cercyon haemorrhoidalis (Fabricius) – Velikaya Guba, Shun’ga (Poppius 1899) *Cercyon unipunctatus (L.) – Velikaya Guba (Poppius 1899) ?*Cryptopleurum atomarium (Fabricius) – Velikaya Guba, Tolvuya (Poppius 1899) *Helophorus aquaticus (L.) – Tolvuya, Shun’ga (Poppius 1899) *Hydrochus elongatus (Schaller) – Kosmozero (Poppius 1899) *Hydrochus brevis (Herbst) – Kizhi Isl. (Poppius 1899) HISTEROIDEA Sphaeritidae Sphaerites glabratus (Fabricius) − Bol. Klim.Isl. Histeridae *Platysoma minus (Rossi) – Kizhi Isl. (Poppius 1899) *Platysoma deplanatum (Gyllenhal) – Kizhi Isl. (Poppius 1899) *Margarinotus ventralis (Marseul) – Kizhi Isl. (Poppius 1899) Plegaderus vulneratus (Panzer) – Kizhi Isl. (Poppius 1899), Bol. Klim.Isl. 280 Reports of the Finnish Environment Institute 40 | 2014 STAPHYLINOIDEA Hydraenidae *Limnebius truncatellus (Thunberg) – Kizhi Isl., Kosmozero, Tolvuya, Shun’ga (Poppius 1899) Ptiliidae *Acrotrichis grandicollis Mannerheim – Kosmozero (Poppius 1899) *Acrotrichis thoracica (Waltl) – Shun’ga (Poppius 1899) *Acrotrichis montandonii (Allibert) – Unitsa (Poppius 1899) *Pteryx suturalis (Heer) – Unitsa (Poppius 1899) *Ptiliolum caledonicum (Sharp) – Unitsa (Poppius 1899) Leiodidae *Leiodes gyllenhalii Stephens – Kizhi Isl., Tolvuya (Poppius 1899) *Leiodes polita (Marsham) – Unitsa (Poppius 1899) Anisotoma axillaris (Gyll.) − Bol. Klim.Isl., Volkostrov Isl. Anisotoma castanea (Hbst.) − Bol. Klim.Isl. Anisotoma glabra (Kug.) − Bol. Klim.Isl., Yu. Oleny Isl. Anisotoma humeralis (Fabricius) − Bol. Klim.Isl., Oyatevschina, Yu. Oleny Isl., Volkostrov Isl. Anisotoma orbicularis (Hbst.) − Bol. Klim.Isl. Amphicyllus globus Fabricius − Bol. Klim.Isl., Oyatevschina, Volkostrov Isl. Agathidium badium Erich. − Bol. Klim.Isl., Yu. Oleny Isl. Agathidium confusum Bris. de Barn. − Bol. Klim. Isl. Agathidium discoideum Erich. − Bol. Klim. Isl., Yu. Oleny Isl. Agathidium pisanum Bris. de Barn. − Bol. Klim.Isl. Agathidium seminulum (L.) − Bol. Klim.Isl., Volkostrov Isl. Sciodrepoides watsoni (Spence) – Velikaya Guba (Poppius 1899), Bol. Klim. Isl., Volkostrov Isl. *Stenichnus bicolor (Denny) – Kizhi Isl. (Poppius 1899) Silphidae Necrodes littoralis (L.) – Unitsa (Poppius 1899), Podyelniki Nicrophorus vespillo (L.) − Bol. Klim.Isl. Nicrophorus vespilloides Herbst − Bol. Klim.Isl. Oiceoptoma thoracica (L.) – Velikaya Guba (Poppius 1899), Lipovitsy, Bol. Klim. Isl. Phosphuga atrata (L.) − Vorobyi Staphylinidae *Acrotona aterrima Gravenhorst – Shun’ga , Tolvuya (Poppius 1899) *Acryria inlata Gyllenhal – Kizhi Isl. (Poppius 1899) *Amisha analis Gravenhorst – Shun’ga (Poppius 1899) *Anthobium longipanne Er. – Kosmozero (Poppius 1899) *Anthobium ophthalmicum Paykull – Kizhi Isl., Kosmozero (Poppius 1899) *Atheta celata Er. – Unitsa (Poppius 1899) *Baptolinus alternans Gravenhorst – Velikaya Guba (Poppius 1899) *Baryodma lanuginosa Gravenhorst – Unitsa (Poppius 1899) *Baryodma lugubris Aubé – Tolvuya (Poppius 1899) *Baryodma morion Gravenhorst – Shun’ga (Poppius 1899) *Baryodma nitida Gravenhorst – Kizhi Isl. (Poppius 1899) *Bledius fracticornis Paykull – Shun’ga (Poppius 1899) *Bolitochara pulchra (Gravenhorst) – Kosmozero (Poppius 1899) *Bryaxis bulbifer Reich. – Shun’ga (Poppius 1899) *Creophilus maxillosus L. – Shun’ga (Poppius 1899) *Cryptobium fracticorne Paykull – Shun’ga (Poppius 1899) *Dinarcaea aequata Er. – Kizhi Isl., Velikaya Guba (Poppius 1899) Reports of the Finnish Environment Institute 40 | 2014 281 *Etheothassa concinna Marsh. – Kizhi Isl. (Poppius 1899) *Euplectus karsteni Reichenbach, – Kizhi Isl. (Poppius 1899) *Gabrius splendidulus Gravenhorst – Kizhi Isl., Kosmozero (Poppius 1899) *Gabrius trossulus Nordmann – Unitsa (Poppius 1899) *Geodromicus plagiatus Fabricius, var. nigrita Mull. – Tolvuya (Poppius 1899) *Gyrophaena laevipennis Kr. – Kosmozero, Unitsa (Poppius 1899) *Gyrophaena manca Er. – Kosmozero (Poppius 1899) *Haploderus caelatus Gravenhorst – Shun’ga (Poppius 1899) *Ischnosoma splendida Gravenhorst – Kosmozero, Velikaya Guba (Poppius 1899) *Leptusa analis Gyllenhal – Kizhi Isl. (Poppius 1899) Lordithon lunulatus L. – Kurgenitsy *Micrisaurus xantopus Er. – Unitsa (Poppius 1899) *Omalium caesum Gravenhorst – Shun’ga (Poppius 1899) *Omalium excavatum Steph. – Shun’ga (Poppius 1899) *Othius lapidicola Kiesw. – Unitsa (Poppius 1899) Oxyporus maxillosus Fabricius – Kurgenitsy Oxyporus rufus (L.) – Kurgenitsy *Oxytelus fulvipes Er. – Shun’ga (Poppius 1899) *Oxytelus rugosus Sahlb. – Shun’ga (Poppius 1899) *Philonthus agilis Gravenhorst – Shun’ga (Poppius 1899) *Philonthus cephalotes Gravenhorst – Kizhi Isl., Shun’ga (Poppius 1899) *Philonthus fulvipes Fabricius – Shun’ga (Poppius 1899) *Philonthus micans Gravenhorst – Tolvuya (Poppius 1899) *Philonthus opacus Gyllenhal – Kizhi Isl., Shun’ga , Tolvuya (Poppius 1899) *Philonthus sordidus Gravenhors – Kizhi Isl. (Poppius 1899) *Philonthus splendens Fabricius – Kizhi Isl. (Poppius 1899) *Philonthus umbratilis Gravenhorst – Shun’ga (Poppius 1899) *Phyllodrepa ruipes Geoffroy – Shun’ga (Poppius 1899) *Placusa inima Er. – Unitsa (Poppius 1899) *Placusa pumilio Er. – Unitsa (Poppius 1899) *Platystethus nodufrons Sahlb. – Shun’ga, Tolvuya (Poppius 1899) *Raphirus attenuatus Gyllenhal – Tolvuya, Unitsa (Poppius 1899) *Raphirus umbrinus Er. – Unitsa (Poppius 1899) Scaphidium quadrimaculatum Olivier − Bol. Klim. Isl. Scaphisoma agaricinum (L.) Kizhi Isl., Tolvuya (Poppius 1899), Bol. Klim.I sl., Volkostrov Isl. Scaphisoma boleti (L.) – Bol. Klim.Isl., Yu. Oleny Isl. Scaphisoma boreale (Lundbl.) – Bol. Klim. Isl., Volkostrov Isl. *Scaphisoma subalpinum Reitter – Kizhi Isl., Kosmozero (Poppius 1899) *Stenus bifoveolatus Gyllenhal – Unitsa (Poppius 1899) *Stenus biguttatus L. – Tolvuya (Poppius 1899) *Stenus canaliculatus Gyllenhal – Tolvuya (Poppius 1899) *Stenus carbonarius Gyllenhal – Kizhi Isl., Shun’ga, Unitsa (Poppius 1899) *Stenus fornicatus Steph. – Kizhi Isl. (Poppius 1899) *Stenus fuscicornis Steph. – Shun’ga (Poppius 1899) *Stenus fuscipes Gravenhorst – Unitsa (Poppius 1899) *Stenus melanarius Steph. – Kizhi Isl., Oleny Island (Poppius 1899) *Stenus nanus Steph. – Unitsa (Poppius 1899) *Stenus nitens Steph. – Shun’ga (Poppius 1899) *Stenus oculatus Gravenhorst – Unitsa (Poppius 1899) *Stenus opticus Gravenhorst – Kizhi Isl. (Poppius 1899) *Stenus palposus Zetterstedt – Shun’ga (Poppius 1899) *Stenus proditor Er. – Velikaya Guba (Poppius 1899) 282 Reports of the Finnish Environment Institute 40 | 2014 *Stenus pussilus Steph. – Kizhi Isl. (Poppius 1899) *Stenus scabriculus J.Sahlb. – Unitsa (Poppius 1899) *Stenus speculator (Lac.) – Kuzaranda, Shun’ga (Poppius 1899) *Stenus tarsatus Ljung. – Kizhi Isl., Kosmozero, Shun’ga, Tolvuya, Velikaya Guba (Poppius 1899) *Stenus vafellus Er. – Velikaya Guba (Poppius 1899) *Tachinus collaris Gravenhorst – Shun’ga (Poppius 1899) *Tachinus imetarius Gravenhorst – Kizhi Isl. (Poppius 1899) *Tachinus laticollis Gravenhorst – Velikaya Guba (Poppius 1899) *Tachinus marginatus Gyllenhal – Tolvuya (Poppius 1899) Tachyporus obtusus L. – Tipinitsy *Tachyporus scitulus Er. – Unitsa (Poppius 1899) *Tanycraerus laqueatus Marsh. – Kizhi Isl. (Poppius 1899) *Trichoderma pubescens DeGeer. – Bol. Klim. Isl. (Poppius 1899) *Xantholinus distans Muls. & Rey. – Unitsa (Poppius 1899) SCARABAEOIDEA Lucanidae Ceruchus chrysomelinus (Hochenwarth) – Lipovitsy Platycerus caprea (DeGeer) – Bol. Klim. Isl., Volkostrov Isl. Geotrupidae Geotrupes stercorosus (Scriba) – Zaonezhye (Poppius 1899), Lipovitsy, Kosmozero, Eglov Isl. Kizhi Isl., Bol. Klim.Isl. Scarabaeidae *Aphodius merdarius Fabricius – Velikaya Guba (Poppius 1899) *Aphodius niger (Panzer, 1797) – Tolvuya (Poppius 1899) *Aphodius plagiatus (L.) – Tolvuya (Poppius 1899) *Aphodius prodromus (Brahm) – Velikaya Guba (Poppius 1899) *Aphodius punctatosulcatus Sturm) – Velikaya Guba (Poppius 1899) Aphodius ruipes (L.) – Kizhi Isl. (Poppius 1899), Bol. Klim.I sl., KIzhIsl., Volkostrov Isl. *Aphodius sordidus (Fabricius) – Tolvuya (Poppius 1899) Cetonia aurata (L.) − Bol. Klim. Isl. *Onthophagus nuchicornis (L.) – Kizhi Isl. (Poppius 1899) Phylloperta horticola (L.) − Bol. Klim.Isl., Volkostrov Isl. Protaetia cuprea (Fabricius, 1775) ssp. metallica Herbst − Kurgenitsy, Yu. Oleny Isl., Nizhneje Myagrozero, Eglov Isl., Khvost Isl., Rogachev Isl. Trichius fasciatus (L.) – Kizhi Isl., Kosmozero, Kuzaranda, Velikaya Guba (Poppius 1899), Bol. Klim. Isl., Eglov Isl., Khvost Isl., Nizhneje Myagrozero, Podyelniki, Uzkaya Salma, Vegoruksy, Lipovitsy. SCIRTOIDEA Scritidae Microcara testacea (L.) – Tolvuya (Poppius 1899), Khvost Isl. *Cyphon variabilis (Thunberg) – Kosmozero (Poppius 1899) Melyridae Dasytes niger (L) – Kosmozero, Shun’ga , Tolvuya (Poppius 1899) DASCILLOIDEA Dascilidae Dascillus cervinus (L.) – Kizhi Isl., Kosmozero (Poppius 1899), Bol. Klim.Isl. Reports of the Finnish Environment Institute 40 | 2014 283 BUPRESTOIDEA Buprestidae Anthaxia quadripunctata (L.) – Tolvuya (Poppius 1899), Oyatevschina, Vegoruksy, Uzkaya Salma Chrysobothris chrysostigma (L.) – Nizhnee Myagrozero, Kosmozero, Vegoruksy *Habroloma nanum (Paykull) – Kizhi Isl. (Poppius 1899) Phaenops cyanea (Fabricius) – Vegoruksy Trachys minutus L. – Khvost Isl. BYRRHOIDEA Byrrhidae *Byrrhus pilula (L.) – Kizhi Isl. (Poppius 1899) *Byrrhus pustulatus (Forster) – Kizhi Isl. (Poppius 1899) *Cytilus auricomus (Duftschmid) – Kosmozero (Poppius 1899) DRYOPOIDEA Elmidae * Normandia nitens (Müller) – Shun’ga (Poppius 1899) ELATEROIDEA Eucnemidae Hylochares populi Muona & Brustle – Polya, Tambitsy Microrrhagus pygmaeus (Fabricius) − Bol. Klim.Isl. Elateridae Ampedus balteatus (L.) − Bol. Klim.Isl., Eglov Isl. *Ampedus cinnabarinus (Eschscholtz) – Kizhi Isl. (Poppius 1899) Ampedus erythrogonus (Müller) − Bol. Klim. Isl., Volkostrov Isl. Ampedus nigrinus (Herbst) – Unitsa (Poppius 1899) − Bol. Klim.Isl., Volkostrov Isl. *Ampedus pomorum (Herbst) – Kosmozero (Poppius 1899) Ampedus sanguineus (L.) – Oyatevschina Ampedus tristis (L.) − Bol. Klim. Isl., Kizhi Isl. Athous subfuscus (Müller) – Velikaya Guba (Poppius 1899), Bol. Klim. Isl., Eglov Isl., Volkostrov Isl. * Cidnopus aeruginosus (Olivier) – Kizhi Isl. (Poppius 1899) Ctenicera pectinicornis (L.) – Kizhi Isl. (Poppius 1899), Bol. Klim.Isl., Volkostrov Isl. Ctenicera cuprea (Fabricius) – Eglov Isl., Khvost Isl., Rogachev Isl. *Dalopius marginatus (L.) – Shun’ga (Poppius 1899), Bol. Klim. Isl. *Denticollis borealis (Paykull) – Kizhi Isl. (Poppius 1899) Denticollis linearis L. – Kizhi Isl., Lipovitsy, Kosmozero (Poppius 1899), Bol. Klim. Isl. Eanus costalis (Paykull) − Bol. Klim.Isl., Kizhi Isl., Volkostrov Isl. *Ectinus aterrimus (L.) – Kizhi Isl. (Poppius 1899) Harminius undulatus (Deg.) − Bol. Klim. Isl., Kosmozero, Yu. Oleny Isl. *Lacon fasciatus (L.) – Tolvuya, Velikaya Guba (Poppius 1899) *Liotrichus affmis (Paykull) − Bol. Klim.Isl. (Poppius 1899) Melanotus castanipes (Paykull) − Bol. Klim. Isl. *Oedostethus quadripustulatus (Fabricius) – Tolvuya, Kosmozero (Poppius 1899) Prosternon tessellatum (L.) – Kizhi Isl., Velikaya Guba (Poppius 1899), Eglov Isl., Rogachev Isl. Sericus brunneus (L.) − Bol. Klim. Isl. Selatosomus aeneus (L.) – Eglov Isl., Rogachev Isl. Selatosomus cruciatus (L.) − Bol. Klim. Isl., Volkostrov Isl. Selatosomus melancholicus (Fabricius) − Bol. Klim. Isl. 284 Reports of the Finnish Environment Institute 40 | 2014 CANTHAROIDEA Lycidae Dictyoptera aurora (Herbst) – Velikaya Guba (Poppius 1899), Kurgenitsy Lopheros rubens (Gyllenhal) – Vikshezero Lygistopterus sanguineus L. – Velikaya Guba (Poppius 1899), Bol. Klim.Isl., Nizhneje Myagrozero, Vikshezero Platycis minutus Fabricius – Turastamozero Lampyriae Lampyrus noctiluca L. – Kizhi Isl., Kosmozero, Uzkaya Salma, Velikaya Guba (Poppius 1899), Bol. Klim.Isl., Kizhi Cantharidae Abdisia schoenherri (Dejean) – Dianova Gora, Kosmozero (Poppius 1899), Bol. Klim. Isl. Polya, Uzkaya Salma, Volkostrov Isl. Cantharis igurata Mannerheim – Kizhi Isl., Kosmozero, Velikaya Guba (Poppius 1899), Eglov Isl., Khvost Isl. *Cantharis lavilabris Fallén – Kosmozero, Shun’ga , Tolvuya (Poppius 1899) Cantharis nigricans (Müller) – Eglov Isl., Rogachev Isl. Cantharis pellucida Fabricius – Lipovitsy, Rogachev Isl. Malthinus biguttatus (L.) – Kuzaranda, Tolvuya (Poppius 1899), Bol. Klim.Isl. Eglov Isl. Malthinus punctatus (Geoffroy) – Kosmozero (Poppius 1899) Eglov Isl., Khvost Isl., Uzkaya Salma Malthodes brevicollis (Paykull) – Kizhi Isl. (Poppius 1899), Eglov Isl. *Malthodes lavoguttatus Kiesenwetter –Tolvuya (Poppius 1899) Malthodes fuscus Waltl – Uzkaya Salma *Malthodes mysticus Kiesenwetter – Schunga (Poppius 1899) *Malthodes maurus (Laporte de Castelnau) – Kizhi Isl. (Poppius 1899) Podabrus lapponicus (Gyllenhal) –Velikaya Guba (Poppius 1899) Rhagonycha atra (L.) – Kizhi Isl., Kosmozero (Poppius 1899), Bol. Klim.Isl. Lipovitsy Rhagonycha elongata (Fallen) – Bol. Klim.Isl. Rhagonycha lignosa (Müller) – Eglov Isl., Lipovitsy, Polya Rhagonycha nigriventris Motschulsky– Khvost Isl., Polya Rhagonycha testacea (L.) – Kizhi Isl. (Poppius 1899) BOSTRICHOIDEA Dermestidae Dermestes lardarius L. – Kizhi Isl. Trogoderma glabrum (Herbst) – Kizhi Isl. Anthrenus museorum (L.) – Schun’ga (Poppius 1899), Kizhi Isl., Oyatevschina Anobiidae Anobium ruipes Fabricius – Kizhi Isl., Oyatevschina, Bol. Klim. Isl. Anobium thomsoni (Kraatz.) – Bol. Klim. Isl. Caenocara bovistae (Hoffmann.) – Kizhi Isl. (Poppius 1899) Dorcatoma dresdensis (Herbst). –Kosmozero (Poppius 1899), Bol. Klim.Isl., Volkostrov Isl. Dorcatoma robusta Strand. – Bol. Klim.Isl. , Volkostrov Isl. Hadrobregmus pertinax (L.) – Kizhi Isl., Bol. Klim. Isl. Hadrobregnus confusus (Kraatz) – Kizhi Isl. Priobium carpini (Herbst) – Kizhi Isl., Kosmozero, Schun’ga (Poppius 1899), Kizhi Isl. Ptilinus fuscus Geoffroy – Bol. Klim. Isl., Lipovitsy, Polya,Vegoruksy, Turastamozero, Volkostrov Isl., Yu. Oleny Ptinus raptor Sturm – Kizhi Isl. Ptinus villiger Reitter – Kizhi Isl. Reports of the Finnish Environment Institute 40 | 2014 285 LYMEXYLOIDEA Lymexylonidae Hylecoetus dermestoides (L.) – Bol. Klim.Isl., Kosmozero, Volkostrov Isl. CLEROIDEA Trogossitidae Grynocharis oblonga (L.) – Kizhi Isl. Ostoma ferruginea (L.) – Uzkaya Salma, Bol. Klim.Isl., Kosmozero, Lipovitsy Peltis grossa (L.) – Dianova Gora (Poppius 1899), Lipovitsy, Kurgenitsy Cleridae Thanasimus formicarius L. – Vikshezero Dasytidae Dasytes niger (L.) – Rogachev Isl. Dolichosoma lineare (Rossi) – Eglov Isl., Rogachev Isl. Malachidae Malachius bipustulatus (L.) – Velikaya Guba (Poppius 1899), Eglov Isl., Kizhi Isl., Vikshezero CUCUJOIDEA Kateretidae *Brachypterolus pulicarius (L.) – Kizhi Isl. (Poppius 1899) *Brachypterus urticae (Fabricius) – Shun’ga (Poppius 1899) *Kateretes pusillus (Thunberg) – Kosmozero (Poppius 1899) Nitidulidae Cychramus luteus (Fabricius) – Kosmozero, Unitsa (Poppius 1899), Velikaya Niva, Bol. Klim.Isl., Volkostrov Isl. Cychramus variegatus (Herbst) – Bol. Klim.Isl., Tambitsy, Tipinitsy, Uzkaya Salma, Volkostrov Isl. Cyllodes ater Hbst. – Kurgenitsy, Oyatevschina, Lipovitsy, Uzkaya Salma, Volkostrov Isl. *Epuraea lapponica (J.Sahlberg ) – Shun’ga , Tolvuya (Poppius 1899) *Epuraea longula Erichson – Velikaya Guba (Poppius 1899) *Epuraea marseuli Reitter – Velikaya Guba (Poppius 1899) *Epuraea pallescens (Stephens) – Kizhi Isl., Tolvuya (Poppius 1899) *Epuraea terminalis (Mannerheim) – Unitsa (Poppius 1899) Glischrochilus hortensis (Geoffroy) – Bol. Klim. Isl. Glischrochilus quadripunctatus (L.) – Bol. Klim. Isl., Tipinitsy, Vikshezero Ipidia binotata Reitter – Volkostrov Isl. *Meligethes aeneus (Fabricius) – Kosmozero, Tolvuya (Poppius 1899) *Meligethes lavimanus Stephens, 1830 – Unitsa (Poppius 1899) *Meligethes subrugosus (Gyllenhal, 1808) – Kizhi Isl., Tolvuya (Poppius 1899) *Meligethes viduatus Sturm – Shun’ga, Kosmozero (Poppius 1899) Pityophagus ferrugineus L. – Volkostrov Isl. Pocadius ferrugineus (Fabricius) – Velikaya Guba (Poppius 1899), Bol. Klim. Isl. Soronia punctatissima (Ill.) – Bol. Klim. Isl. Monotomidae *Rhizophagus bipustulatus (Fabricius) – Shun’ga, Kosmozero (Poppius 1899) Rhizophagus cribratus (Gyllenhal) – Bol. Klim. Isl. Rhizophagus depressus (Fabricius) – Bol. Klim. Isl. Rhizophagus dispar (Paykull) – Kizhi Isl., Kosmozero (Poppius 1899), Bol. Klim. Isl., Volkostrov Isl. 286 Reports of the Finnish Environment Institute 40 | 2014 Rhizophagus puncticollis Sahlberg – Kopanets Lake, Kurgenitsy Silvanidae * Silvanus unidentatus (Olivier) – Dianova Gora,Velikaya Guba (Poppius 1899) Phalacridae *Phalacrius substriatus Gyllenhal – Kizhi Isl., Kosmozero, Shun’ga, Tolvuya, Velikaya Guba (Poppius 1899) Cryptophagidae *Antherophagus pallens (L.) – Kizhi Isl. (Poppius 1899) *Atomaria fuscata (Schönherr) – Unitsa, Velikaya Guba (Poppius 1899) *Atomaria peltata Kraatz – Unitsa (Poppius 1899) Micrambe abietis (Paykull) – Bol. Klim. Isl. Erotylidae Dacne bipustulata (Thunberg) – Bol. Klim. Isl. Triplax aenea Schall. – Bol. Klim. Isl., Lipovitsy, Kosmozero Triplax ruipes Fabricius – Vikshezero Triplax russica L. – Zaonezhye (Poppius 1899), Bol. Klim. Isl., Volkostrov Isl., Yu. Oleny, Turastamozero, Uzkaya Salma Triplax scutellaris (Charp.) – Kurgenitsy Byturidae Byturus tomentosus (Deg.) – Bol. Klim.Isl., Volkostrov Isl. Cerylonidae Cerylon fagi Brisout de Barneville − Bol. Klim. Isl., Volkostrov Isl. Cerylon ferrugineum Stephens − Volkostrov Isl. Cerylon histeroides (Fabricius) – Kosmozero, Unitsa (Poppius 1899), Bol. Klim. Isl. Endomychidae Endomychus coccineus (L.) – Volkostrov Isl. Coccinellidae Anatis ocellata L. – Turastamozero Anisosticta novemdecimpunctata L. – Vorobyi Calvia quatuordecimguttata L. – Oyatevschina, Podyelniki, Rogachev Isl., Turastamozero Chilocorus renipustulatus Scriba – Turastamozero Coccinella hieroglyphica L. –Eglov Isl., Podyelniki, Turastamozero, Verkhnee Myagrozero *Coccinella magniica Redtenbacher – Unitsa (Poppius 1899) Coccinella septempunctata L. – Kizhi Isl., Kosmozero, Vikshezero, Bol. Klim. Isl., Tolvuya (Poppius 1899) Coccinula quatuordecimpustulata L. – Vorobyi, Eglov Isl., Oyatevschina, Podyelniki, Verkhnee Myagrozero, Vikshezero Hippodamia notata L. – B. Klim. Isl., Oyatevschina, Podyelniki, Uzkaya Salma, Vegoruksy, Vorobyi Hippodamia septemmaculata DeGeer – Vorobyi Myrrha octodecimguttata L. – Kizhi Isl. (Poppius 1899), Eglov Isl., Turastamozero Myzia oblongoguttata (L.) – Vegoruksy, Eglov Isl. *Oenopia conglobata L – Kosmozero (Poppius 1899) Propylea quatuordecimpunctata L. – Vorobyi, Eglov Isl., Podyelniki, Rogachev Isl., Tipinitsy, Turastamozero, Vikshezero Psyllobora vigintiduopunctata (L.) – Vorobyi, Eglov Isl., Tambitsy, Vegoruksy, Vikshezero Latridiidae Corticarina fuscula (Gyllenhal) – Kizhi Isl., Kosmozero, Shun’ga , Velikaya Guba (Poppius 1899) *Corticaria ferruginea Marsham – Tolvuya (Poppius 1899) Corticaria lapponica Zett. – Bol. Klim. Isl. Reports of the Finnish Environment Institute 40 | 2014 287 *Corticaria lateritia Mannerheim – Oleny Isl. (Poppius 1899) *Corticaria pubescens (Gyllenhal) – Shun’ga (Poppius 1899) Enicmus rugosus (Herbst) – Bol. Klim. Isl., Volkostrov Isl. Latridius hirtus (Gyllenhal) – Bol. Klim. Isl. *Latridius minutus (L.) – Shun’ga (Poppius 1899) *Stephostethus lardarius (DeGeer) – Oleny Isl. (Poppius 1899) Mordellidae *Mordellochroa abdominalis (Fabricius, 1775)– Kuzaranda (Poppius 1899) Mordella aculeata L. – Bol. Klim. Isl. Mordella holomelaena Apfelbeck – Shunevskiy Isl. Mordellistena humeralis (L.) – Shun’ga (Poppius 1899), Shunevskiy Isl. Mordellistena parvula (Gyllenhal) – Kizhi Isl. (Poppius 1899), Bol. Klim. Isl. Mordellistena pumila (Gyllenhal, 1810)– Vorobyi Tomoxia bucephala Costa – Bol. Klim. Isl., Podyelniki Zopheridae Bitoma crenata (Fabricius) – Dianova Gora, Unitsa (Poppius 1899) TENEBRIONOIDEA Mycetophagidae Litargus connexus (Geoffroy) – Bol. Klim. Isl. *Mycetophagus decempunctatus Fabricius – Kizhi Isl. (Poppius 1899) Mycetophagus fulvicollis Fabricius – Bol. Klim. Isl. Mycetophagus multipunctatus Fabricius – Kosmozero, Unitsa (Poppius 1899), Bol. Klim. Isl. Mycetophagus piceus (Fabricius) – Velikaya Guba (Poppius 1899), Bol. Klim. Isl. Mycetophagus populi Fabricius – Bol. Klim. Isl. Mycetophagus quadripustulatus (L.) – Velikaya Guba (Poppius 1899), Kurgenitsy, Volkostrov Isl. Ciidae *Cis comptus (Gyllenhal) – Dianova Gora, Schun’ga, Unitsa (Poppius 1899) *Cis bidentatus (Olivier) – Kosmozero (Poppius 1899) Cis jacquemartii Mellié – Bol. Klim.Isl. Cis micans (Fabricius) – Dianova Gora, Unitsa (Poppius 1899), B. Klim. Isl. *Cis rugulosus Mellié –Schun’ga (Poppius 1899) *Dolichocis laricinus (Mellié, 1848) – Kosmozero (Poppius 1899) *Octotemnus glabriculus (Gyllenhal) – Dianova Gora (Poppius 1899) Orthocis alni (Gyllenhal) – Bol. Klim. Isl., Volkostrov Isl. *Sulcacis fronticornis (Panzer, 1805) – Dianova Gora (Poppius 1899) Tenebrionidae Bolitophagus reticulatus (L.) – Bol. Klim. Isl., Uzkaya Salma, Polya, Volkostrov Isl. Diaperis boleti (L.) – Bol. Klim. Isl. Lagria hirta (L.) – Zaonezhye (Poppius 1899), Vorobyi, Eglov Isl., Khvost Isl., Nizhneje Myagrozero, Podyelniki, Rogachev Isl. Mycetochara lavipes (Fabricius) – Kizhi Isl., Rogachev Isl. *Tenebrio molitor L. – Unitsa (Poppius 1899) *Uloma culinaris (L.) – Unitsa (Poppius 1899) Oedemeridae Chrysanthia geniculata Heyden – Nizhneje Myagrozero, Verkhnee Myagrozero Chrysanthia viridissima (L.) – Kosmozero, Tolvuya (Poppius 1899), Bol. Klim.Isl. Oedemera virescens L. – Rogachev Isl. Tetratomidae Tetratoma ancora (Fabricius) – Bol. Klim. Isl. Hallomenus binotatus (Quensel) – Bol. Klim. Isl. 288 Reports of the Finnish Environment Institute 40 | 2014 Melandryidae Melandrya dubia Schall. – Bol. Klim. Isl. Orchesia fasciata (Illiger) – Bol. Klim. Isl., Podyelniki Orchesia micans (Panzer) – Bol. Klim.Isl., Volkostrov Isl. Phryganophilus ruicollis (Fabricius) – Bol. Klim. Isl. Xylita laevigata (Hellenius) – Bol. Klim. Isl. Pythidae Pytho depressus (L.) – Bol. Klim. Isl., Velikaya Guba (Poppius 1899), Kosmozero, Uzkaya Salma Pytho kolwensis Sahlberg – Lipovitsy, Polya, Tambitsy Pyrochroidae Schizotus pectinicornis (L.) – Zaonezhye (Poppius 1899), Bol. Klim. Isl. Anthicidae Latreille, 1819 *Notoxus monoceros (L.) – Tolvuya (Poppius 1899) Scraptiidae Anaspis arctica Zetterstedt – Dianova Gora, Kosmozero, Unitsa (Poppius 1899), Bol. Klim. Isl., Volkostrov Isl. *Anaspis frontalis (L.) – Kizhi Isl., Kosmozero, Oleny Isl., Shun’ga, Velikaya Guba (Poppius 1899) Anaspis marginicollis Lindberg – Bol. Klim. Isl. Salpingidae *Salpingus planirostris (Fabricius) – Shun’ga (Poppius 1899), Kizhi Isl. Salpingus ruicollis L. – Zaonezhye *Sphaeriestes stockmanni (Biström) – Kizhi Isl. (Poppius 1899) CHRYSOMELOIDEA Cerambycidae *Acmaeops pratensis (Laicharting) – Kizhi Isl. (Poppius 1899) Aegomorphus clavipes (Schrank) – Kosmozero (Poppius 1899), Bol. Klim. Isl., Verkhnee Myagrozero Agapanthia villosoviridescens DeGeer – Rogachev Isl. Alosterna tabacicolor DeGeer – Kosmozero (Poppius 1899), Bol. Klim. Isl., Kizhi Isl., Eglov Isl., Klimenicy, Lipovitsy, Rogachev Isl., Uzkaya Salma, Vikshezero Anoplodera livida (Fabricius) – Podyelniki, Vorobyi Anoplodera maculicornis (L.) – Vorobyi, Podyelniki, Vegoruksy, Polya, Eglov Isl., Kizhi Isl., Nizhneje Myagrozero, Rogachev Isl., Shunevskiy Isl. Anoplodera reyi (Heyden) – Podyelniki, Kuzaranda, Eglov Isl., Kainos Isl., Nizhneje Myagrozero, Polya, Turastamozero, Uzkaya Salma, Vegoruksy, Verkhnee Myagrozero Anoplodera sanguinolenta L. – Podyelniki, Nizhneje Myagrozero, Oyatevschina, Vikshezero Anoplodera virens L. – Kuzaranda (Poppius 1899), Kosmozero, Bol. Klim.Isl., Kizhi Isl., Podyelniki, Nizhneje Myagrozero, Volkostrov Isl. *Arhopalus rusticus (L.) – Kizhi Isl., Velikaya Guba (Poppius 1899) Aromia moschata (L.) – Bol. Klim. Isl. Brachyta interrogationis (L.) – Kizhi Isl., Velikaya Guba (Poppius 1899), Tipinitsy, Bol. Klim.Isl. Callidium coriaceum Paykull – Velikaya Guba (Poppius 1899), Bol. Klim. Isl., Lipovitsy, Vikshezero Callidium violaceum (L.) – Kizhi Isl. Gaurotes virginea L. –Velikaya Guba (Poppius 1899), Lipovitsy, Vegoruksy, Uzkaya Salma, Tipinitsy, Vikshezero Judolia sexmaculata L. – Kuzaranda (Poppius 1899), Bol. Klim. Isl., Turastamozero Reports of the Finnish Environment Institute 40 | 2014 289 Leiopus punctulatus (Paykull) – Polya Leptura melanura L. – Kizhi Isl., Bol. Klim.Isl., Kosmozero, Eglov Isl., Nizhneje Myagrozero, Rogachev Isl., Vorobyi Leptura nigripes (DeGeer) – Velikaya Guba (Poppius 1899), Podyelniki, Oyatevschina, Turastamozero, Vegoruksy Leptura pubescens Fabricius – Turastamozero Leptura quadrifasciata L. – Kosmozero (Poppius 1899), Kizhi Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Turastamozero, Vorobyi *Molorchus minor (L.) – Kizhi Isl. (Poppius 1899) Monochamus galloprovincialis Olivier – Tolvuya (Poppius 1899), Podyelniki, Nizhneje Myagrozero Monochamus sutor L. Turastamozero, Nizhneje Myagrozero Monochamus urussovi Fischer von Waldheim – Turastamozero, Nizhneje Myagrozero, Oyatevschina Necydalis major L. – Kosmozero, Kurgenitsy Nivellia sanguinosa (Gyllenhal) – Oyatevschina, Vikshezero Pachyta quadrimaculata L. – Kosmozero, Nizhneje Myagrozero, Podyelniki Pedostrangalia pubescens (Fabricius) – Turastamozero. Phytoecia cylindrica (L.) – Vegoruksy, Bol. Klim. Isl. Pogonocherus fasciculatus (DeGeer) – Bol. Klim. Isl. Rhagium inquisitor L. – Lipovitsy Rhagium mordax Deg. – Bol. Klim. Isl., Kazhma, Volkostrov Isl. Saperda carcharias (L.) – Bol. Klim. Isl. Saperda perforata Pallas – Verkhnee Myagrozero * Saperda scalaris (L.) – Kizhi Isl. (Poppius 1899) Tetropium castaneum (L.) – Lipovitsy Tetrops praeusta (L.) – Tolvuya (Poppius 1899), Rogachev Isl. Xylotrechus rusticus (L.) – Bol. Klim.Isl., Turastamozero, Nizhneje Myagrozero Chrysomelidae *Altica oleracea (L.) – Tolvuya (Poppius 1899) *Aphthona erichsoni (Zetterstedt) – Unitsa (Poppius 1899) (Silfverberg 1987) Bromius obscurus L. – Podyelniki, Eglov Isl., Khvost Isl., Kizhi Isl., Nizhneje Myagrozero, Oyatevschina, Rogachev Isl., Tipinitsy, Vegoruksy, Vikshezero *Bruchus atomarius L. – Bol. Klim.Isl., Kosmozero (Poppius 1899) *Cassida denticollis Suffrian – Kizhi Isl., Oleny Isl. (Poppius 1899) *Cassida nebulosa L. – Shun’ga (Poppius 1899) *Cassida rubiginosa Müller – Shun’ga (Poppius 1899) *Cassida sanguinosa Suffrian – Kosmozero, Tolvuya (Poppius 1899) Cassida viridis L. – Verkhnee Myagrozero *Chaetocnema aerosa (Letzner) – Shun’ga (Poppius 1899) *Chaetocnema aridula (Gyllenhal, 1827) – Kuzaranda (Poppius 1899) polita (L.) – Tolvuya (Poppius 1899), Eglov Isl. *Chrysolina hyperici (Forster) – Kizhi Isl. (Poppius 1899) Chrysolina varians (Schaller) – Podyelniki, Nizhneje Myagrozero, Verkhnee Myagrozero, Vikshezero Chrysomela collaris L. – Kosmozero, Tolvuya (Poppius 1899), Uzkaya Salma Chrysomela cuprea Fabricius – Kizhi Isl. (Poppius 1899), Vorobyi Chrysomela lapponica L. – Oleny Isl. (Poppius 1899), Tipinitsy, Turastamozero, Uzkaya Salma, Verkhnee Myagrozero Clytra quadripunctata L. – Eglov Isl. Crepidodera fulvicornis Fabricius – Tipinitsy 290 Reports of the Finnish Environment Institute 40 | 2014 Cryptocephalus aureolus Suffrian – Vikshezero, Vorobyi, Zaonezhye (Silfverberg 1987) *Cryptocephalus bipunctatus (L.) – Kosmozero (Poppius 1899), Zaonezhye (Silfverberg 1987) *Cryptocephalus cordiger (L.) – Kizhi Isl. (Poppius 1899), Zaonezhye (Silfverberg 1987) Cryptocephalus coryli L. – Rogachev Isl. *Cryptocephalus distinguendus Schneider – Bol. Klim. Isl., Kizhi Isl. (Poppius 1899), Zaonezhye Chrysolina *Cryptocephalus exiguus Schneider – Kosmozero, Shun’ga , Velikaya Guba (Poppius 1899), Zaonezhye (Silfverberg 1987) *Cryptocephalus labiatus (L.) – Kizhi Isl., Tolvuya, Shun’ga (Poppius 1899), Zaonezhye (Silfverberg 1987) Cryptocephalus moraei (L.) – Zaonezhye (Silfverberg 1987) *Cryptocephalus nitidulus Fabricius – Kizhi Isl. (Poppius 1899), Zaonezhye (Silfverberg 1987) *Cryptocephalus octopunctatus (Scopoli) – Kizhi Isl. (Poppius 1899), Zaonezhye (Silfverberg 1987) Cryptocephalus pini (L.) – Zaonezhye (Silfverberg 1987) Cryptocephalus sericeus (L.) – Kizhi Isl. (Poppius 1899), Bol. Klim. Isl., Oyatevschina, Turastamozero, Vikshezero *Cryptocephalus sexpunctatus (L.) – Velikaya Guba (Poppius 1899), Zaonezhye (Silfverberg 1987) *Derocrepis ruipes (L.) – Kuzaranda (Poppius 1899) Donacia clavipes Fabricius – Podyelniki, Oyatevschina Donacia crassipes Fabricius –Kosmozero (Poppius 1899), Zaonezhye (Silfverberg 1987), Eglov Isl. Donacia impressa Paykull – Zaonezhye (Silfverberg 1987) Donacia obscura Gyllenhal – Dianova Gora (Poppius 1899), Zaonezhye (Silfverberg 1987) Donacia thalassina Germar – Zaonezhye (Silfverberg 1987) Donacia vulgaris Zschach – Velikaya Guba (Poppius 1899), Zaonezhye (Silfverberg 1987) Galeruca tanaceti L. – Eglov Isl., Podyelniki, Nizhnee Myagrozero Galerucella calmariensis L. – Kizhi Isl., Uzkaya Salma Galerucella grisescens Joannis – Vorobyi Galerucella lineola Fabricius – Kizhi Isl. Galerucella nymphaeae L. – Vorobyi, Eglov Isl., Khvost Isl., Rogachev Isl., Verkhnee Myagrozero, Vorobyi *Galerucella sagittariae (Gyllenhal) – Unitsa (Poppius 1899) *Gastrophysa polygoni (L.) – Shun’ga (Poppius 1899) *Gonioctena lavicornis (Suffrian) – Oleny Isl. (Poppius 1899) *Gonioctena pallida (L.) – Bol. Klim.Isl. (Poppius 1899) Gonioctena quinquepunctata F. – Podyelniki, Verkhnee Myagrozero Gonioctena viminalis (L. – Kizhi Isl., Shun’ga (Poppius 1899), Bol. Klim. Isl., Turastamozero *Hippuriphila modeeri (L.) – Kuzaranda, Unitsa (Poppius 1899) *Hydrothassa hannoveriana (Fabricius) – Velikaya Guba (Poppius 1899) Hydrothassa marginella L. – Podyelniki, Oyatevschina *Lema cyanella (L.) – Shun’ga (Poppius 1899), Zaonezhye (Silfverberg 1987) Lilioceris merdigera (L.) – Oyatevschina, Tambitsy Lochmaea caprea L. – Rogachev Isl., Tipinitsy *Lochmaea suturalis (Thomson) – Kizhi Isl. (Poppius 1899), Tipinitsy *Longitarsus holsaticus (L.) – Kosmozero, Unitsa (Poppius 1899) Reports of the Finnish Environment Institute 40 | 2014 291 *Longitarsus lycopi (Foudras) – Tolvuya (Poppius 1899) *Longitarsus pratensis (Panzer) (as L. pusillus Gyllenhal) – Shun’ga, Unitsa (Poppius 1899) *Lythraria salicariae (Paykull) – Kizhi Isl. (Poppius 1899) Neocrepidodera femorata (Gyllenhal) – Velikaya Guba (Poppius 1899), Tambitsy *Oulema erichsonii (Suffrian) – Kosmozero (Poppius 1899), Zaonezhye (Silfverberg 1987) *Oulema gallaeciana (Heyden – Shun’ga , Tolvuya (Poppius 1899), Zaonezhye (Silfverberg 1987) *Phaedon cochleariae (Fabricius) (as Hydrothassa egena (Gyllenhal) – Kizhi Isl., Oleny Isl. (Poppius 1899) Phratora atrovirens Cornelius – Vikshezero *Phratora vitellinae (L.) – Zaonezhye (Poppius 1899) Phyllobrotica quadrimaculata L. – Podyelniki Phyllotreta nemorum (L.) – Tolvuya (Poppius 1899) *Plagiodera versicolora (Laicharting) – Oleny Isl. (Poppius 1899) Plagiosterna aenea (L.) – Uzkaya Salma, Tambitsy Plateumaris afinis (Kunze) – Rogachev Isl., Zaonezhye (Silfverberg 1987) Plateumaris discolor – Zaonezhye (Silfverberg 1987) *Plateumaris rustica (Kunze) – Velikaya Guba (Poppius 1899) *Plateumaris sericea (L.) – Kizhi Isl., Velikaya Guba (Poppius 1899), Zaonezhye (Silfverberg 1987) *Psylliodes cucullata (Illiger) – Shun’ga , Tolvuya, Unitsa (Poppius 1899) *Psylliodes napi (Fabricius) – Shun’ga (Poppius 1899) Pyrrhalta viburni Paykull – Tipinitsy Smaragdina afinis (Illiger) – Zaonezhye (Silfverberg 1987) *Smaragdina aurita (L.) – Kizhi Isl., Tolvuya (Poppius 1899) Smaragdina lavicollis Charp. – Podyelniki *Smaragdina salicina (Scopoli) – Kosmozero (Poppius 1899) Anthribidae Dissoleucas niveirostris Fabricius – Turastamozero Platystomos albinus L. – Bol. Klim.Isl., Kizhi Isl. (Poppius 1899), Verkhnee Myagrozero Atellabidae Apoderus coryli (L.) – Kizhi Isl., Kuzaranda (Poppius 1899), Uzkaya Salma *Byctiscus betulae (L.) – Kizhi (Poppius 1899) Byctiscus populi L. – Velikaya Guba (Poppius 1899), Vikshezero Deporaus betulae L. – Kosmozero (Poppius 1899), Khvost Isl. Curculionidae *Amycterus marshami (Schönherr) – Shun’ga, Tolvuya (Poppius 1899) *Apion apricans Herbst – Kizhi Isl. (Poppius 1899) Apion cerdo Gerstaecker Bol. Klim. Isl., Kizhi Isl., Kosmozero, Shun’ga (Poppius 1899), Eglov Isl. *Apion ervi Kirby – Unitsa (Poppius 1899) *Apion frumentarium (L.) – Kizhi Isl. (Poppius 1899) *Apion gyllenhali Kirby– Kizhi Isl., Shun’ga (Poppius 1899) ? Apion opeticum Bach – Tipinitsy *Apion viciae (Paykull) – Shun’ga (Poppius 1899) *Apion violaceum Kirby – Kosmozero, Shun’ga , Tolvuya (Poppius 1899) *Apion virens Herbst – Kosmozero, Shun’ga , Tolvuya, Velikaya Guba (Poppius 1899) Auleutes epilobii (Paykull) – Kuzaranda (Poppius 1899), Tipinitsy *Bagous lutulentus (Gyllenhal) – Velikaya Guba (Poppius 1899) *Brachysomus echinatus (Bonsdorff) – Kizhi Isl. (Poppius 1899) 292 Reports of the Finnish Environment Institute 40 | 2014 *Ceutorhynchus rugulosus (Herbst) – Shun’ga, Unitsa (Poppius 1899) *Ceutorhynchus typhae (Herbst – Shun’ga (Poppius 1899) *Cionus tuberculosus (Scopoli) (as C. verbasci Fabricius) – Kizhi Isl. (Poppius 1899) Cleopomiarus distinctus Boheman – Rogachev Isl. Cryphalus saltuarius Weise – Bol. Klim. Isl. Cryptorhynchus lapathi L. – Khvost Isl. *Dorytomus minutus (Gyllenhal) – Kizhi Isl. (Poppius 1899) Dryocoetes alni (Georg) – Bol. Klim.Isl., Volkostrov Isl. *Eutrichapion facetum (Gyllenhal) (as Apion sundevallii Boheman) – Bol. Klim. Isl., Shun’ga, Unitsa *Grypus equiseti (Fabricius) – Shun’ga (Poppius 1899) *Hylastes angustatus (Herbst) – Kosmozero (Poppius 1899) Hylastes cunicularius Erichsen – Bol. Klim. Isl. Hylobius abietis (L.) Bol. Klim.Isl., Vegoruksy, Uzkaya Salma, Eglov Isl. Hylobius pinastri Gyllenhal – Lipovitsy, Tipinitsy Hylurgops palliatus (Gyllenhal) – Kosmozero, Velikaya Guba (Poppius 1899), Bol. Klim. Isl., Uzkaya Salma, Vegoruksy *Hypera arator (L.) (as H. polygoni L.) – Oleny Isl., Shun’ga (Poppius 1899) *Hypera nigrirostris (Fabricius) – Kosmozero, Shun’ga, Tolvuya (Poppius 1899) Hypera rumicis (L.) – Tolvuya (Poppius 1899), Verkhnee Myagrozero *Hypera suspiciosa (Herbst) – Kizhi Isl., Oleny Isl., Shun’ga, Unitsa (Poppius 1899) *Ips sexdentatus (Börner) – Kosmozero (Poppius 1899) Ips typographus (L.) – Kosmozero, velikaya Guba (Poppius 1899), Bol. Klim. Isl., Lipovitsy, Polya, Uzkaya Salma, Vegoruksy Limnobaris dolorosa Goeze – Eglov Isl., Khvost Isl. ?Limobius borealis (Paykull) – (as Hypera dissimilis Herbst – Oleny Isl., Shun’ga (Poppius 1899)) *Magdalis carbonarius (L.) – Kizhi Isl. (Poppius 1899) *Magdalis frontalis (Gyllenhal) – Velikaya Guba (Poppius 1899) *Magdalis ruicornis (L.)(as M. pruni L.) – Bol. Klim. Isl., Oleny Isl. (Poppius 1899) *Magdalis violacea (L.) – Kizhi Isl. (Poppius 1899) *Miarus campanulae (L.) – Tolvuya (Poppius 1899) *Orthotomicus laricis (Fabricius) – Kosmozero (Poppius 1899) Otiorhynchus ovatus (L.) – Kosmozero, Shun’ga, Tolvuya (Poppius 1899), Kizhi Isl. Otiorhynchus scaber (L.) – Kizhi Isl. (Poppius 1899), Tipinitsy, Vorobyi *Pelenomus comari (Herbst) – Zaonezhye (Poppius 1899) Phloeotribus spinulosus (Rey) – Kurgenitsy Phyllobius arborator Herbst – Kizhi Isl. Phyllobius maculicornis Germar – Kosmozero (Poppius 1899), Kizhi Isl., Rogachev Isl. *Phyllobius pomaceus Gyllenhal – Tolvuya (Poppius 1899) Pissodes pini L. – Eglov Isl. Pityogenes chalcographus L. – Kizhi *Polydrusus cervinus (L.) – Kizhi Isl., Oleny Isl. (Poppius 1899) Polydrusus fulvicornis (Fabricius) – Shun’ga (Poppius 1899), Eglov Isl., Podyelniki, Rogachev Isl., Turastamozero *Polydrusus micans (Fabricius) – Kizhi Isl., Velikaya Guba (Poppius 1899 Polygraphus poligraphus (L.) – Kosmozero (Poppius 1899), Bol. Klim. Isl. *Rhinoncus castor (Fabricius) – Kizhi Isl. (Poppius 1899) *Rhynchites cupreus (L.) – Kosmozero (Poppius 1899) Scolytus ratzeburgi Janson – Bol. Klim. Isl., Volkostrov Isl. ? *Scolytus scolytus (Fabricius) (as S. destructor Olivier) – Velikaya Guba (Poppius 1899) *Sitona lineatus (L.) – Kizhi Isl., Shun’ga (Poppius 1899 Reports of the Finnish Environment Institute 40 | 2014 293 Strophosoma capitatum DeGeer – Eglov Isl., Khvost Isl., Tipinitsy *Taeniapion urticarium (Herbst ) (as Apion vernale Fabricius) – Shun’ga (Poppius 1899) *Tachyerges stigma (Germar) – Kosmozero (Poppius 1899) *Tanymecus palliatus (Fabricius) – Kosmozero, Tolvuya (Poppius 1899) *Temnocerus nanus (Paykull) – Kizhi Isl. (Poppius 1899) *Tomicus minor (Hartig) – Bol. Klim.Isl., Kosmozero, Vegoruksy, Uzkaya Salma Tomicus piniperda (L.) –Velikaya Guba (Poppius 1899), Kosmozero, Bol. Klim. Isl., Uzkaya Salma, Vegoruksy Trypodendron lineatum Olivier – Bol. Klim. Isl., Volkostrov Isl. Trypodendron signatum (Fabricius) – Bol. Klim.Isl., Volkostrov Isl. *Tychius quinquepunctatus (L.) – Oleny Isl. (Poppius 1899) Xyleborus cryptographus (Ratz.) – Bol. Lelikovskiy Isl. Xylechinus pilosus (Ratz.) – Kurgenitsy LEPIDOPTERA Hepialidae Hepialis humuli L. – Vegoruksy. Phymatopus hecta L. – Nizhneje Myagrozero Pharmacis fusconebulosa Deg. – Nizhneje Myagrozero Adelidae Nemophora amatella Staudinger – Vikshezero Nemophora degeerella L. – Eglov Isl., Khvost Isl. Tineidae Scardia boletella Fabricius – Oyatevschina Yponomeutidae Yponomeuta evonymellus L. – Eglov Isl., Rogachev Isl. Argyresthia sorbiella (Treitschke) – Vegoruksy Plutellidae Plutella xylostella (L.) – Vegoruksy Coleophoridae Coleophora deauratella Lienig & Zeller – Vegoruksy Choreutidae Anthophila fabriciana L. – Vorobyi Gelechiididae Metzneria aprilella (Herr.-Schäff.) – Vegoruksy Helcystogramma rufescens (Haworth) – Vegoruksy Acompsia cinerella (Clerck) – Vegoruksy Cossidae Cossus cossus L. – Bol. Klim. Isl., Kazhma, Kosmozero Tortricidae Celypha lacunana Den. & Schiff. – Eglov Isl., Khvost Isl., Rogachev Isl., Vegoruksy Olethreutes arcuella – Eglov Isl., Khvost Isl., Rogachev Isl. Epinotia trigonella (L.) – Vegoruksy Thiodia citrana (Hbn.) – Vegoruksy Eucosma cana (Haworth) – Vegoruksy Lathronympha strigana (F.) – Eglov Isl., Vegoruksy Clepsis rogana – Khvost Isl., Rogachev Isl. Phiaris umbrosana – Rogachev Isl. Eana argentana – Rogachev Isl. Aphelia unitana Hübner – Kizhi Isl., Rogachev Isl. Dichrorampha petiverella L. – Rogachev Isl. Epermeniidae Epermenia illigerella Hb. – Khvost Isl. 294 Reports of the Finnish Environment Institute 40 | 2014 Pterophoridae Hellinsia didactylites (Ström) – Vegoruksy Hellinsia osteodactylus (Zeller) – Vegoruksy Gillmeria pallidactyla (Haworth) – Rogachev Isl. Pyralidae Eurrhypara hortulata L. – Rogachev Isl. Evergestis pallidata Hufn. – Kizhi Isl. ? Udea lutealis Hübner – Nizhneje Myagrozero Udea hamalis Thunb. – Lipovitsy Nymphula nitidulata Hufnagel – Podyelniki, Verkhnee Myagrozero Crambidae Crambus lathoniellus (Zincken) – Vegoruksy Chrysoteuchia culmella L. – Eglov Isl., Khvost Isl., Zygaenidae Adscita statices L. – Kizhi Isl., Vikshezero, Rogachev Isl. Zygaena lonicera Scheven – B. Klimenetsky Isl., Podyelniki, Rechnoi Isl. Zygaena osterodensis Reiss – B. Klimenetsky Isl., Podyelniki, Eglov Isl., Khvost Isl., Rogachev Isl. Zygaena viciae Scheven – Podyelniki Hesperidae Pyrgus alveus Hb. – Isl. B. Klimenetsky, Eglov Isl., Kosmozero (Kaisila 1947), Sennaya Guba, Shun‘ga (Kaisila 1947) Pyrgus malvae L. – Bol. Klim. Isl., Sennaya Guba, Sennaya Guba Carterocephalus palaemon Pallas – Bol. Klim. Isl., Eglov Isl.,Velikaya Guba (Kaisila 1947). Carterocephalus silvicola Mg. – Bol. Klim. Isl., Kizhi Isl. (Kaisila 1947), Sennaya Guba, Velikaya Guba (Kaisila 1947), Volkostrov Isl., Oyatevschina Thymelicus lineola Ochs. – Bol. Klim. Isl., Myagrozero, Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Sennaya Guba, Shun‘ga, Turastamozero, Verkhnee Myagrozero, Vorobyi Hesperia comma L. – Shun’ga (Kaisila 1947), Vorobyi Ochlodes sylvanus Esper – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kizhi Isl., Lelikovo, Myagrozero, Rogachev Isl., Sennaya Guba, Turastamozero, Uzkaya Salma, Vegoruksy Pieridae Leptidea sinapis L. – Kizhi Isl., Bol. Klim. Isl., Oyatevschina, Eglov Isl. , Sennaya Guba, Kosmozero Aporia crataegi L. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kizhi Isl., , Kuzaranda, Nizhneje Myagrozero, Oyatevschina, Isl. Rechnoi, Rogachev Isl., Sennaya Guba, Vorobyi. Pieris brassicae L. – Bol. Klim. Isl., Kizhi Isl. Pieris napi L. – Bol. Klim. Isl., Kizhi Isl., Lelikovo, Kosmozero, Sennaya Guba, Oyatevschina Pieris rapae L. – Bol. Klim. Isl., Oyatevschina, Sennaya Guba Pontia edusa F.– Kizhi Isl., Kurgenitsy Anthocharis cardamines L. – Bol. Klim. Isl., Eglov Isl., Kizhi Isl., Sennaya Guba, Uzkaya Salma, Oyatevschina, Gonepteryx rhamni L. –Bol. Klim. Isl., B.Lelikoskiy Isl., Kizhi Isl., Kosmozero, Lelikovo, Podyelniki, Sennaya Guba, Tambitsy, Verkhnee Myagrozero, Vorobyi Colias palaeno L. – Sennaya Guba, Turastamozero Papilionidae Papilio machaon L. – Bol. Klim. Isl., Kizhi Isl., Oyatevschina, Podyelniki, Sennaya Guba, Turastamozero, Vorobyi Parnassius mnemosyne (L.) – Kizhi Isl., Sennaya Guba, Shunevskiy Isl., Velikaya Niva, Volkostrov Isl., Vorobyi Reports of the Finnish Environment Institute 40 | 2014 295 Lycaenidae Lycaena virgaureae L. – Kizhi Isl., Bol. Klim. Isl., Kosmozero, Lelikovo, Nizhneye Myagrozero, Oyatevschina, Podyelniki, Sennaya Guba, Turastamozero, Vorobyi Lycaena hippothoe L. – Bol. Klim. Isl., Eglov Isl., Rogachev Isl., Sennaya Guba, Tolvuya (Kaisila 1947) Lycaena dispar Haworth – Lelikovo (Juho Paukkunen pers. comm.) Celastrina argiolus L. – Bol. Klim. Isl., Eglov Isl., Nizhneye Myagrozero, Sennaya Guba Glaucopsyche alexis Poda – Bol. Klim. Isl., Sennaya Guba Aricia artaxerxes F. – Bol. Klim. Isl., Sennaya Guba Aricia eumedon Esper – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Rogachev Isl., Sennaya Guba *Aricia nicias Meigen – Kosmozero (Kaisila 1947) Plebeius optilete Knoch – Podyelniki, Turastamozero Plebeius argus L. – Nizhneye Myagrozero, Sennaya Guba, Turastamozero Polyommatus amandus Schneider – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kuzaranda, Nizhneje Myagrozero, Podyelniki, Rechnoi Isl., Rogachev Isl., Sennaya Guba, Turastamozero Polyommatus icarus Rott. – Bol. Klim. Isl., Lelikovo, Sennaya Guba Polyommatus semiargus Rott. – Bol. Klim. Isl., Kizhi Isl., Nizhneye Myagrozero, Rogachev Isl., Sennaya Guba, Turastamozero, Isl. Volkostrov Callophrys rubi L. – Bol. Klim. Isl., Sennaya Guba Thecla betulae (L.) –Nikonova Guba Satyrium pruni L. – Bol. Klim. Isl., Eglov Isl., Kosmozero (Kaisila 1947), Tolvuya (Kaisila 1947), Velikaya Niva (Kaisila 1947), Uzkaya Salma Nymphalidae Aglais urticae L. – Bol. Klim. Isl., Kizhi Isl., Kosmozero, Lelikovo, Nizhneje Myagrozero, Podyelniki, Isl. Rechnoi, Sennaya Guba, Tambitsy, Turastamozero. Vanessa atalanta L. – Bol. Klim. Isl., Kosmozero, Lelikovo, Polya, Sennaya Guba, Vegoruksy Vanessa cardui L.– Bol. Klim. Isl., Sennaya Guba Nymphalis antiopa L.– Bol. Klim. Isl., B.Lelikoskiy Isl., Kosmozero, Oyatevschina, Sennaya Guba, Turastamozero Polygonia c-album L. – Bol. Klim. Isl., Kazhma, Kizhi Isl., Kosmozero, Kuzaranda, Podyelniki, Isl. Rechnoi, Sennaya Guba, Tambitsy, Turastamozero, Vorobyi Inachis io L.– Bol. Klim. Isl., B.Lelikoskiy Isl., Sennaya Guba, Turastamozero Araschnia levana L. – Bol. Klim. Isl., Eglov Isl., Kizhi Isl., Kosmozero, Lelikovo, Podyelniki, Sennaya Guba., Oyatevschina Limenitis populi L. – Bol. Klim. Isl., Oyatevschina, Sennaya Guba, Turastamozero Euphydryas maturna L. – Bol. Klim. Isl., Kizhi Isl., Sennaya Guba Argynnis niobe L. – Kosmozero, Tolvuya (Kaisila 1947) Argynnis adippe Den. & Schiff. – Bol. Klim. Isl., Kosmozero, Sennaya Guba, Tolvuya Argynnis aglaja L. – Bol. Klim. Isl., Kizhi Isl., Nizhneje Myagrozero, Podyelniki, Sennaya Guba, Turastamozero, Verkhnee Myagrozero, Vikshezero Argynnis paphia L. – Bol. Klim. Isl., Kosmozero, Myagrozero, Nizhneje Myagrozero, Podyelniki, Turastamozero, Vegoruksy, Verkhnee Myagrozero, Shun’ga Brenthis ino Rott. – Bol. Klim. Isl., Eglov Isl., Kizhi Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Sennaya Guba, Turastamozero Melitaea athalia Rott. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kizhi Isl., Rogachev Isl., Sennaya Guba, Turastamozero Boloria euphrosyne L. – Bol. Klim. Isl. Boloria selene Den. & Schiff. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kosmozero, Kuzaranda, Lelikovo, Podyelniki, Rogachev Isl., Sennaya Guba, Tipinitsy, Turastamozero, Volkostrov Isl., Oyatevschina. 296 Reports of the Finnish Environment Institute 40 | 2014 *Boloria titania Esper – Shun’ga, Vegoruksy (Kaisila 1947) Boloria aquilonaris Stich. – Tolvuya (Kaisila 1947), Uzkaya Salma Pararge aegeria L. –Bol. Klim. Isl., Boyarschina, Sennaya Guba Aphantopus hyperantus L. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kuzaranda, Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Sennaya Guba, Shun’ga, Turastamozero, Vegoruksy Coenonympha glycerion Borkh. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kuzaranda, Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Sennaya Guba, Turastamozero, Vegoruksy Maniola jurtina L. – Bol. Klim. Isl., Sennaya Guba, Turastamozero, Vegoruksy *Oenis jutta Hübner – Kizhi Isl., Velikaya Guba (Kaisila 1947) *Hyponephele lycaon Kühn – Shun’ga (Kaisila 1947) Lasiommata maera L. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kuzaranda, Rogachev Isl., Sennaya Guba, Turastamozero Lasiommata petropolitana F. – Bol. Klim. Isl. *Erebia euryale Esper. – Lizhma (Kaisila 1947) Erebia ligea L. – Bol. Klim. Isl., Kosmozero, Oyatevschina, Turastamozero Geometridae *Baptria tibiale borealis Lankeila – Bol. Klim. Isl., Kizhi Isl. (Kaisila 1947) Abraxas sylvatus Scop. – Oyatevschina, Sennaya Guba, Volkostrov Isl. Antonechloris smaragdaria F. – Rogachev Isl. Thetidia smaragdaria (F.) – Rogachev Isl. Cabera pusaria L. – Vegoruksy Macaria alternata Den. & Schiff. – Rogachev Isl. Plemyria rubiginata (Den. & Schiff.) – Vorobyi Geometra papilionaria L. – Bol. Klim. Isl., Kosmozero. Scotopteryx chenopodiata L. – Kizhi Isl., Podyelniki, Turastamozero Dysstroma citrata (L.) – Oyatevschina, Kizhi Isl., Lelikovo, Vegoruksy Eulithis populata L. – Oyatevschina *Apeira syringaria L. – Kosmozero (Kaisila 1947) *Arichanna melanaria L. – Tolvuya (Kaisila 1947) *Anticollix sparsatus Treitschke – Tolvuya (Kaisila 1947) *Catarhoe cuculata Hufn. – Kosmozero, Velikaya Guba (Kaisila 1947) *Electrophaes corylata Thunb. – Kizhi Isl., Velikaya Guba (Kaisila 1947) *Spargania luctuata (Den. & Schiff.) – Bol. Klim. Isl., Kizhi Isl., Kuzaranda, Velikaya Guba (Kaisila 1947) *Antyclea derivata (Den. & Schiff.) – Velikaya Guba (Kaisila 1947) *Colostygia aptata Hbn. – Kizhi Isl., Kosmozero (Kaisila 1947) Hydriomena furcata Thunb. – Oyatevschina. Plemyria rubiginata Den. & Schiff. – Vorobyi Perizoma alchemillatum L. – Kizhi Isl. Perizoma didymatum L. – Oyatevschina Perizoma lavofasciata Thunb. – Khvost Isl. Odezia atrata L. – Eglov Isl., Khvost Isl., Polya, Rogachev Isl. Siona lineata Scop. – Eglov Isl., Khvost Isl., Rogachev Isl., Vegoruksy Itame brunneatum Thunb. – Oyatevschina Pseudopanthera macularia L. – Bol. Klim. Isl. Epirrhoe alternata (Müller) – Lelikovo, Sennaya Guba, Vorobyi Epirrhoe tartuensis Möls – Khvost Isl. Epirrhoe tristata L. – Rogachev Isl. Xanthorhoe montanata (Den. & Schiff.) – Rogachev Isl., Vegoruksy Scopula loslactata Haworth – Vegoruksy Reports of the Finnish Environment Institute 40 | 2014 297 Scopula immorata L. – Khvost Isl., Vegoruksy Scopula immutata L. – Khvost Isl. Idaea aversata L. – Vegoruksy Timandra griseata W. Petersen – Khvost Isl., Rogachev Isl., Vegoruksy Angerona prunaria (L.) – Rogachev Isl., Vegoruksy Chiasmia clathrata L. – Eglov Isl., Khvost Isl. Cosmorhoe ocellata L. – Khvost Isl. Crocallis elinguaria L. – Kizhi Isl. Chloroclysta citrata L. – Kizhi Isl. Sphingidae Hemaris tityus L. – Kizhi Isl. (Kaisila 1947), Vorobyi *Hemaris fuciformis L. – Kuzaranda (Kaisila 1947) Deilephila elpenor (L.) – Turastamozero, Velikaya Niva, Vorobyi *Deilephila porcellus L. – Kizhi Isl. (Kaisila 1947) *Smerinthus ocellatus L. – Kizhi Isl., Kosmozero (Kaisila 1947) Hyles gallii Rtmbrg – Velikaya Niva, Kazhma, Nizhnee Myagrozero, Kazhma. Lasiocampidae Gastropacha quercifolia L. – Vegoruksy Euthrix potatoria L. – Eglov Isl., Kizhi Isl., Tambitsy, Vegoruksy, Shunevsky Isl. Lasiocampa quercus L. – Shunevsky Isl. Notodontidae *Pterostoma palpinum Clerck – Bol. Klim. Isl., Kizhi Isl., Velikaya Guba (Kaisila 1947) Clostera anastomosis (L.) – Vegoruksy Ptilodon capucina L. – Tipinitsy Lymantriidae Orgyia antiqua L. – Zaonezhye Calliteara pudibunda (L.) – Turastamozero, Lambasruchey, Tambitsy Nolidae Nola aerugula Hübner – Vegoruksy Arctiidae *Thumatha senex (Hb.) –Tolvuya (Kaisila 1947) Eilema lurideolum (Zinck.) – Kizhi Isl. *Eilema lutarellum (L.) – Kosmozero (Kaisila 1947) *Eilema cereolum (Hb.) – Velikaya Niva (Kaisila 1947) Parasemia plantaginis (L.) – Zaonezhye Rhyparia purpurata (L.) – Eglov Isl., Isl., Kuzaranda, Paleostrov Isl., Rechnoi, Vegoruksy Cybosia mesomella (L.) – Eglov Isl., Rogachev Isl., Vegoruksy *Coscinia cribraria (L.) – Lizhma (Kaisila 1947) Diacrisia sannio (L.) – Eglov Isl., Rogachev Isl., Uzkaya Salma, Vegoruksy Spilosoma luteum (Hufnagel) – Khvost Isl., Oyatevschina Noctuidae Hypena proboscidalis L. – Kizhi Isl., Rogachev Isl. Euclidia glyphica L. – Eglov Isl., Oyatevschina Plusia putnami Grote – Kizhi Isl. Autographa excelsa Kretschmar – Kizhi Isl., Vorobyi *Autographa macrogamma Ev. – Kosmozero, Tolvuya (Kaisila 1947) Autographa bractea (Den. & Schiff.) – Vorobyi Acronicta rumicis L. – Vorobyi, Turastamozero Acronicta auricoma (Den. & Schiff.) – Podyelniki, Vorobyi Syngrapha interrogationis L. – Kizhi Isl. *Syngrapha microgamma Hbn. – Velikaya Guba, Velikaya Niva (Kaisila 1947) Abrostola triplasia L. – Kizhi Isl. 298 Reports of the Finnish Environment Institute 40 | 2014 Oligia strigilis L. – Kizhi Isl. Cerapteryx graminis L. – Kizhi Isl. Mythimna impura Hbn. – Kizhi Isl. Actinotia polyodon Cl. – Kizhi Isl. Phytometra viridaria Clerck – Kizhi Isl. (Kaisila 1947) Rivula sericealis Scop. – Khvost Isl., Kosmozero (Kaisila 1947), Vegoruksy, Velikaya Guba (Kaisila 1947) *Anarta myrtilli L. – Kizhi Isl. (Kaisila 1947) *Athetis pallustris Hbn. – Bol. Klim. Isl. (Kaisila 1947) *Platyperigea montana (Bremer) – Shun’ga (Kaisila 1947) *Cucullia gnaphalii Hbn. – Kosmozero (Kaisila 1947) *Cucullia umbratica L. – Kosmozero (Kaisila 1947) *Panemeria tenebrata Scop. – Zaonezhye (Kaisila 1947) *Hadena bicruris Hufnagel – Kosmozero (Kaisila 1947) *Papestra biren Goeze – Kosmozero (Kaisila 1947) *Discestra trifolii Hufnagel – Velikaya Guba (Kaisila 1947) *Mamestra brassicae L. – Kuzaranda (Kaisila 1947) *Spaelotis ravida (Den. & Schiff.) – Shun’ga (Kaisila 1947) Chersotis cuprea Den. & Schiff. – Vorobyi Xestia baja Den. & Schiff. – Nizhneje Myagrozero *Xestia c-nigrum L. – Kosmozero (Kaisila 1947) *Xestia cincera Herrich-Schaeffer – Velikaya Guba (Kaisila 1947) Xanthia icteritia Hufnagel – Turastamozero Polymixis gemmea Treitschke – Vegoruksy Hoplodrina blanda Den. & Schiff. – Vegoruksy Rusina ferruginea Esper – Vegoruksy Amphipoea crinanensis Burrows – Vegoruksy Lasionycta imbecilla (F.) – Nizhneje Myagrozero, Tolvuya (Kaisila 1947), Vegoruksy Helotropha leucostigma Hübner – Velikaya Niva Catocala fraxini – Lipovitsy, Polya, Vegoruksy Melanchra pisi (L.) – Vorobyi Melanchra persicariae L. – Tambitsy Staurophora celsia L. – Turastamozero,Vegoruksy Polypogon tentacularia L. – Khvost Isl., Rogachev Isl., Vegoruksy Protodeltote pygarga Hufnagel – Eglov Isl., Khvost Isl., Vegoruksy Deltote uncula Clerck – Eglov Isl. Allophyes oxyacanthae L. – Vegoruksy HYMENOPTERA Argidae Arge nigripes Retz. – Kurgenitsy, Turastamozero, Eglov Isl., Rogachev Isl., Sennaya Guba Arge pagana Pz. – Kurgenitsy, Podyelniki, Turastamozero, Nizhnee Myagrozero Arge ustulata L. – Vorobyi, Uzkaya Salma, Turastamozero, Nizhnee Myagrozero, Eglov Isl. Aprosthema hyalinopterum Conde – Sennaya Guba Pamphilidae Pamphilius hortorum Klug – Rogachev Isl. Cimbicidae Abia candens Konow – Velikaya Niva, Kosmozero (Kontuniemi 1965) Abia (Zaraea) fasciata L. – Kurgenitsy Reports of the Finnish Environment Institute 40 | 2014 299 Cimbex connata Schr. – Vorobyi Cimbex femorata L. – Vorobyi, Myagrozero, Nizhnee Myagrozero Cimbex lutea L. – Lydskoi Isl. Corynis obscura (F.) – Lelikovo, Sennaya Guba *Trichiosoma aenescens Guss. – Oyatevschina, Kizhi Isl. (Kontuniemi 1965) Trichiosoma sylvaticum Leach – Vorobyi Diprionidae *Monoctenus obscuratus Htg. – Podyelniki, Kizhi Isl. (Kontuniemi 1965) *Macrodiprion nemoralis Ensl. – Velikaya Guba (Kontuniemi 1965) Neodiprion sertifer Geoffr. – Vorobyi Tenthredinidae *Dolerus elderi Kincaid – Shun’ga (Kontuniemi 1965) *Brachythops lavens (Klug) – Kizhi Isl. (Kontuniemi 1965) *Brachythops wuestneii (Konow) – Kizhi Isl. (Kontuniemi 1965) *Heterarthrus nemoratus (Fallen) – Kizhi Isl. (Kontuniemi 1965) *Hoplocampa alpina Zett. – Kizhi Isl. (Kontuniemi 1965) *Nematus (Pteronidea) capreae (L.) – Shun’ga (Kontuniemi 1965) *Athalia glabricollis Thoms. – Tolvuya (Kontuniemi 1965) Cladius pectinicornis Geoffr. – Vorobyi *Eriocampa dorpatica Konow – Velikaya Niva (Kontuniemi 1965) Siobla ruicornis (Cameron) – Tipinitsy Fenusa pusilla Lep. – Shun’ga (Kontuniemi 1965, Viramo, 1969) *Tenthredo rossii (Panzer) – Shun’ga, Velikaya Niva (Kontuniemi 1965) Cephidae Cephus cultratus Evers. – Kizhi Isl. (Kontuniemi 1965), Eglov Isl., Khvost Isl., Rogachev Isl., Lyudskoi Isl., Sennaya Guba Cephus fumipennis Evers. – Lelikovo, Ernitsky Isl. Cephus nigrinus Thoms. – Eglov Isl., Rogachev Isl., Lyudskoi Isl. Calameuta iliformis (Evers.) – Lyudskoi Isl., Sennaya Guba, Lelikovo Xiphydriidae Xiphydria camelus L. – Vorobyi, Kurgenitsy, Myagrozero, Oyatevschina Xiphydria picta Konow – Kizhi Isl. Siricidae Urocerus gigas L. – Oyatevschina, Nizhnee Myagrozero Sirex juvencus L. – Kizhi Isl. Bethylidae Bethylus fuscicornis (Jurine) – Eglov Isl. Dryinidae Lonchodryinus ruicornis-complex – Vorobyi, Velikaya Niva Mutillidae Mutilla europaea L. – Bol. Klim. Isl., B.Lelikoskiy Isl., Kuzaranda, Oyatevschina, Turastamozero, Nizhnee Myagrozero Chrysididae Chrysis angustula Schenck – Oyatevschina, Kizhi Isl., Vorobyi, Turastamozero Chrysis impressa Schenck – Vorobyi, Turastamozero Chrysis solida Haupt – Kurgenitsy Chrysis ruddii Shuckard – Kizhi Isl. Chrysura hirsuta (Gerstaecker) – Vorobyi *Pseudomalus auratus (L.) – Tolvuya (Hellén 1919) Formicidae Myrmica lobicornis Nyl. – Sennaya Guba Myrmica lonae Finzi – Sennaya Guba 300 Reports of the Finnish Environment Institute 40 | 2014 Myrmica rubra L. – Kizhi Isl., Vorobyi, Sennaya Guba Myrmica ruginodis Nyl. – Vorobyi Myrmica rugulosa Nyl. – Sennaya Guba Myrmica scabrinodis Nyl. – Sennaya Guba Lasius niger (L.) – Sennaya Guba Formica fusca L.– Sennaya Guba Formica rufa coll. – Sennaya Guba Formica sanguinea Latr. – Sennaya Guba Camponotus herculeanus L. – Vorobyi Pompilidae Dipogon vechti Day – Myagrozero, Nizhnee Myagrozero Dipogon bifasiatus (Geoffr.) – Velikaya Guba (Wolf 1967),Turastamozero, Auplopus carbonarius (Scop.) – Turastamozero, Nizhnee Myagrozero Agenioideus cinctellus (Spin.) – Vorobyi, Podyelniki, Myagrozero, Nizhnee Myagrozero, Eglov Isl. Arachnospila opinata (Tourn.) – Vorobyi, Myagrozero Anoplius nigerrimus (Scop.) – Podyelniki, Myagrozero, Nizhnee Myagrozero, Lelikovo Vespidae Eumenes coarctatus (L.) – Shun’ga Eumenes coronatus (Panz.) – Vorobyi, Shun’ga, Turastamozero Eumenes pedunculatus (Panz.) – Vorobyi, Nizhnee Myagrozero Discoelius dufourii Lep. – Kurgenitsy, Turastamozero Ancistrocerus antilope (Panz.) – Vorobyi, Turastamozero, Nizhnee Myagrozero Ancistrocerus claripennis Thoms. – Shun’ga (Pekkarinen & Huldén 1991), Turastamozero, Nizhnee Myagrozero Ancistrocerus parietinus (L.) – Rogachev Isl., Shun’ga, Podyelniki Ancistrocerus parietum (L.) – Kizhi Isl., Ladmozero, Nizhnee Myagrozero Ancistrocerus scoticus Curtis – Turastamozero Ancistrocerus trifasciatus Mull. – Kizhi Isl., Turastamozero, Podyelniki, Kosmozero, Eglov Isl. Symmorphus angustatus Zett. – Turastamozero, Ladmozero, Nizhnee Myagrozero Symmorphus allobrogus (Saussure) – Tolvuya (Pekkarinen & Huldén 1991), Kizhi Isl., Turastamozero, Vikshezero Symmorphus bifasciatus (L.) – Vorobyi, Kurgenitsy, Kosmozero, Turastamozero, Shun’ga, Rogachev Isl. Gymnomerus laevipes (Schuck.) – Vorobyi, Lelikovo Stenodynerus picticrus Thoms. – Nizhnee Myagrozero Euodynerus quadrifasciatus (F.) – Vorobyi Vespa crabro L. – Vorobyi, Podyelniki, Turastamozero, Nizhnee Myagrozero, Myagrozero Vespula rufa L. – Kizhi Isl., Turastamozero Vespula vulgaris L. – Kizhi Isl., Boyarschina, Sennaya Guba, Turastamozero Dolichovespula media Retz. – Bol’shoiu Lelikoskiy Isl., Eglov Isl., Polya, Uzkaya Salma, Turastamozero Dolichovespula norwegica F. – Kizhi Isl., Vorobyi, Vikshezero, Podyelniki, Polya, Uzkaya Salma, Turastamozero, Myagrozero Dolichovespula saxonica F. – Myagrozero, Turastamozero, Eglov Isl., Rogachev Isl. Dolichovespula sylvestris Scop. – Podyelniki, Turastamozero Sphecidae Ammophila sabulosa L. – Kurgenitsy, Vorobyi Crabronidae Trypoxylon attenuatum Smith – Vegoruksy, Lyudskoi Isl., Lelikovo Trypoxylon igulus (L.) – Podyelniki Reports of the Finnish Environment Institute 40 | 2014 301 Pemphredon inornata Say – Eglov Isl., Pemphredon lugubris (F.) – Eglov Isl., Podyelniki Pemphredon morio v.d.Lind. – Podyelniki, Nizhnee Myagrozero Pemphredon wesmaeli A.Mor. – Rogachev Isl. Mimumesa dahlbomi (Wesm.) – Kurgenitsy Crabro peltarius (Schreber) – Rechnoi Isl. Ectemnius cavifrons Thoms. – Kizhi Isl., Volkostrov Isl. Ectemnius continuus F. – Kurgenitsy, Myagrozero, Turastamozero Ectemnius dives Lep. et Br. – Podyelniki Ectemnius fossorius L. – Vorobyi, Kurgenitsy, Volkostrov Isl., Bolshoi Lelikoskiy Isl., Turastamozero, Podyelniki, Zubovo, Eglov Isl., Ladmozero, Myagrozero, Nizhnee Myagrozero Ectemnius lapidarius Panz. – Kurgenitsy Ectemnius ruicornis Zett. – Nizhnee Myagrozero, Kurgenitsy, Turastamozero Ectemnius spinipes (A. Mor.) – Nizhnee Myagrozero, Turastamozero Lestica clypeata (Schreber) – Podyelniki Crossocerus assimilis Smith – Kizhi Isl. Crossocerus dimidiatus (F.) – Kurgenitsy Crossocerus heydeni Koehl. – Vorobyi, Podyelniki Crossocerus vagabundus Pz. – Eglov Isl. Spilomena enslini Blüthgen – Podyelniki, Myagrozero Mellinus arvensis (L.) – Vorobyi Oxybelus uniglumis – Ladmozero Nysson interruptus (F.) – Vorobyi Nysson niger Chevrier – Nizhnee Myagrozero Nysson spinosus – Nizhnee Myagrozero ?Passaloecus borealis Dahlbom – Nizhnee Myagrozero ?Passaloecus gracilis (Curtis) – Vorobyi Passaloecus insignis v.d.Lind. – Vorobyi, Ernitsky Isl., Nizhnee Myagrozero Argogorytes fargei Shuckard – Vorobyi Argogorytes mystaceus L. – Nizhnee Myagrozero, Eglov Isl. Gorytes quadrifasciatus (F.) – Vorobyi, Kurgenitsy, Yu. Oleny Isl., Podyelniki Rhopalum clavipes L. – Turastamozero Rhopalum coarctatum Scop. – Kurgenitsy, Nizhnee Myagrozero, Eglov Isl., Rogachev Isl. Tachysphex pompiliformis (Panzer) – Volkostrov Isl. Apidae Hylaeus annulatus (L.) – Kizhi Isl., Rogachev Isl., Sennaya Guba Hylaeus bisinuatus Först. – Kizhi Isl., Kurgenitsy Hylaeus communis Nyl. – Kizhi Isl., Kurgenitsy *Hylaeus confusus Nyl. – Sennaya Guba, Tolvuya (Söderman & Leinonen 2003) Hylaeus gibbus Sounders – Rogachev Isl. Hylaeus nigritus (F.) – Vorobyi Lasioglossum albipes (F.) – Sennaya Guba *Lasioglossum fratellum (Perez) – Sennaya Guba (Söderman & Leinonen 2003) Lasioglossum leucopus (Kirby) – Sennaya Guba Halictus rubicundus Christ – Kizhi Isl. *Halictus tumulorum (L.) – Sennaya Guba, Tolvuya (Söderman & Leinonen 2003) *Nomada panzeri Lep. – Sennaya Guba (Söderman & Leinonen 2003) *Andrena cineraria L. – Sennaya Guba (Söderman & Leinonen 2003) Andrena intermedia Thoms. – Kosmozero *Andrena haemorrhoa F. – Sennaya Guba (Söderman & Leinonen 2003) *Andrena pilipes F. – Sennaya Guba (Söderman & Leinonen 2003) 302 Reports of the Finnish Environment Institute 40 | 2014 *Andrena ruicrus Nyl. – Tolvuya (Söderman & Leinonen 2003) *Andrena semilaevis Perez – Tolvuya (Söderman & Leinonen 2003) *Andrena subopaca Nyl. – Sennaya Guba (Söderman & Leinonen 2003) *Andrena tarsata Nyl. – Tolvuya (Söderman & Leinonen 2003) *Dufourea dentiventris (Nyl.) – Tolvuya (Söderman & Leinonen 2003) *Melitta haemorrhoidalis F. – Tolvuya (Söderman & Leinonen 2003) *Anthophora furcata Pz. – Tolvuya (Söderman & Leinonen 2003) Osmia nigriventris Zett. – Vorobyi Osmia pilicornis F.Smith – Vorobyi Megachile lagopoda L. – Nizhnee Myagrozero *Megachile lapponica Thoms. – Kuzaranda (Niemelä 1936) *Megachile versicolor F.Smith – Tolvuya (Söderman & Leinonen 2003) *Megachile willughbiella (Kirby) – Turastamozero, Shun’ga (Niemelä 1936) Macropis fulvipes (F.) – Myagrozero Bombus consobrinus Dahlb. – Oyatevschina *Bombus distinguendus F.Mor. – Kizhi Isl., Tolvuya (Söderman & Leinonen 2003) Bombus hypnorum L. – Sennaya Guba, Oyatevschina, Lipovitsy, Polya Bombus humilis Ill. – Kizhi Isl., Sennaya Guba, Rogachev Isl. Bombus jonellus Kirby – Eglov Isl., Oyatevschina Bombus lapidarius L. – Kizhi Isl., Vorobyi, Oyatevschina, Podyelniki, Sennaya Guba, Rogachev Isl. Bombus lucorum L. – Kizhi Isl., Vorobyi, Sennaya Guba, Nizhnee Myagrozero, Turastamozero, B.Lelikoskiy Isl., Lipovitsy, Polya, Uzkaya Salma, Tambitsy, Eglov Isl. Bombus pascuorum Scop. – Vorobyi, Oyatevschina, Nizhnee Myagrozero, Podyelniki, Turastamozero, Sennaya Guba, Lipovitsy, Eglov Isl. Bombus pratorum Scop. – Kizhi Isl., Oyatevschina, Podyelniki, Nizhnee Myagrozero, Turastamozero, Polya Bombus ruderarius Muller – Kizhi Isl. Bombus schrencki Morawitz, – Polya, Tambitsy, Turastamozero Bombus semenoviellus Skorikov – Lelikovo Bombus solstitialis Pz. – Vorobyi *Bombus soroeensis (F.) – Sennaya Guba, Tolvuya (Söderman & Leinonen 2003) Bombus sporadicus Nyl. – Polya, Lipovitsy, Uzkaya Salma, Turastamozero Bombus veteranus F. – Kizhi Isl., Vorobyi, Oyatevschina, Lelikovo, Sennaya Guba, Rogachev Isl. Bombus Psithyrus campestris Pz. – Oyatevschina Bombus Psithyrus bohemicus (Seidl.) – Sennaya Guba *Bombus Psithyrus quadricolor globosus Ev. – Sennaya Guba, Tolvuya (Pekkarinen et al. 1981) Bombus Psithyrus rupestris F. – Kizhi Isl., Sennaya Guba Bombus Psithyrus sylvestris (Lep.) – Sennaya Guba Gasteruptiidae Gasteruption assectator L. – Kizhi Isl. Gasteruption jaculator L. – Kizhi Isl. Evaniidae Brachygaster minuta Ol. – Lipovitsy, Bol. Lelikoskiy Isl., Nizhnee Myagrozero, Turastamozero, Uzkaya Salma Diapriidae *Zygota nigra (Thoms.) – Velikaya Guba (Hellén 1964) Heloridae Helorus striolatus Cameron – Myagrozero Proctotrupidae Disogmus areolator Hal. – Podyelniki Reports of the Finnish Environment Institute 40 | 2014 303 Phaneroserphus calcar (Hal.) – Eglov Isl. Proctotrupes gravidator L. – Vegoruksy Exallonyx (Eocodrus) sp. – Oyatevschina Scelionidae Sparasion ruipes Ruthe – Kizhi Isl. Aphidiidae Pauesia unilachni (Gahan) – Turastamozero Aphidius cingulatus (Ruthe) – Turastamozero Aphidius urticae Haliday – Lipovitsy Aphidius sp. – Turastamozero Lipolexis gracilis Först. – Turastamozero *Trioxys (Binodoxys) centaureae (Hal.) – Shun’ga (Mackauer 1968) Braconidae Chorebus trjapitzini Tobias – Kizhi Isl. Rogas circumscriptus Nees – Eglov Isl. Rogas geniculator Nees – Eglov Isl. Rogas medianus Thoms. – Podyelniki *Proterops nigripennis Wesm. – Tolvuya (Hellén 1958) Ichneumonidae Hybrizon buccatus Breb. – Vorobyi, Turastamozero, Nizhnee Myagrozero Endromopoda arundinator (F.) – Lelikovo, Ernitsky Isl. Endromopoda detrita (Holmgr.) – Lelikovo, Turastamozero, Eglov Isl., Rogachev Isl. Endromopoda phragmitidis (Perkins) – Ernitsky Isl. Endromopoda nigricoxis (Ulbricht) – Velikaya Niva Scambus inanis (Schrank) – Myagrozero Scambus nigricans Thoms. – Oyatevschina Gregopimpla inquisitor (Scop.) – Rogachev Isl. Ephialtes manifestator (L.) – Kizhi Isl. ?Dolichomitus dux Tscheck – Lipovitsy Perithous albicinctus (Grav.) – Turastamozero Apechtis capulifera (Kriecb.) – Turastamozero Apechtis compunctor L. – Vorobyi, Turastamozero, Shun’ga, Nizhnee Myagrozero, Eglov Isl., Rogachev Isl. Apechtis quadridentata Thoms. – Vorobyi, Turastamozero, Polya, Tipinitsy, Tambitsy Pimpla arctica Zett. – Kizhi Isl., Uzkaya Salma l., Turastamozero Pimpla contemplator (Müll.) – Velikaya Niva, Shun’ga Pimpla insignatoria (Grav.) – Kizhi Isl., Vorobyi, Kosmozero, Oyatevschina, Sennaya Guba, Podyelniki, Turastamozero, Uzkaya Salma Pimpla melanacrias Perkins – Kizhi Isl., Uzkaya Salma Pimpla ruipes (Miller) – Vorobyi, Kurgenitsy, Oyatevschina, Sennaya Guba,Turastamozero, Nizhnee Myagrozero, Eglov Isl., Rogachev Isl. Pimpla turionellae L. – Velikaya Niva, Vorobyi Itoplectis alternans (Grav.) – Oyatevschina, Turastamozero Acropimpla pictipes (Grav.) – Tolvuya Iseropus stercorator F. – Kizhi Isl., Vorobyi Zaglyptus multicolor Grav. – Vorobyi, Tipinitsy Zaglyptus varipes (Grav.) – Vorobyi, Sennaya Guba, Podyelniki, Uzkaya Salma ?Clistopyga canadensis Prov. – Vorobyi, Turastamozero Schizopyga lavifrons Holmgr. – Vorobyi Schizopyga frigida Cresson – Kosmozero Acrodactyla degener (Hal.) – Lipovitsy, Turastamozero Acrodactyla quadrisculpta (Grav.) – Lipovitsy, Turastamozero 304 Reports of the Finnish Environment Institute 40 | 2014 Polysphincta ruipes Grav. – Kurgenitsy, Yu. Oleny Isl., Sennaya Guba, Oyatevschina Zatypota albicoxa Walk. – Tambitsy Delomerista sp. – Oyatevschina Poemenia hectica Grav. – Podyelniki, Kazhma Megarhyssa rixator (Shellenberg) – Kizhi Isl. Rhyssella approximator (F.) – Kizhi Isl., Myagrozero, Uzkaya Salma Diplazon deletus (Thoms.) – Podyelniki Diplazon laetatorius F., Yu. Oleny Isl., Nizhnee Myagrozero, Podyelniki, Khvost Isl., Rogachev Isl., Tipinitsy Diplazon tetragonus Thunb. – Vorobyi Diplazon tibiatorius (Thunb.) – Velikaya Niva Diplazon scutatorius Teunissen – Eglov Isl. Homotropus megaspis Thoms. – Eglov Isl. Homotropus nigritarsus (Grav.) – Eglov Isl. Promethes sulcator (Grav.) – Kurgenitsy, Eglov Isl. Syrphophilus bizonarius Grav. – Kizhi Isl., Sennaya Guba Sussaba cognata (Holmgr.) – Lelikovo, Tolvuya Cylloceria caligata (Grav.) – Oyatevschina Cylloceria melancholica (Grav.) – Bol. Lelikoskiy Isl., Myagrozero, Turastamozero, Uzkaya Salma, Polya Rossemia longithorax Humala – Polya Orthocentrus patulus Holmgr. – Turastamozero Orthocentrus sannio Holmgr. – Turastamozero Orthocentrus spurius Grav. – Podyelniki, Volkostrov Isl., Oyatevschina, Turastamozero Orthocentrus winnertzii Först. – Myal› Isl., Turastamozero, Podyelniki Plectiscus impurator – Nizhnee Myagrozero, Uzkaya Salma, Turastamozero Picrostigeus recticauda (Thoms.) – Turastamozero, Bol. Lelikoskiy Isl. Stenomacrus celer (Holmgr.) – Bol. Klim. Isl., Polya Nerateles compressus – Turastamozero Gnathochorisis crassulus (Thoms.) – Oyatevschina, Podyelniki, Lipovitsy, Uzkaya Salma, Turastamozero Gnathochorisis dentifer Thoms. – Turastamozero, Kopanets lake. Aperileptus albipalpus (Grav.) – Turastamozero, Nizhnee Myagrozero Aperileptus infuscatus Först. – Turastamozero Aperileptus vanus Först. – Turastamozero Aperileptus cf. vanus Först. – Lipovitsy Eusterinx argutula Först. – Uzkaya Salma, Turastamozero, Tipinitsy Eusterinx inaequalis Först. – Nizhnee Myagrozero Eusterinx tenuicincta Först. – Vorobyi Symplecis bicingulata Grav. – Turastamozero Symplecis cf. clipeator Lundbeck – Vorobyi Hemiphanes erratum Humala – Tipinitsy Megastylus cruentator Schiødte – Podyelniki Megastylus orbitator Schiødte – Volkostrov Isl., Podyelniki, Uzkaya Salma, Turastamozero Megastylus pectoralis – Lipovitsy Helictes borealis Holmgr. – Turastamozero, Vorobyi Helictes erythrostoma Gmelin – Vorobyi Proclitus ardentis Rossem – Myagrozero, Turastamozero Proclitus comes Hal. – Lipovitsy, Turastamozero Proclitus praetor Hal. – Vorobyi, Eglov Isl. Nizhnee Myagrozero, Turastamozero Dialipsis exilis Först. – Turastamozero Reports of the Finnish Environment Institute 40 | 2014 305 Plectiscidea aquilonia Humala – Turastamozero Plectiscidea collaris Grav. – Lipovitsy, Turastamozero, Tipinitsy Plectiscidea communis Först. – Lipovitsy, Tipinitsy Plectiscidea posticata Först. – Myagrozero, Turastamozero, Tipinitsy Plectiscidea zonata (Grav.) – Velikaya Niva Pantisarthrus lubricus Först. – Turastamozero Pantisarthrus luridus Först. – Turastamozero Lycorina triangulifera Holmgr. – Sennaya Guba Coleocentrus caligatus Grav. – Eglov Isl. Coleocentrus exareolatus Kriechb. – Lipovitsy Coleocentrus excitator Poda – Kosmozero, Vikshezero Arotes albicinctus (Grav.) – Myagrozero Ischnocerus rusticus Geoffr. – Kizhi Isl., Vorobyi, Podyelniki Odontocolon dentipes Gmel. – Vorobyi *Gelis agilis (F.) – Velikaya Niva (Hellén 1970) *Gelis discedens (Först.) – Velikaya Niva (Hellén 1970) Ecthrus reluctator L. – Velikaya Niva Theroscopus hemipterus (F.) – Turastamozero Mesoleptus distinctus (Först.) – Eglov Isl. Glyphicnemis proligator (F.) – Tolvuya Pleolophus basizonus (Grav.) – Uzkaya Salma Schenkia graminicola (Grav.) – Velikaya Niva,Velikaya Niva Cubocephalus femoralis (Thoms.) – Velikaya Niva Cubocephalus associator Thunb. – Tolvuya, Velikaya Niva, Oyatevschina Megaplectes monticola (Grav.) – Unitsa Sphecophaga vesparum Curtis – Vorobyi Acroricnus stylator Thunb. – Vorobyi ?Aptesis improba (Grav.) – Tolvuya Ischnus migrator (F.) – Vorobyi, Velikaya Niva Glypta caudata Thoms. – Kizhi Isl. Glypta ceratites Grav. – Eglov Isl., Podyelniki Glypta cylindrator F. – Vorobyi, Turastamozero, Podyelniki, Oyatevschina, Eglov Isl., Rogachev Isl. Glypta extincta Ratz. – Velikaya Niva Glypta heterocera Thoms. – Kizhi Isl. Glypta mensurator F. – Turastamozero, Nizhnee Myagrozero Lissonota lineolaris (Gmel.) – Kurgenitsy, Yu. Oleny Isl., Oyatevschina, Rogachev Isl. Lissonota nitida (Grav.) – Velikaya Niva Lissonota punctiventris Thoms. – Velikaya Niva Alloplasta piceator (Thunb.) – Kizhi Isl., Eglov Isl. Cryptopimpla caligata (Grav.) – Vorobyi, Kosmozero Cryptopimpla errabunda (Grav.) – Podyelniki, Velikaya Niva Exetastes laevigator (Villers) – Shun’ga Adelognathus brevicornis Holmgr. – Lydskoi Isl., Sennaya Guba ?Adelognathus dealbatus Kasp. – Nizhnee Myagrozero Adelognathus dorsalis (Grav.) – Vorobyi, Eglov Isl., Podyelniki Adelognathus pilosus Thoms. – Eglov Isl. Idiogramma euryops Schmied. – Velikaya Niva Phytodietus gelitorius Thunb. – Vorobyi, Turastamozero Dyspetes luteomarginatus Hab. – Tipinitsy, Turastamozero Cosmoconus ceratophorus Thoms. – Podyelniki Cosmoconus elongator F. – Zubovo, Nizhnee Myagrozero 306 Reports of the Finnish Environment Institute 40 | 2014 Cosmoconus hinzi Kasp. – Vorobyi, Kosmozero Cosmoconus nigriventris Kasp. – Vorobyi, Podyelniki Polyblastus nanus Kasp. – Kurgenitsy Polyblastus pinguis Grav. – Vorobyi Polyblastus subalpinus Holmgr. – Turastamozero Polyblastus tener Haberm. – Lyudskoi Isl. Polyblastus varitarsus (Grav.) – Eglov Isl., Polya, Tipinitsy, B.Lelikoskiy Isl., Myal Isl. Polyblastus wahlbergi Holmgr. – Turastamozero Ctenochira gilvipes (Holmgr.) – Eglov Isl. Ctenochira marginata Holmgr. – B.Lelikoskiy Isl., Kopanets lake Ctenochira propinqua Grav. – Vorobyi, B.Lelikoskiy Isl., Sennaya Guba Ctenochira xanthopyga (Holmgr.) – Eglov Isl. Tryphon bidentatus Stephens – Vorobyi, Kurgenitsy, Lelikovo Tryphon exclamationis Grav. – Kurgenitsy Tryphon obtusator (Thunb.) – Kizhi Isl., Eglov Isl., Ernitsky Isl., Lyudskoi Isl. Tryphon thomsoni Roman – Kurgenitsy Erromenus plebejus (Woldst.) – Lelikovo Cycasis rubiginosa Grav. – Vorobyi Kristotomus laetus Grav. – Vorobyi Exyston sponsorius (F.) – Vorobyi, Oyatevschina Eridolius auriluus (Hal.) – Kurgenitsy Eridolius ruilabris (Holmgr.) – Oyatevschina Eridolius rufonotatus (Holmgr.) – Oyatevschina Eridolius schiodtei Holmgr. – Kosmozero Smicroplectrus excisus Kerrich – Lelikovo Smicroplectrus perkinsi Kerrich – Vorobyi Exenterus amictorius Panz. – Vorobyi Excavarus apiarius (Grav.) – Vorobyi Ctenopelma lapponicum Holmgr. – Rogachev Isl. Ctenopelma nigrum Holmgr. – Velikaya Niva (Hellén 1948) Ctenopelma tomentosum Desv. – Oyatevschina Xenoschesis ustulata (Desv.) – Podyelniki, Lipovitsy, Velikaya Niva Pion fortipes Grav. – Vorobyi, Kizhi Isl., Rogachev Isl. Pion nigripes Schiødte =crassipes Holmgr. – Kizhi Isl. Scolobates auriculatus F. – Lipovitsy Opheltes glaucopterus L. – Kurgenitsy, Vorobyi, Lipovitsy, Vegoruksy Perilissus rufoniger (Grav.) – Oyatevschina Perilissus variator (Müll.) – Vorobyi, Rogachev Isl. *Phobetes leptocerus (Grav.) – Velikaya Niva (Hellén1961) Hypamblys albopictus (Grav.) – Velikaya Niva Rhaestus lativentris Holmgr. – Vorobyi Rhaestus ophthalmicus Holmgr. – Vorobyi Rhaestus ruipes Holmgr. – Vorobyi ?Alexeter multicolor (Grav.) – Kosmozero Sympherta jactator (Thunb.) – Podyelniki Sympherta obligator (Thunb.) – Vorobyi, Velikaya Niva Mesoleius aulicus Grav. – Polya Anisotacrus bipunctatus (Grav.) – Oyatevschina Hadrodactylus tiphae (Geoffr.) – Tolvuya, Kizhi Isl. Oxytorus luridator (Grav.) – Vorobyi, Turastamozero, Nizhnee Myagrozero, Myagrozero Collyria trichophthalma Thoms. – Lelikovo, Sennaya Guba, Ernitsky Isl., Eglov Isl., Rogachev Isl. Reports of the Finnish Environment Institute 40 | 2014 307 Probles microcephalus Grav. – Kurgenitsy Tersilochus caudatus (Holmgr.) – Vorobyi Barycnemis bellator (Müll.) – Vorobyi Charops cantator (DeGeer) – Eglov Isl. Casinaria sp. – Podyelniki Tranosemella coxalis Brischke – Kurgenitsy *Dusona stenogaster (Först.) – Velikaya Niva (Hellén 1962) *Dusona stragifex (Först.) – Velikaya Niva (Hellén 1937) ?Diadegma rectiicator Aubert – Kosmozero *Enicospilus undulatus (Grav.) – Kizhi Isl. (Hellén 1926) Cidaphus areolatus Boie – Podyelniki Therion circumlexum L. – Turastamozero Heteropelma amictum (F.) – Tipinitsy Aphanistes ruicornis Grav. – Vorobyi, Eglov Isl. Camposcopus canaliculatus Ratz. – B.Lelikoskiy Isl. Agrypon lexorium Thunb. – Velikaya Niva, Podyelniki, Turastamozero Chorinaeus brevicalcar Thoms. – Podyelniki Exochus prosopius Grav. – Sennaya Guba Triclistus pallipes Holmgr. – Eglov Isl. Alomya debellator F. – Kizhi Isl., Turastamozero, Kosmozero, Podyelniki, Eglov Isl., Rogachev Isl. Alomya pygmaea Heinrich – Kurgenitsy, Vorobyi, Sennaya Guba, Radkol‘e, Tolvuya (Hellén 1951), Eglov Isl., Rogachev Isl. Misetus oculatus Wesm. – Vorobyi, Turastamozero, Uzkaya Salma, Polya Heterischnus debilis Grav. – Podyelniki Platylabus vibratorius Thunb. – Vorobyi Platylabus heteromallus (Berthouemieu) – Vikshezero Pseudoplatylabus violentus (Grav.) – Kurgenitsy Acolobus albimanus (Grav.) – Megostrov Isl. Protichneumon similatorius (F.) – Kizhi Isl., Vorobyi, Oyatevschina Aoplus castaneus (Grav.) – Vorobyi Cratichneumon jocularis (Wesm.) – Ernitsky Isl. Cratichneumon ruifrons (Grav.) – Eglov Isl. Cratichneumon sicarius (Grav.) – Kizhi Isl. Cratichneumon viator (Scop.) – Kizhi Isl., Velikaya Guba, Oyatevschina, Vorobyi, Eglov Isl. Ctenichneumon divisorius (Grav.) – Vorobyi Ctenichneumon inspector (Wesm.) – Vorobyi Syspasis scutellator (Grav.) – Vikshezero, Eglov Isl. *Hoplismenus bidentatus (Gmel.) – Kizhi Isl. (Hellén 1936) Homotherus locutor (Thunb.) – Ernitsky Isl. Homotherus varipes (Grav.) – Vorobyi *Hybophorellus injucundus (Wesm.) – Velikaya Niva (Hellén 1951) Anisopygus pseudonymus (Wesm.) – Rogachev Isl. Hepiopelmus melanogaster (Gmelin) – Vorobyi Ichneumon balteatus Wesm. – Kurgenitsy Ichneumon caedator Grav. – Lambaznik Isl. Ichneumon cessator Müller – Velikaya Niva Ichneumon gracilicornis Grav. – Vorobyi, Myal Isl. Ichneumon oblongus Schrank – Vikshezero Ichneumon primatorius Först. – Eglov Isl. *Eurylabus tristis (Grav.) – Shun’ga (Hellén 1951) Amblyjoppa proteus Christ – Vorobyi, Bol. Lelikoskiy Isl., Turastamozero 308 Reports of the Finnish Environment Institute 40 | 2014 Limerodops elongatus (Brischke) – Vikshezero, Kizhi Isl. Sycaonia foersteri (Wesm.) – Ernitsky Isl. Virgichneumon albosignatus (Grav.) – Vorobyi *Virgichneumon faunus (Grav.) – Kuzaranda (Ranin 1979) Vulgichneumon deceptor (Scop.) – Ernitsky Isl. Vulgichneumon suavis (Grav.) – Ernitsky Isl., Lelikovo DIPTERA Trichoceridae Trichocera rufescens Edwards – Polya, Tambitsy, Tipinitsy Pediciidae Ula bolitophila Loew – Velikaya Niva Ula sylvatica Meigen – Polya, Tipinitsy Pedicia rivosa L. – Lipovitsy, Tambitsy, Tipinitsy, Turastamozero Tricyphona unicolor Schummel – Ernitskiy Isl., Kizhi Isl., Lelikovo Limoniidae Elephantomyia krivosheinae Savtshenko – Myal’ Isl. Helius longirostris Meigen – Ernitskiy Isl., Klimenicy, Lelikovo, Polya, Sennaya Guba, Shunevskiy Isl., Uzkaya Salma, Vikshezero Austrolimnophila unica Osten-Sacken – Paleostrov Isl., Tolvuya Idioptera linnei Oosterbroek – Kizhi Isl., Vikshezero Idioptera pulchella Meigen – Vikshezero, Volkostrov Isl. Limnophila pictipennis Meigen – Lelikovo Neolimnomyia nemoralis Meigen – Lipovitsy, Lyudskoi Isl., Paleostrov Isl., Rogachev Isl., Sennaya Guba Euphylidorea phaeostigma Schummel – Podyelniki, Polya Phylidorea abdominalis Staeger – Verkhnee Myagrozero Phylidorea ferruginea Meigen – Ernitskiy Isl., Vorobyi Phylidorea fulvonervosa Schummel – Bol. Lelikovskiy Isl. Phylidorea longicornis Schummel – Klimenicy, Lipovitsy, Shunevskiy Isl., Verkhnee Myagrozero, Vikshezero Phylidorea squalens Zetterstedt – Lipovitsy, Verkhnee Myagrozero Pilaria discicollis Meigen – Klimenicy, Kurgenitsy, Podyelniki Erioptera lutea Meigen – Vegoruksy Erioptera nielseni de Meijere – Uzkaya Salma Molophilus ater Meigen – Tolvuya Molophilus bihamatus de Meijere – Klimenicy Molophilus lavus Goetghebuer – Lipovitsy Molophilus griseus Meigen – Kurgenitsy Molophilus medius de Meijere – Lipovitsy Molophilus ochraceus Meigen – Vikshezero Ormosia depilata Edwards – Kizhi Isl., Lelikovo Ormosia ruicauda Zetterstedt – Bol. Lelikovskiy Isl., Klimenicy, Vikshezero Ormosia staegeriana Alexander – Klimenicy, Lipovitsy Rhypholophus varius Meigen – Lipovitsy Gnophomyia viridipennis Gimmerthal – Bol. Lelikovskiy Isl., Kopanets lake, Lipovitsy Neolimonia dumetorum Meigen – Bol. Lelikovskiy Isl., Myagrozero Dicranomyia distendens Lundström – Eglov Isl. Dicranomyia modesta Meigen – Klimenicy, Paleostrov Isl., Polya, Vavlok Isl. Discobola annulata L. – Turastamozero Discobola caesarea Osten-Sacken – Bol. Lelikovskiy Isl. Limonia badia Walker – Polya, Tipinitsy Reports of the Finnish Environment Institute 40 | 2014 309 Limonia lavipes Fabricius – Klimenicy, Shunevskiy Isl., Vorobyi Limonia macrostigma Schummel – Turastamozero, Yu. Oleny Isl. Limonia phragmitidis Schrank – Verkhnee Myagrozero Limonia sylvicola Schummel – Lipovitsy Limonia trivittata Schummel – Kurgenitsy, Volkostrov Isl. Metalimnobia bifasciata Schrank – Bol. Lelikovskiy Isl., Khvost Isl., Lipovitsy, Polya, Turastamozero, Uzkaya Salma, Vorobyi, Yu. Oleny Isl. Metalimnobia quadrimaculata L. – Turastamozero, Verkhnee Myagrozero, Vorobyi Metalimnobia quadrinotata Meigen – Bol. Lelikovskiy Isl., Turastamozero, Verkhnee Myagrozero, Yu. Oleny Isl. Metalimnobia zetterstedti Tjeder – Lipovitsy Rhipidia maculata Meigen – Klimenicy Rhipidia uniseriata Schiner – Lyudskoi Isl. Cylindrotomidae Cylindrotoma distinctissima Meigen – Polya, Vorobyi Diogma glabrata Meigen – Lipovitsy Tipulidae Tipula afinis Schummel – Eglov Isl., Paleostrov Isl. Tipula autumnalis Loew – Vorobyi Tipula circumdata Siebke – Tambitsy Tipula confusa Van der Wulp – Vorobyi Tipula fascipennis Meigen – Kazhma, Vavlok Isl. Tipula fulvipennis fulvipennis DeGeer – Klimenicy Tipula humilis Staeger – Bol. Lelikovskiy Isl., Kizhi Isl., Kosmozero, Podyelniki Tipula irrorata Macquart – Ernitskiy Isl., Tolvuya Tipula laetabilis Zetterstedt – Podyelniki Tipula limitata Schummel – Kosmozero Tipula luna Westhoff – Eglov Isl. Tipula nubeculosa Meigen – Oyatevschina Tipula paludosa Meigen – Vegoruksy Tipula pruinosa pruinosa Wiedemann – Vikshezero Tipula pseudovariipennis Czizek – Kizhi Isl. Tipula scripta Meigen – Bol. Lelikovskiy Isl., Lipovitsy Tipula variicornis Schummel – Lipovitsy, Polya, Vorobyi Tipula varipennis Meigen – Kizhi Isl., Tolvuya, Vorobyi Prionocera turcica Fabricius – Kizhi Isl., Klimenicy Nephrotoma analis Schummel – Vikshezero Nephrotoma cornicina L. – Kosmozero Nephrotoma pratensis L. – Shun’ga Dictenidia bimaculata L. – Rogachev Isl., Turastamozero, Verkhnee Myagrozero Tanyptera atrata L. – Vorobyi Ptychopteridae Ptychoptera minuta Tonnoir – Klimenicy Psychodidae Clytocerus ocellaris Meigen – Vorobyi Dixidae Dixella aestivalis Meigen – Khvost Isl., Vikshezero Dixella borealis Martini – Tambitsy Dixella hyperborea Bergroth – Shunevskiy Isl. Culicidae Anopheles maculipennis Meigen – Kizhi Isl. Culiseta alaskaensis Ludlow – Shunevskiy Isl. 310 Reports of the Finnish Environment Institute 40 | 2014 Culiseta fumipennis Stephens – Lipovitsy, Polya, Uzkaya Salma Culiseta ochroptera Peus – Vorobyi Coquillettidia richiardii Ficalbi – Uzkaya Salma ? Aedes annulipes Meigen – Vikshezero Aedes behningi Martini – Ernitskiy Isl. Aedes cataphyla Dyar – Ernitskiy Isl., Lelikovo, Sennaya Guba Aedes cinereus Meigen – Verkhnee Myagrozero, Vikshezero Aedes communis DeGeer – Ernitskiy Isl. Aedes diantaeus Howard, Dyar et Knab – Ernitskiy Isl., Lipovitsy, Shunevskiy Isl., Vikshezero Aedes excrucians Walker – Ernitskiy Isl., Lelikovo, Shunevskiy Isl., Vikshezero Aedes intrudens Dyar – Lyudskoi Isl Aedes pionips Dyar – Eglov Isl., Vikshezero Aedes punctor Kirby – Polya, Vikshezero Culex territans Walker – Polya, Verkhnee Myagrozero Ceratopogonidae Clinohelea unimaculata Macquart – Klimenicy Anisopodidae Sylvicola cinctus Fabricius – Turastamozero Sylvicola punctatus Fabricius – Vorobyi Scatopsidae Apiloscatopse lavicollis Meigen – Tipinitsy Bibionidae Dilophus femoratus Meigen – Eglov Isl., Kuzaranda, Paleostrov Isl., Rogachev Isl., Vikshezero Bibio clavipes Meigen – Myagrozero Bibio nigriventris Haliday – Eglov Isl., Ernitskiy Isl., Kainos Isl., Klimenicy, Kuivakhda Isl., Lelikovo, Lipovitsy, Lyudskoi Isl., Myal’ Isl., Paleostrov Isl., Polya, Sennaya Guba, Tipinitsy, Vikshezero, Yu. Oleny Isl. Bibio pomonae Fabricius – Vorobyi Ditomyiidae Symmerus nobilis Lackschewitz – Kosmozero Diadocidiidae Diadocidia ferruginosa Meigen – Bol. Lelikovskiy Isl., Kizhi Isl., Lyudskoi Isl., Myal’ Isl., Polya, Shunevskiy Isl., Tambitsy, Tipinitsy, Turastamozero, Vavlok Isl., Verkhnee Myagrozero, Vikshezero, Vorobyi Diadocidia spinosula Tollet – Lyudskoi Isl., Tipinitsy Mycetophilidae Mycomya afinis Staeger – Tambitsy, Tipinitsy, Turastamozero Mycomya annulata Meigen – Klimenicy, Lipovitsy, Myagrozero, Polya, Tambitsy, Tipinitsy, Turastamozero Mycomya brunnea Dziedzicki – Tipinitsy Mycomya cinerascens Macquart – Myal’ Isl., Tipinitsy Mycomya collini Edwards – Paleostrov Isl. Mycomya egregia Dziedzicki – Lyudskoi Isl. Mycomya festivalis Väisänen – Klimenicy Mycomya imbriata Meigen – Turastamozero Mycomya lavicollis Zetterstedt – Podyelniki, Uzkaya Salma Mycomya griseovittata Zetterstedt – Vorobyi Mycomya nigricornis Zetterstedt – Myagrozero, Vorobyi Mycomya nitida Zetterstedt – Klimenicy, Kuivakhda Isl., Lelikovo, Lyudskoi Isl., Paleostrov Isl., Velikaya Niva, Vikshezero, Yu. Oleny Isl. Reports of the Finnish Environment Institute 40 | 2014 311 Mycomya paradentata Väisänen – Polya, Tambitsy, Tipinitsy, Turastamozero Mycomya parva Dziedzicki – Lyudskoi Isl. Mycomya penicillata Dziedzicki – Myagrozero, Turastamozero, Vorobyi Mycomya permixta Väisänen – Lipovitsy, Myagrozero, Polya, Tambitsy, Tipinitsy, Turastamozero Mycomya prominens Lundström – Paleostrov Isl. Mycomya pseudoapicalis Landrock – Klimenicy Mycomya ruicollis Zetterstedt – Klimenicy, Vikshezero Mycomya shermani Garrett – Myagrozero, Polya, Tambitsy, Tipinitsy Mycomya siebecki Landrock – Tambitsy, Tipinitsy Mycomya sp4 (cf. penicillata) – Turastamozero Mycomya trilineata Zetterstedt – Bol. Lelikovskiy Isl., Kurgenitsy, Podyelniki, Turastamozero, Verkhnee Myagrozero, Volkostrov Isl. Mycomya trivittata Zetterstedt – Klimenicy, Lyudskoi Isl., Paleostrov Isl., Tipinitsy, Vikshezero Mycomya wankowiczii Dziedzicki – Lyudskoi Isl., Turastamozero, Yu. Oleny Isl. Mycomya winnertzi Dziedzicki – Paleostrov Isl. Neoempheria pictipennis Haliday – Tipinitsy Neoempheria tuomikoskii Väisänen – Vikshezero Acnemia angusta A. Zaitzev – Kopanets lake, Vikshezero Acnemia nitidicollis Meigen – Bol. Lelikovskiy Isl., Kopanets lake, Kosmozero, Kurgenitsy, Lyudskoi Isl., Oyatevschina, Podyelniki, Polya, Turastamozero, Uzkaya Salma, Velikaya Niva, Vorobyi, Voynavolok Allocotocera pulchella Curtis – Eglov Isl., Klimenicy, Oyatevschina, Turastamozero, Uzkaya Salma Leptomorphus subforcipatus A. Zaitzev & Ševcík – Vorobyi Leptomorphus walkeri Curtis – Kopanets lake Megalopelma nigroclavatum Strobl – Lyudskoi Isl. Monoclona ruilatera Walker – Bol. Lelikovskiy Isl., Kizhi Isl., Kurgenitsy, Oyatevschina, Turastamozero, Vikshezero, Volkostrov Isl. Neuratelia nemoralis Meigen – Lelikovo, Velikaya Niva Phthinia humilis Winnertz – Turastamozero Polylepta borealis Lundström – Kopanets lake Polylepta guttiventris Zetterstedt – Klimenicy, Lipovitsy, Polya, Shunevskiy Isl., Tambitsy, Tipinitsy, Turastamozero, Volkostrov Isl., Yu. Oleny Isl. Sciophila fenestella Curtis – Lyudskoi Isl., Oyatevschina, Podyelniki, Uzkaya Salma, Vikshezero, Vorobyi Sciophila geniculata Zetterstedt – Klimenicy, Oyatevschina Sciophila hirta Meigen – Podyelniki Sciophila nigronitida Landrock – Kizhi Isl., Vorobyi Sciophila persubtilis Polevoi – Oyatevschina, Turastamozero Sciophila thoracica Staeger – Eglov Isl., Ernitskiy Isl., Turastamozero, Vorobyi Syntemna nitidula Edwards – Ernitskiy Isl. Syntemna relicta Lundström – Vikshezero Syntemna setigera Lundström – Lyudskoi Isl. Syntemna stylatoides A. Zaitzev – Lyudskoi Isl., Vorobyi Apolephthisa subincana Curtis – Lyudskoi Isl., Podyelniki, Turastamozero, Velikaya Niva Boletina basalis Meigen – Ernitskiy Isl., Kizhi Isl., Kuivakhda Isl., Lyudskoi Isl., Myal’ Isl., Oyatevschina, Tolvuya, Velikaya Niva, Vorobyi Boletina cincticornis Walker – Kizhi Isl., Oyatevschina, Velikaya Niva, Vorobyi Boletina dissipata Plassmann – Klimenicy Boletina edwardsi Chandler – Turastamozero 312 Reports of the Finnish Environment Institute 40 | 2014 Boletina gripha Dziedzicki – Klimenicy, Lyudskoi Isl., Oyatevschina, Tipinitsy, Tolvuya, Turastamozero, Velikaya Niva, Verkhnee Myagrozero, Vikshezero, Volkostrov Isl., Vorobyi Boletina griphoides Edwards – Oyatevschina, Turastamozero ? Boletina gusakovae A. Zaitzev – Tambitsy, Tipinitsy, Turastamozero Boletina kivachiana Polevoi & Hedmark – Turastamozero Boletina lundstroemi Landrock – Turastamozero Boletina moravica Landrock – Turastamozero, Verkhnee Myagrozero Boletina nigricans Dziedzicki – Kizhi Isl., Klimenicy, Oyatevschina Boletina nigrofusca Dziedzicki – Klimenicy Boletina nitida Grzegorzek – Kainos Isl., Turastamozero Boletina pinusia Maximova – Ernitskiy Isl. Boletina populina Polevoi – Klimenicy, Oyatevschina, Turastamozero, Velikaya Niva, Vorobyi Boletina sciarina Staeger – Kizhi Isl., Turastamozero Boletina silvatica Dziedzicki – Turastamozero Boletina subtriangularis Polevoi & Hedmark – Turastamozero Boletina takagii Sasakava et Kimura – Turastamozero Boletina triangularis Polevoi – Oyatevschina Boletina trivittata Meigen – Klimenicy, Lipovitsy, Myagrozero, Polya, Tambitsy, Tipinitsy Boletina villosa Landrock – Tambitsy Coelosia tenella Zetterstedt – Bol. Lelikovskiy Isl., Turastamozero Coelosia truncata Lundström – Vorobyi Dziedzickia marginata Dziedzicki – Myagrozero Gnoriste apicalis Meigen – Kizhi Isl. Gnoriste bilineata Zetterstedt – Klimenicy Grzegorzeckia collaris Meigen – Oyatevschina Palaeodocosia vittata Coquillett – Bol. Lelikovskiy Isl., Lipovitsy, Tipinitsy Saigusaia laviventris Strobl – Kopanets lake, Lipovitsy Synapha fasciata Meigen – Eglov Isl., Ernitskiy Isl., Khvost Isl. Synapha vitripennis Meigen – Kainos Isl., Lipovitsy Docosia gilvipes Walker – Lyudskoi Isl. Ectrepesthoneura colyeri Chandler – Myagrozero, Uzkaya Salma, Vikshezero, Vorobyi Ectrepesthoneura hirta Winnertz – Eglov Isl., Kizhi Isl., Lyudskoi Isl., Oyatevschina, Podyelniki, Vikshezero, Vorobyi Ectrepesthoneura ovata Ostroverkhova – Uzkaya Salma Ectrepesthoneura pubescens Zetterstedt – Oyatevschina, Velikaya Niva, Vikshezero, Vorobyi Ectrepesthoneura referta Plassmann – Velikaya Niva Leia bilineata Winnertz – Volkostrov Isl. Leia cylindrica Winnertz – Vorobyi Leia picta Meigen – Polya Leia subfasciata Meigen – Ernitskiy Isl., Lipovitsy, Lyudskoi Isl., Oyatevschina, Vikshezero Leia winthemi Lehmann – Uzkaya Salma, Volkostrov Isl. Rondaniella dimidiata Meigen – Turastamozero Tetragoneura sylvatica Curtis – Eglov Isl. Dynatosoma fuscicorne Meigen – Kopanets lake, Podyelniki, Turastamozero Dynatosoma nigromaculatum Lundström – Turastamozero Dynatosoma reciprocum Walker – Vikshezero Dynatosoma thoracicum (s. Zaitzev) – Paleostrov Isl., Uzkaya Salma Epicypta aterrima Zetterstedt – Ernitskiy Isl., Verkhnee Myagrozero Mycetophila abiecta Laštovka – Bol. Lelikovskiy Isl., Vikshezero Reports of the Finnish Environment Institute 40 | 2014 313 Mycetophila alea Laffoon – Tambitsy, Tipinitsy, Turastamozero, Vorobyi Mycetophila attonsa Laffoon – Yu. Oleny Isl. Mycetophila blanda Winnertz – Myagrozero, Tipinitsy, Vorobyi Mycetophila brevitarsata Laštovka – Uzkaya Salma Mycetophila conluens Dziedzicki – Turastamozero, Vorobyi Mycetophila curviseta Lundström – Uzkaya Salma Mycetophila delexa Chandler – Lipovitsy, Turastamozero Mycetophila estonica Kurina – Tipinitsy Mycetophila fungorum DeGeer – Bol. Lelikovskiy Isl., Klimenicy, Kosmozero, Kurgenitsy, Paleostrov Isl., Polya, Tipinitsy, Turastamozero, Vikshezero, Vorobyi Mycetophila gemerensis Ševčík & Kurina – Vorobyi Mycetophila gibbula Edwards – Turastamozero, Yu. Oleny Isl. Mycetophila hetschkoi Landrock – Lipovitsy, Turastamozero Mycetophila ichneumonea Say – Bol. Lelikovskiy Isl., Klimenicy, Kosmozero, Lipovitsy, Paleostrov Isl., Podyelniki, Tambitsy, Tipinitsy, Turastamozero, Verkhnee Myagrozero, Volkostrov Isl., Vorobyi Mycetophila laeta Walker – Tipinitsy Mycetophila lubomirskii Dziedzicki – Tambitsy Mycetophila luctuosa Meigen – Klimenicy, Lipovitsy, Myagrozero, Tambitsy, Turastamozero, Vavlok Isl., Yu. Oleny Isl. Mycetophila magnicauda Strobl – Turastamozero Mycetophila morosa Winnertz – Turastamozero Mycetophila nigrofusca Dziedzicki – Kopanets lake, Turastamozero Mycetophila ocellus Walker – Klimenicy, Turastamozero, Verkhnee Myagrozero Mycetophila perpallida Chandler – Myagrozero, Paleostrov Isl., Polya, Tipinitsy, Turastamozero Mycetophila schnabli Dziedzicki – Lipovitsy, Polya, Tipinitsy Mycetophila signata Meigen – Lipovitsy Mycetophila signatoides Dziedzicki – Lyudskoi Isl., Myagrozero, Polya, Tambitsy, Tipinitsy Mycetophila sordida Van der Wulp – Tambitsy Mycetophila stolida Walker – Lyudskoi Isl. Mycetophila stricklandi Laffoon – Bol. Lelikovskiy Isl., Turastamozero Mycetophila strigata Staeger – Vorobyi Mycetophila strigatoides Landrock – Nizhneje Myagrozero, Turastamozero, Vikshezero Mycetophila strobli Laštovka – Klimenicy, Kosmozero, Lyudskoi Isl., Tipinitsy, Turastamozero, Vikshezero Mycetophila stylata Dziedzicki – Bol. Lelikovskiy Isl. Mycetophila sublunata A. Zaitzev – Klimenicy, Paleostrov Isl., Tipinitsy, Verkhnee Myagrozero Mycetophila subsigillata A. Zaitzev – Bol. Lelikovskiy Isl., Paleostrov Isl., Tambitsy, Tipinitsy, Turastamozero Mycetophila triangulata Dziedzicki – Vorobyi Mycetophila trinotata Staeger – Kurgenitsy, Turastamozero, Vorobyi Mycetophila uschaica Subbotina & Maksimova – Polya Phronia braueri Dziedzicki – Turastamozero, Volkostrov Isl. Phronia caliginosa Dziedzicki – Polya, Tambitsy Phronia cinerascens Winnertz – Turastamozero, Vikshezero Phronia disgrega Dziedzicki – Lyudskoi Isl., Myagrozero, Vikshezero Phronia egregia Dziedzicki – Tipinitsy, Turastamozero Phronia exigua Zetterstedt – Turastamozero Phronia lavipes Winnertz – Tambitsy 314 Reports of the Finnish Environment Institute 40 | 2014 Phronia forcipata Winnertz – Bol. Lelikovskiy Isl., Lyudskoi Isl., Oyatevschina, Volkostrov Isl Phronia forcipula Winnertz – Klimenicy Phronia gagnei Chandler – Bol. Lelikovskiy Isl., Klimenicy Phronia maculata Dziedzicki – Lipovitsy, Tipinitsy, Uzkaya Salma Phronia nigricornis Zetterstedt – Uzkaya Salma Phronia nigripalpis Lundström – Kizhi Isl., Kopanets lake, Vikshezero, Volkostrov Isl., Vorobyi Phronia nitidiventris Van der Wulp – Tambitsy, Turastamozero Phronia notata Dziedzicki – Turastamozero Phronia persimilis Hackman – Khvost Isl., Turastamozero, Vikshezero Phronia siebeckii Dziedzicki – Uzkaya Salma Phronia signata Winnertz – Tambitsy Phronia strenua Winnertz – Bol. Lelikovskiy Isl., Klimenicy, Lelikovo, Shunevskiy Isl., Turastamozero, Volkostrov Isl., Vorobyi Phronia taczanowskii Dziedzicki – Turastamozero Phronia tenuis Winnertz – Polya, Tambitsy, Yu. Oleny Isl. Phronia vitrea Plassmann – Polya Phronia willistoni Dziedzicki – Bol. Lelikovskiy Isl. Platurocypta punctum Stannius – Bol. Lelikovskiy Isl., Klimenicy, Lyudskoi Isl., Turastamozero, Vorobyi Platurocypta testata Edwards – Bol. Lelikovskiy Isl., Kizhi Isl., Kosmozero, Kurgenitsy, Tipinitsy, Turastamozero, Vorobyi, Yu. Oleny Isl. Sceptonia concolor Winnertz – Lipovitsy Sceptonia costata Van der Wulp – Myagrozero, Turastamozero Sceptonia demeijerei Bechev – Vorobyi Sceptonia lavipuncta Edwards – Ernitskiy Isl. Sceptonia fumipes Edwards – Turastamozero, Vorobyi Sceptonia fuscipalpis Edwards – Tambitsy, Turastamozero, Vikshezero Sceptonia hamata Ševčík – Bol. Lelikovskiy Isl., Turastamozero Sceptonia longisetosa Ševčík – Oyatevschina Sceptonia membranacea Edwards – Klimenicy, Polya Sceptonia nigra Meigen – Bol. Lelikovskiy Isl., Ernitskiy Isl., Kuivakhda Isl., Turastamozero, Volkostrov Isl., Vorobyi, Yu. Oleny Isl. Sceptonia pilosa Bukowski – Bol. Lelikovskiy Isl., Kuivakhda Isl., Lyudskoi Isl., Turastamozero Sceptonia regni Chandler – Turastamozero Trichonta atricauda Zetterstedt – Vikshezero Trichonta concinna Gagné – Tambitsy Trichonta conjungens Lundström – Tipinitsy Trichonta excisa Lundström – Volkostrov Isl. Trichonta hamata Mik – Yu. Oleny Isl. Trichonta subfusca Lundström – Turastamozero Trichonta vulcani Dziedzicki – Lipovitsy Trichonta vulgaris Loew – Turastamozero Zygomyia angusta Plassmann – Lyudskoi Isl. Zygomyia kiddi Chandler – Oyatevschina Zygomyia notata Stannius – Oyatevschina, Paleostrov Isl., Vorobyi Zygomyia pseudohumeralis Caspers – Bol. Lelikovskiy Isl., Oyatevschina, Podyelniki, Shunevskiy Isl., Tipinitsy, Turastamozero, Uzkaya Salma, Volkostrov Isl., Vorobyi Zygomyia semifusca Meigen – Turastamozero Zygomyia valida Winnertz – Kurgenitsy, Turastamozero, Vorobyi Reports of the Finnish Environment Institute 40 | 2014 315 Zygomyia zaitzevi Chandler – Bol. Lelikovskiy Isl., Klimenicy, Vorobyi Allodia alternans Zetterstedt – Klimenicy, Turastamozero Allodia anglofennica Edwards – Kizhi Isl., Lipovitsy, Polya, Tambitsy, Verkhnee Myagrozero Allodia czernyi Landrock – Tambitsy Allodia foliifera Strobl – Turastamozero Allodia lugens Wiedemann – Myal’ Isl., Tipinitsy Allodia ornaticollis Meigen – Kurgenitsy Allodia pyxidiiformis A. Zaitzev – Turastamozero Allodiopsis domestica Meigen – Klimenicy, Tambitsy Allodiopsis gracai ŠeЯčík & Papp – Klimenicy Allodiopsis rustica Edwards – Polya, Tipinitsy, Verkhnee Myagrozero Notolopha cristata Staeger – Klimenicy, Lipovitsy, Tambitsy, Tipinitsy, Verkhnee Myagrozero Myrosia maculosa Meigen – Tipinitsy Synplasta karelica A. Zaitzev – Turastamozero Synplasta pseudingeniosa A. Zaitzev – Tambitsy Synplasta sintenisi Lackschewitz – Myal’ Isl. Anatella lavomaculata Edwards – Volkostrov Isl. Brachypeza armata Winnertz – Kopanets lake Brachypeza bisignata Winnertz – Lyudskoi Isl., Nizhneje Myagrozero Brevicornu bellum Johansen – Turastamozero Brevicornu fasciculatum Lackschewitz – Kizhi Isl., Lyudskoi Isl., Turastamozero, Volkostrov Isl. Brevicornu fuscipenne Staeger – Klimenicy, Turastamozero, Vorobyi Brevicornu griseicolle Staeger – Kosmozero, Turastamozero, Volkostrov Isl., Vorobyi Brevicornu griseolum Zetterstedt – Bol. Lelikovskiy Isl. Brevicornu improvisum A. Zaitzev – Turastamozero Brevicornu nigrofuscum Lundström – Turastamozero Brevicornu parafennicum A. Zaitzev – Turastamozero, Vorobyi Brevicornu serenum Winnertz – Bol. Lelikovskiy Isl., Kopanets lake, Turastamozero Brevicornu sericoma Meigen – Bol. Lelikovskiy Isl., Kizhi Isl., Vavlok Isl. Cordyla brevicornis Staeger – Klimenicy, Paleostrov Isl., Polya, Turastamozero, Vorobyi Cordyla crassicornis Meigen – Lipovitsy, Polya, Tambitsy, Tipinitsy, Turastamozero Cordyla fasciata Meigen – Turastamozero Cordyla issa Edwards – Vorobyi Cordyla laviceps Staeger – Myagrozero, Turastamozero, Uzkaya Salma, Vorobyi Cordyla insons Laštovka et Matile – Lipovitsy, Turastamozero, Vorobyi Cordyla nitens (s. Zaitzev) Winnertz – Tipinitsy, Turastamozero Cordyla nitidula Edwards – Oyatevschina Cordyla parvipalpis Edwards – Turastamozero, Uzkaya Salma Cordyla pseudomurina (in prep.) – Lipovitsy Cordyla pusilla Edwards – Kizhi Isl., Lyudskoi Isl., Polya, Tambitsy, Turastamozero, Vorobyi Cordyla semilava Staeger – Turastamozero Exechia cincta Winnertz – Tipinitsy Exechia coninis Winnertz – Turastamozero, Yu. Oleny Isl. Exechia contaminata Winnertz – Klimenicy, Paleostrov Isl., Polya, Tambitsy, Tipinitsy Exechia dizona Edwards – Tambitsy, Tipinitsy Exechia dorsalis Staeger – Myagrozero, Polya, Tambitsy, Turastamozero, Velikaya Niva Exechia exigua Lundström – Paleostrov Isl., Tipinitsy, Turastamozero ? Exechia macula Chandler – Kurgenitsy 316 Reports of the Finnish Environment Institute 40 | 2014 Exechia nigroscutellata Landrock – Klimenicy, Paleostrov Isl. Exechia parva Lundström – Tambitsy, Turastamozero, Verkhnee Myagrozero Exechia parvula Zetterstedt – Polya, Tipinitsy Exechia pectinivalva Stackelberg – Vorobyi Exechia pseudocincta Strobl – Klimenicy, Tambitsy Exechia repanda Johansen – Turastamozero, Volkostrov Isl. Exechia separata Lundström – Polya, Tipinitsy Exechia seriata Meigen – Klimenicy Exechia spinuligera Lundström – Vorobyi Exechia subfrigida Laštovka & Matile – Polya Exechia unifasciata Lackschewitz – Polya Exechiopsis aemula Plassmann – Turastamozero Exechiopsis crucigera Lundström – Yu. Oleny Isl. Exechiopsis davatchii Matile – Turastamozero Exechiopsis lackschewitziana Stackelberg – Lipovitsy, Tambitsy Exechiopsis praedita Plassmann – Oyatevschina Exechiopsis subulata Winnertz – Verkhnee Myagrozero Pseudobrachypeza helvetica Walker – Polya, Tambitsy, Tipinitsy Pseudorymosia fovea Dziedzicki – Turastamozero Rymosia fasciata Meigen – Turastamozero Rymosia setiger Dziedzicki – Tipinitsy Rymosia signatipes Van der Wulp – Kurgenitsy, Lipovitsy Tarnania fenestralis Meigen – Klimenicy Tarnania tarnanii Dziedzicki – Klimenicy, Lipovitsy, Polya, Tambitsy, Tipinitsy, Turastamozero Bolitophilidae Bolitophila dubia Siebke – Velikaya Niva Bolitophila modesta Lackschewitz – Lipovitsy, Tambitsy, Velikaya Niva Bolitophila nigrolineata Landrock – Polya, Tambitsy, Volkostrov Isl. Bolitophila occlusa Edwards – Klimenicy, Polya Bolitophila saundersi Curtis – Velikaya Niva Keroplatidae Macrocera angulata Meigen – Ernitskiy Isl., Klimenicy, Kuivakhda Isl., Lelikovo, Myal’ Isl. Macrocera centralis Meigen – Klimenicy, Tipinitsy Macrocera fasciata Meigen – Podyelniki Macrocera fascipennis Staeger – Rogachev Isl. Macrocera lutea Meigen – Tipinitsy, Yu. Oleny Isl. Macrocera maculata Meigen – Vikshezero Macrocera parva Lundström – Klimenicy Macrocera phalerata Meigen – Vavlok Isl., Vikshezero Macrocera pilosa Landrock – Velikaya Niva Macrocera stigma Curtis – Klimenicy, Shunevskiy Isl., Vavlok Isl. Macrocera stigmoides Edwards – Podyelniki, Polya Macrocera vittata Meigen – Turastamozero Rocetelion humerale Zetterstedt – Klimenicy Isoneuromyia semirufa Meigen – Podyelniki Keroplatus tipuloides Bosc – Oyatevschina Macrorrhyncha lava Winnertz – Podyelniki, Volkostrov Isl., Vorobyi Neoplatyura lava Macquart – Bol. Lelikovskiy Isl., Kopanets lake, Podyelniki, Uzkaya Salma Orfelia bicolor Macquart – Podyelniki, Turastamozero, Vorobyi Orfelia falcata A. Zaitzev – Lyudskoi Isl. Reports of the Finnish Environment Institute 40 | 2014 317 Orfelia fasciata Meigen – Paleostrov Isl., Vavlok Isl. Orfelia ochracea Meigen – Lipovitsy Pyratula zonata Zetterstedt – Ernitskiy Isl., Kuivakhda Isl., Lelikovo, Lyudskoi Isl., Paleostrov Isl., Sennaya Guba, Vikshezero, Yu. Oleny Isl. Urytalpa dorsalis Staeger – Ernitskiy Isl. Bombyliidae Anthrax anthrax Schrank – Kizhi Isl., Oyatevschina ? Villa paniscus Rossi – Kurgenitsy, Podyelniki, Vorobyi Asilidae Dioctria hyalipennis Fabricius – Eglov Isl., Verkhnee Myagrozero Cyrtopogon lateralis Fallén – Uzkaya Salma Leptogaster cylindrica DeGeer – Vegoruksy Laphria lava L. – Klimenicy, Nizhneje Myagrozero Choerades gilva L. – Kazhma Choerades tenebraus Esipenko – Verkhnee Myagrozero Neoitamus socius Loew – Oyatevschina, Podyelniki, Uzkaya Salma Machimus atricapilus Fallén – Kurgenitsy, Podyelniki, Vorobyi Scenopinidae Scenopinus vitripennis Meigen – Kizhi Isl. Therevidae ? Thereva inornata Verrall – Lipovitsy, Shun’ga Thereva microcephala Loew – Uzkaya Salma Rhagionidae Rhagio annulatus DeGeer – Kainos Isl. Rhagio lineola Fabricius – Bol. Lelikovskiy Isl., Eglov Isl., Kosmozero, Kurgenitsy, Lipovitsy, Myagrozero, Oyatevschina, Podyelniki, Polya, Turastamozero, Vavlok Isl. Rhagio maculatus DeGeer – Eglov Isl., Kainos Isl., Lipovitsy, Polya, Vorobyi, Yu. Oleny Isl. Rhagio scolopaceus L. – Eglov Isl., Ernitskiy Isl., Kizhi Isl., Lelikovo, Lipovitsy, Myagrozero, Polya, Rogachev Isl., Sennaya Guba, Vegoruksy, Vorobyi Chrysopilus nubecula Fallén – Klimenicy, Kosmozero, Kurgenitsy, Oyatevschina, Vorobyi Symphoromyia crassicornis Panzer – Kuzaranda Stratiomyidae Beris morrisi Dale – Eglov Isl., Khvost Isl., Kizhi Isl., Klimenicy, Kosmozero, Lelikovo, Paleostrov Isl., Rogachev Isl., Vavlok Isl., Velikaya Niva, Yu. Oleny Isl. Microchrysa polita L. – Kizhi Isl. Sargus ruipes Wahlberg – Oyatevschina, Polya Stratiomys chamaeleon L. – Velikaya Niva Stratiomys singularior Harris – Shun’ga Odontomyia hydroleon L. – Tolvuya Odontomyia tigrina Fabricius – Sennaya Guba Oplodontha viridula Fabricius – Velikaya Guba Neopachygaster meromelas Dufour – Kopanets lake, Oyatevschina Xylomyidae Xylomya czekanovskii Pleske – Khvost Isl., Klimenicy, Kopanets lake, Podyelniki, Polya, Tambitsy, Tipinitsy Tabanidae Chrysops caecutiens L. – Polya, Uzkaya Salma Chrysops divaricatus Loew – Lipovitsy, Podyelniki, Polya, Turastamozero, Uzkaya Salma, Vikshezero Chrysops nigripes Zetterstedt – Lipovitsy, Polya, Uzkaya Salma Chrysops relictus Meigen – Oyatevschina, Podyelniki, Sennaya Guba, Turastamozero 318 Reports of the Finnish Environment Institute 40 | 2014 Chrysops sepulcralis Fabricius – Vegoruksy Chrysops sp1 – Oyatevschina Chrysops viduatus Fabricius – Lipovitsy, Podyelniki, Polya, Turastamozero, Uzkaya Salma Hybomitra arpadi Szilády – Lipovitsy, Polya, Uzkaya Salma Hybomitra bimaculata Macquart – Lipovitsy, Polya, Turastamozero, Uzkaya Salma Hybomitra borealis Fabricius – Lipovitsy, Polya, Uzkaya Salma Hybomitra coniformis Chvála et Moucha – Lelikovo Hybomitra distinguenda Verrall – Lipovitsy, Polya, Uzkaya Salma Hybomitra kaurii Chvála et Lyneborg – Uzkaya Salma Hybomitra lundbecki Lyneborg – Lipovitsy, Polya, Uzkaya Salma Hybomitra montana Meigen – Uzkaya Salma Hybomitra muehlfeldi Brauer – Lipovitsy, Oyatevschina, Podyelniki, Polya, Turastamozero, Uzkaya Salma Hybomitra nigricornis Zetterstedt – Turastamozero, Volkostrov Isl. ? Tabanus bromius L. – Turastamozero Tabanus glaucopis Meigen – Vorobyi Tabanus maculicornis Zetterstedt – Lipovitsy, Polya, Uzkaya Salma Atylotus fulvus Meigen – Kopanets lake, Podyelniki, Uzkaya Salma Heptatoma pellucens Fabricius – Oyatevschina, Uzkaya Salma Haematopota pluvialis L. – Oyatevschina, Podyelniki, Polya, Turastamozero Xylophagidae Xylophagus ater Meigen – Kizhi Isl., Vorobyi Xylophagus cinctus DeGeer – Velikaya Niva Brachystomatidae Gloma fuscipennis Meigen – Lipovitsy Heleodromia immaculata Haliday – Lipovitsy Trichopeza albocincta Boheman – Yu. Oleny Isl. Dolichopodidae Dolichopus claviger Stannius – Khvost Isl., Kopanets lake, Nizhneje Myagrozero, Podyelniki Dolichopus discifer Stannius – Bol. Lelikovskiy Isl., Eglov Isl., Klimenicy, Kopanets lake, Kurgenitsy, Lelikovo, Lipovitsy, Myagrozero, Oyatevschina, Podyelniki, Polya, Uzkaya Salma, Vegoruksy, Verkhnee Myagrozero, Vorobyi Dolichopus lepidus Staeger – Ernitskiy Isl., Lelikovo, Lyudskoi Isl., Nizhneje Myagrozero, Podyelniki Dolichopus nigripes Fallén – Ernitskiy Isl. Dolichopus nitidus Fallén – Ernitskiy Isl., Kizhi Isl., Klimenicy, Sennaya Guba, Vegoruksy Dolichopus notatus Staeger – Kizhi Isl. Dolichopus pennatus Meigen – Oyatevschina, Vorobyi Dolichopus picipes Meigen – Bol. Lelikovskiy Isl., Klimenicy, Kopanets lake Dolichopus plumipes Scopoli – Kizhi Isl., Klimenicy, Kopanets lake, Kurgenitsy, Kuzaranda, Shunevskiy Isl., Tipinitsy, Vegoruksy, Volkostrov Isl. Dolichopus popularis Wiedemann – Eglov Isl. Dolichopus simplex Meigen – Bol. Lelikovskiy Isl., Kizhi Isl., Klimenicy Dolichopus trivialis Haliday – Kosmozero, Vorobyi Dolichopus ungulatus L. – Eglov Isl., Kizhi Isl., Podyelniki, Vorobyi Dolichopus wahlbergi Zetterstedt – Oyatevschina Dolichopus zetterstedti Stenhammar – Eglov Isl., Kurgenitsy, Vegoruksy Hercostomus aerosus Fallén – Bol. Lelikovskiy Isl., Eglov Isl., Ernitskiy Isl., Khvost Isl., Klimenicy, Lelikovo, Lipovitsy, Shunevskiy Isl., Vikshezero Hercostomus angustifrons Staeger – Ernitskiy Isl., Lelikovo, Lyudskoi Isl. Reports of the Finnish Environment Institute 40 | 2014 319 Hercostomus celer Meigen – Vikshezero Hercostomus chalybeus Wiedemann – Eglov Isl., Kizhi Isl., Kurgenitsy, Podyelniki Hercostomus metallicus Stannius – Eglov Isl., Khvost Isl., Klimenicy, Lyudskoi Isl., Polya, Sennaya Guba, Shunevskiy Isl., Vikshezero Hercostomus nigrilamellatus Macquart – Shunevskiy Isl. Hercostomus sahlbergi Zetterstedt – Turastamozero Hydrophorus praecox Lehmann – Kuzaranda Dolichophorus kerteszi Lichtwardt – Lelikovo, Lyudskoi Isl. Rhaphium crassipes Meigen – Oyatevschina, Vorobyi Rhaphium elegantulum Meigen – Kopanets lake Rhaphium lanceolatum Loew – Kizhi Isl. ? Rhaphium riparium Meigen – Vorobyi Syntormon bicolorellum Zetterstedt – Vorobyi Syntormon tarsatus Fallén – Kurgenitsy Neurigona abdominalis Fallén – Eglov Isl., Kizhi Isl. Neurigona pallida Fallén – Bol. Lelikovskiy Isl., Kainos Isl., Kopanets lake, Kosmozero, Kurgenitsy, Lipovitsy, Myagrozero, Podyelniki, Polya Neurigona quadrifasciata Fabricius – Eglov Isl., Khvost Isl., Klimenicy, Kopanets lake, Kurgenitsy, Oyatevschina, Shunevskiy Isl., Turastamozero, Vavlok Isl., Volkostrov Isl., Yu. Oleny Isl. Chrysotus cilipes Meigen – Nizhneje Myagrozero Chrysotus neglectus Wiedemann – Vorobyi Campsicnemus curvipes Fallén – Bol. Lelikovskiy Isl. Campsicnemus scambus Fallén – Bol. Lelikovskiy Isl., Lelikovo, Lipovitsy, Myagrozero, Podyelniki, Polya, Sennaya Guba, Shunevskiy Isl., Tambitsy, Tipinitsy, Vorobyi Empididae Rhamphomyia anomalina Zetterstedt – Vorobyi Rhamphomyia galacoptera Strobl – Kizhi Isl. Rhamphomyia lividiventris Zetterstedt – Uzkaya Salma ? Rhamphomyia modesta Wahlberg – Yu. Oleny Isl. Rhamphomyia nigripennis Fabricius – Khvost Isl., Lelikovo, Yu. Oleny Isl. Rhamphomyia nigripes Strobl – Vikshezero Rhamphomyia obscuripennis Meigen – Ernitskiy Isl., Kuivakhda Isl., Sennaya Guba Rhamphomyia sp2 (cf. hybotina) – Paleostrov Isl. Rhamphomyia spinipes Fallén – Tambitsy Rhamphomyia stigmosa Macquart – Vikshezero Rhamphomyia sulcatina Collin – Oyatevschina ? Rhamphomyia tipularia Fallén – Kopanets lake Rhamphomyia trigemina Oldenberg – Kizhi Isl. Rhamphomyia umbripennis Meigen – Ernitskiy Isl., Kizhi Isl., Lyudskoi Isl., Oyatevschina, Vorobyi Empis bicuspidata Collin – Lelikovo Empis borealis L. – Kizhi Isl., Klimenicy Empis livida L. – Vorobyi Empis prodromus Loew – Lelikovo Empis stercorea L. – Eglov Isl. Empis tessellata Fabricius – Eglov Isl., Kizhi Isl., Kurgenitsy, Lelikovo, Oyatevschina, Paleostrov Isl., Rogachev Isl., Sennaya Guba, Vegoruksy, Vikshezero, Vorobyi, Yu. Oleny Isl. Hilara sp1 (cf. canescens) – Vegoruksy Chelipoda albiseta Zetterstedt – Kosmozero, Yu. Oleny Isl. Chelipoda inexpactata Tuomikoski – Lipovitsy Chelipoda vocatoria Fallén – Lipovitsy 320 Reports of the Finnish Environment Institute 40 | 2014 Phyllodromia melanocephala Fabricius – Bol. Lelikovskiy Isl., Khvost Isl., Kopanets lake, Podyelniki ? Hemerodromia melangyna Collin – Kurgenitsy, Yu. Oleny Isl. Hemerodromia raptoria Meigen – Kurgenitsy, Vorobyi Hybotidae Hybos femoratus Müller – Eglov Isl., Ernitskiy Isl., Klimenicy, Lipovitsy, Polya Hybos grossipes L. – Bol. Lelikovskiy Isl., Eglov Isl., Khvost Isl., Klimenicy, Kopanets lake, Kosmozero, Kurgenitsy, Kuzaranda, Lipovitsy, Myagrozero, Nizhneje Myagrozero, Oyatevschina, Paleostrov Isl., Polya, Tambitsy, Tipinitsy, Turastamozero, Uzkaya Salma, Verkhnee Myagrozero, Volkostrov Isl., Vorobyi Trichinomyia lavipes Meigen – Lipovitsy, Myagrozero, Tambitsy, Turastamozero, Uzkaya Salma, Vorobyi Trichina bilobata Collin – Lipovitsy Trichina clavipes Meigen – Kosmozero Bicellaria intermedia Lundbeck – Bol. Lelikovskiy Isl., Kurgenitsy Bicellaria nigra Meigen – Kuivakhda Isl., Verkhnee Myagrozero Oedalea holmgreni Zetterstedt – Vikshezero Oedalea stigmatella Zetterstedt – Lyudskoi Isl. Oedalea zetterstedti Collin – Lipovitsy Euthyneura myrtilli Macquart – Lipovitsy, Velikaya Niva Ocydromia glabricula Fallén – Paleostrov Isl., Podyelniki, Tambitsy, Tipinitsy, Velikaya Niva Leptopeza borealis Zetterstedt – Kurgenitsy, Oyatevschina Leptopeza lavipes Meigen – Eglov Isl., Klimenicy, Kuivakhda Isl., Podyelniki, Vorobyi ? Platypalpus calceatus Meigen – Vorobyi Platypalpus candicans Fallén – Eglov Isl., Khvost Isl. Platypalpus ciliaris Fallén – Khvost Isl., Klimenicy, Kopanets lake, Polya, Tambitsy, Uzkaya Salma, Vorobyi Platypalpus cursitans Fabricius – Kizhi Isl., Lyudskoi Isl., Oyatevschina, Sennaya Guba, Tolvuya, Vorobyi ? Platypalpus dificilis Frey – Bol. Lelikovskiy Isl. Platypalpus ecalceatus Zetterstedt – Eglov Isl., Ernitskiy Isl., Khvost Isl., Klimenicy, Kuivakhda Isl., Lyudskoi Isl., Myagrozero, Myal’ Isl., Polya Platypalpus exilis Meigen – Eglov Isl., Klimenicy, Paleostrov Isl., Vavlok Isl. Platypalpus longicornis Meigen – Turastamozero, Vorobyi ? Platypalpus longicornoides Chvála – Sennaya Guba Platypalpus luteus Meigen – Kainos Isl., Lipovitsy, Podyelniki, Polya, Vorobyi Platypalpus macula Zetterstedt – Lipovitsy, Vavlok Isl. Platypalpus major Zetterstedt – Kopanets lake, Tipinitsy Platypalpus nigritarsis Fallén – Myagrozero Platypalpus nonstriatus Strobl – Klimenicy Platypalpus pectoralis Fallén – Bol. Lelikovskiy Isl., Podyelniki, Polya, Tipinitsy, Turastamozero, Uzkaya Salma, Verkhnee Myagrozero Platypalpus pseudorapidus Kovalev – Kizhi Isl., Oyatevschina, Vorobyi Platypalpus scandinavicus Chvála – Oyatevschina Platypalpus stigmatellus Zetterstedt – Klimenicy, Tambitsy ? Platypalpus tuomikoskii Chvála – Turastamozero Tachypeza fennica Tuomikoski – Vikshezero, Vorobyi Tachypeza fuscipennis Fallén – Vorobyi Tachypeza heeri Zetterstedt – Lipovitsy, Oyatevschina, Polya, Volkostrov Isl. Tachypeza nubila Meigen – Eglov Isl., Kurgenitsy, Lipovitsy, Polya, Vavlok Isl., Vorobyi Tachypeza truncorum Fallén – Lipovitsy, Polya Reports of the Finnish Environment Institute 40 | 2014 321 Tachydromia aemula Loew – Khvost Isl. Drapetis parilis Collin – Nizhneje Myagrozero Lonchopteridae Lonchoptera fallax de Meijere – Klimenicy, Lelikovo, Lyudskoi Isl. Lonchoptera lutea Panzer – Kizhi Isl., Vegoruksy, Vorobyi Platypezidae Microsania pectipennis Meigen – Bol. Lelikovskiy Isl., Klimenicy Callomyia amoena Meigen – Klimenicy, Lyudskoi Isl., Myal’ Isl. Callomyia speciosa Meigen – Eglov Isl., Lyudskoi Isl. Agathomyia elegantula Fallén – Lipovitsy Polyporivora ornata Meigen – Polya Polyporivora picta Meigen – Tipinitsy Platypeza consobrina Zetterstedt – Myagrozero Platypeza fasciata Meigen – Myagrozero Platypezina connexa Boheman – Tipinitsy Phoridae Anevrina thoracica Meigen – Kizhi Isl. Pipunculidae Chalarus holosericeus Meigen – Podyelniki ? Chalarus spurius Fallén – Podyelniki Verrallia aucta Fallén – Eglov Isl., Khvost Isl., Rogachev Isl., Turastamozero Nephrocerus lavicornis Zetterstedt – Oyatevschina Tomosvaryella geniculata Meigen – Lipovitsy Dorylomorpha maculata Walker – Kurgenitsy, Podyelniki, Verkhnee Myagrozero ? Cephalops semifumosus Kowarz – Turastamozero ? Eudorylas terminalis Thomson – Turastamozero Syrphidae Paragus albifrons Fallén – Vorobyi Paragus bicolor Fabricius – Eglov Isl., Vorobyi Paragus initimus Goeldlin – Sennaya Guba, Tolvuya, Vikshezero Paragus pecchiolii Rondani – Vikshezero Paragus tibialis Fallén – Oyatevschina Baccha elongata Fabricius – Bol. Lelikovskiy Isl., Eglov Isl., Lelikovo, Paleostrov Isl., Polya, Tipinitsy, Turastamozero, Velikaya Guba, Verkhnee Myagrozero, Volkostrov Isl. Platycheirus albimanus Fabricius – Kuivakhda Isl., Kurgenitsy, Lyudskoi Isl., Vikshezero Platycheirus angustatus Zetterstedt – Sennaya Guba Platycheirus clypeatus Meigen – Kosmozero, Lelikovo, Lyudskoi Isl., Nizhneje Myagrozero, Sennaya Guba, Tipinitsy Platycheirus europaeus Goeldlin, Maibach & Speight – Vikshezero Platycheirus fulviventris Macquart – Eglov Isl., Rogachev Isl. Platycheirus granditarsus Förster – Bol. Lelikovskiy Isl., Klimenicy, Kurgenitsy, Nizhneje Myagrozero, Podyelniki, Turastamozero, Volkostrov Isl. Platycheirus immarginatus Zetterstedt – Kosmozero Platycheirus occultus Goeldlin, Maibach & Speight – Turastamozero Platycheirus peltatus Meigen – Kizhi Isl., Velikaya Niva Platycheirus rosarum Fabricius – Eglov Isl., Kizhi Isl. Platycheirus scambus Staeger – Kopanets lake, Velikaya Niva Platycheirus scutatus Meigen – Kosmozero, Kurgenitsy Xanthandrus comtus Harris – Tipinitsy, Uzkaya Salma Melanostoma mellinum L. – Eglov Isl., Khvost Isl., Kopanets lake, Kosmozero, Kurgenitsy, Kuzaranda, Lelikovo, Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Turastamozero, Velikaya Niva, Verkhnee Myagrozero, Vikshezero, Volkostrov Isl., Vorobyi 322 Reports of the Finnish Environment Institute 40 | 2014 Melanostoma scalare Fabricius – Eglov Isl., Ernitskiy Isl., Klimenicy, Lelikovo, Lipovitsy, Lyudskoi Isl., Oyatevschina, Paleostrov Isl., Polya, Sennaya Guba, Tipinitsy, Turastamozero, Uzkaya Salma, Vorobyi Melangyna compositarum Verrall – Turastamozero, Verkhnee Myagrozero Melangyna umbellatarum Fabricius – Khvost Isl., Kizhi Isl., Vorobyi Meligramma guttata Fallén – Klimenicy Leucozona glaucia L. – Kurgenitsy, Nizhneje Myagrozero, Turastamozero, Velikaya Niva, Verkhnee Myagrozero, Vorobyi Leucozona inopinata Doczkal – Uzkaya Salma Leucozona laternaria Müller – Khvost Isl., Kurgenitsy, Nizhneje Myagrozero, Paleostrov Isl., Rogachev Isl. Leucozona lucorum L. – Kizhi Isl., Oyatevschina, Velikaya Niva Epistrophe lava Doczkal & Schmid – Eglov Isl. Epistrophe grossulariae Meigen – Turastamozero, Vorobyi Eriozona erratica L. – Tambitsy Scaeva pyrastri L. – Vegoruksy, Velikaya Niva, Vorobyi Scaeva selenitica Meigen – Kurgenitsy, Nizhneje Myagrozero, Turastamozero, Verkhnee Myagrozero Meliscaeva cinctella Zetterstedt – Lipovitsy, Turastamozero, Vikshezero, Vorobyi Didea fasciata Macquart – Lipovitsy, Uzkaya Salma Didea intermedia Loew – Eglov Isl., Kurgenitsy, Turastamozero, Vegoruksy Dasysyrphus hilaris Zetterstedt – Eglov Isl., Vikshezero Dasysyrphus pinastri DeGeer – Eglov Isl., Vikshezero Dasysyrphus tricinctus Fallén – o. B.Klimeckiy, Klimenicy, Kopanets lake, Nizhneje Myagrozero, Oyatevschina, Turastamozero, Velikaya Niva, Vorobyi Dasysyrphus venustus Meigen – Eglov Isl., Vikshezero Episyrphus balteatus DeGeer – Kizhi Isl., Kosmozero, Oyatevschina, Turastamozero, Uzkaya Salma, Vikshezero, Vorobyi Eupeodes bucculatus Rondani – Turastamozero, Vorobyi Eupeodes corollae Fabricius – Nizhneje Myagrozero Eupeodes latifasciatus Macquart – Klimenicy Eupeodes lundbecki Soot Ryen – Velikaya Niva, Vorobyi Eupeodes nitens Zetterstedt – Turastamozero Syrphus admirandus Goeldlin – Vikshezero Syrphus ribesii L. – Eglov Isl., Khvost Isl., Turastamozero, Vikshezero, Vorobyi Syrphus torvus Osten-Sacken – Eglov Isl., Kizhi Isl., Nizhneje Myagrozero, Vorobyi Syrphus vitripennis Meigen – Eglov Isl., Vikshezero Parasyrphus annulatus Zetterstedt – Velikaya Niva Parasyrphus lineolus Zetterstedt – Nizhneje Myagrozero Parasyrphus nigritarsis Zetterstedt – Vikshezero Sphaerophoria batava Goeldlin – Eglov Isl., Podyelniki, Vikshezero Sphaerophoria interrupta Fabricius – Kizhi Isl., Kosmozero, Lyudskoi Isl., Vikshezero, Vorobyi Sphaerophoria menthastri L. – Kuzaranda, Paleostrov Isl. Sphaerophoria philantha Meigen – Kurgenitsy, Sennaya Guba, Vikshezero Sphaerophoria scripta L. – Eglov Isl., Kizhi Isl., Klimenicy, Kosmozero, Kuzaranda, Lelikovo, Lyudskoi Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Rogachev Isl., Sennaya Guba, Tipinitsy, Turastamozero, Vertilovo, Vikshezero, Volkostrov Isl., Vorobyi Sphaerophoria taeniata Meigen – Kizhi Isl., Kuzaranda, Podyelniki, Rogachev Isl., Vorobyi Sphaerophoria virgata Goeldlin – Eglov Isl., Tipinitsy Reports of the Finnish Environment Institute 40 | 2014 323 Xanthogramma pedissequum Harris – Rogachev Isl., Vorobyi Xanthogramma stackelbergi Violovitsh – Khvost Isl., Rogachev Isl. Ceriana conopsoides L. – Turastamozero Chrysotoxum arcuatum L. – Velikaya Guba, Vikshezero Chrysotoxum bicinctum L. – Eglov Isl., Khvost Isl., Kuzaranda, Rogachev Isl., Turastamozero, Vikshezero, Vorobyi Chrysotoxum fasciolatum DeGeer – Kosmozero Chrysotoxum festivum L. – Shun’ga Rhingia borealis Ringdahl – Oyatevschina, Velikaya Niva Rhingia campestris Meigen – Kizhi Isl., Tolvuya Hammerschmidtia ferruginea Fallén – Klimenicy, Velikaya Niva Neoascia geniculata Meigen – Vikshezero Neoascia tenur Harris – Eglov Isl., Ernitskiy Isl., Kizhi Isl., Klimenicy, Kurgenitsy, Lelikovo, Lyudskoi Isl., Sennaya Guba, Vikshezero Sphegina clunipes Fallén – Klimenicy, Kopanets lake, Lipovitsy Sphegina sibirica Stackelberg – Kizhi Isl., Klimenicy, Tipinitsy, Vavlok Isl., Vikshezero Pipizella certa Violovitsh – Rogachev Isl. Pipizella viduata L. – Klimenicy, Kuzaranda, Lyudskoi Isl., Rogachev Isl., Turastamozero, Vikshezero Pipiza austriaca Meigen – Lelikovo, Velikaya Niva Pipiza bimaculata Meigen – Lelikovo, Paleostrov Isl. Pipiza noctiluca L. – Velikaya Niva, Vikshezero, Yu. Oleny Isl. Pipiza quadrimaculata Panzer – Velikaya Guba, Vikshezero Orthonevra erythrogona Malm – Sennaya Guba Orthonevra stackelbergi Thompson & Torp – Klimenicy, Vikshezero ? Chrysogaster virescens Loew – Sennaya Guba Cheilosia carbonaria Egger – Oyatevschina, Vikshezero Cheilosia lavipes Panzer – Kizhi Isl., Tolvuya Cheilosia frontalis Loew – Kizhi Isl. Cheilosia gigantea Zetterstedt – Klimenicy Cheilosia illustrata Harris – Eglov Isl., Kizhi Isl., Kosmozero, Kurgenitsy, Nizhneje Myagrozero, Oyatevschina, Rogachev Isl., Vorobyi Cheilosia impressa Loew – Ernitskiy Isl. Cheilosia longula Zetterstedt – Myagrozero, Nizhneje Myagrozero, Turastamozero, Velikaya Niva Cheilosia mutabilis Fallén – Kurgenitsy, Podyelniki, Rogachev Isl., Turastamozero, Vegoruksy, Velikaya Niva, Verkhnee Myagrozero, Volkostrov Isl. Cheilosia pagana Meigen – Eglov Isl., Kizhi Isl., Kurgenitsy, Lelikovo, Nizhneje Myagrozero, Oyatevschina, Podyelniki, Rogachev Isl., Tolvuya, Vikshezero, Vorobyi Cheilosia pubera Zetterstedt – Klimenicy, Oyatevschina, Sennaya Guba Cheilosia rotundiventris Becker – Kizhi Isl. Cheilosia scutellata Fallén – Velikaya Niva Cheilosia sootryeni Nielsen – Vikshezero Cheilosia variabilis Panzer – Kainos Isl. Cheilosia vernalis Fallén – Kizhi Isl., Lelikovo, Nizhneje Myagrozero, Velikaya Niva, Vorobyi ? Cheilosia vicina Zetterstedt – Vikshezero Cheilosia vulpina Meigen – Kizhi Isl., Klimenicy Chamaesyrphus scaevoides Fallén – Ernitskiy Isl., Paleostrov Isl. Volucella bombylans L. – Eglov Isl., Khvost Isl., Kizhi Isl., Lelikovo, Lyudskoi Isl., Oyatevschina, Rogachev Isl., Sennaya Guba, Volkostrov Isl. 324 Reports of the Finnish Environment Institute 40 | 2014 Volucella pellucens L. – Eglov Isl., Khvost Isl., Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Turastamozero Sericomyia lappona L. – Podyelniki, Uzkaya Salma Sericomyia nigra Portschinsky – Nizhneje Myagrozero Sericomyia silentis Harris – Dianova Gora, Tambitsy, Turastamozero Eristalis abusiva Collin – Kosmozero, Kurgenitsy Eristalis anthophorina Fallén – Shun’ga Eristalis arbustorum L. – Lipovitsy, Nizhneje Myagrozero, Verkhnee Myagrozero, Vorobyi Eristalis cryptarum Fabricius – Tolvuya Eristalis horticola DeGeer – Kizhi Isl. Eristalis interrupta Poda – Eglov Isl., Nizhneje Myagrozero, Turastamozero, Vegoruksy, Velikaya Niva, Verkhnee Myagrozero, Vorobyi Eristalis intricaria L. – Shun’ga, Vegoruksy Eristalis obscura Loew – Eglov Isl., Kurgenitsy, Nizhneje Myagrozero, Turastamozero, Verkhnee Myagrozero, Vikshezero, Vorobyi Eristalis oestracea L. – Kizhi Isl. Eristalis rupium Fabricius – Oyatevschina, Podyelniki, Turastamozero Eristalis tenax L. – Turastamozero, Vegoruksy Myathropa lorea L. – Eglov Isl., Podyelniki, Turastamozero Anasimyia interpuncta Harris – Lelikovo Anasimyia lineata Fabricius – Eglov Isl., Podyelniki Anasimyia lunulata Meigen – Uzkaya Salma, Vikshezero, Vorobyi Helophilus afinis Wahlberg – Lyudskoi Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Turastamozero, Vavlok Isl., Vikshezero, Volkostrov Isl., Vorobyi Helophilus hybridus Loew – Kurgenitsy, Lelikovo, Lyudskoi Isl., Nizhneje Myagrozero, Podyelniki, Tipinitsy, Turastamozero, Volkostrov Isl. Helophilus pendulus L. – Eglov Isl., Kizhi Isl., Kurgenitsy, Nizhneje Myagrozero, Oyatevschina, Paleostrov Isl., Podyelniki, Rogachev Isl., Shun’ga, Turastamozero, Vegoruksy, Verkhnee Myagrozero, Vikshezero, Volkostrov Isl., Vorobyi Helophilus trivittatus Fabricius – Kizhi Isl., Kurgenitsy Parhelophilus consimilis Malm – Rogachev Isl., Volkostrov Isl., Vorobyi Eumerus strigatus Fallén – Nizhneje Myagrozero, Rogachev Isl., Velikaya Niva Microdon miki Doczkal & Schmid – Kosmozero Criorrchina asilica Fallén – Polya, Velikaya Niva, Vikshezero Blera fallax L. – Lipovitsy, Vegoruksy Xylota abiens Meigen – Podyelniki Xylota caeruleiventris Zetterstedt – Polya Xylota lorum Fabricius – Eglov Isl., Nizhneje Myagrozero, Podyelniki, Vegoruksy, Verkhnee Myagrozero Xylota jakutorum Bagatshanova – Eglov Isl. Xylota meigeniana Stackelberg – Eglov Isl., Klimenicy, Kurgenitsy, Kuzaranda, Nizhneje Myagrozero, Podyelniki, Polya, Turastamozero Xylota segnis L. – Eglov Isl., Kosmozero, Kuzaranda, Nizhneje Myagrozero, Podyelniki, Vegoruksy, Velikaya Niva, Verkhnee Myagrozero Xylota sylvarum L. – Khvost Isl., Lipovitsy, Oyatevschina, Polya, Turastamozero Xylota tarda Meigen – Eglov Isl., Khvost Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Tambitsy, Verkhnee Myagrozero Xylota xanthocnema Collin – Klimenicy, Verkhnee Myagrozero Chalcosyrphus nemorum Fabricius – Kosmozero, Podyelniki, Rogachev Isl., Uzkaya Salma Chalcosyrphus ruipes Loew – Eglov Isl. Reports of the Finnish Environment Institute 40 | 2014 325 Chalcosyrphus valgus Gmelin – Klimenicy Syritta pipiens L. – Kosmozero Spilomyia diophthalma L. – Kurgenitsy, Oyatevschina, Podyelniki, Turastamozero, Uzkaya Salma, Vorobyi Temnostoma angustistriatum Krivosheina – Klimenicy, Kosmozero, Rogachev Isl., Tipinitsy, Vikshezero Temnostoma apiforme Fabricius – Klimenicy, Kosmozero, Rogachev Isl., Turastamozero, Velikaya Niva, Verkhnee Myagrozero, Vikshezero, Yu. Oleny Isl. Temnostoma carens Gaunitz – Eglov Isl. Temnostoma sericomyiaeforme Portschinsky – Eglov Isl., Kizhi Isl., Kurgenitsy, Rogachev Isl., Turastamozero, Uzkaya Salma, Vegoruksy Temnostoma vespiforme L. – Eglov Isl., Klimenicy, Lipovitsy, Oyatevschina, Paleostrov Isl., Rogachev Isl., Turastamozero, Velikaya Niva, Yu. Oleny Isl. Conopidae Conops quadrifasciatus DeGeer – Bol. Lelikovskiy Isl., Oyatevschina, Podyelniki, Turastamozero, Verkhnee Myagrozero, Vorobyi Myopa buccata L. – Vikshezero Sicus ferrugineus L. – Eglov Isl., Kizhi Isl., Kurgenitsy, Nizhneje Myagrozero, Oyatevschina, Podyelniki, Sennaya Guba, Vegoruksy, Verkhnee Myagrozero, Vorobyi Chloropidae Gaurax dubius Macquart – Lelikovo Elachiptera cornuta Fallén – Bol. Lelikovskiy Isl., Eglov Isl., Ernitskiy Isl., Kurgenitsy, Lelikovo, Lyudskoi Isl., Myagrozero, Podyelniki, Sennaya Guba Elachiptera tuberculifera Corti – Lelikovo, Lyudskoi Isl., Myagrozero, Nizhneje Myagrozero Lasiambia palposa Fallén – Vorobyi Siphonella oscinina Fallén – Vorobyi Tricimba cincta s.l. – Vorobyi Oscinella cariciphila Collin – Sennaya Guba Oscinella frit L. – Lelikovo Oscinella pusilla Meigen – Myagrozero, Sennaya Guba Rhopalopterum fasciola Meigen – Kurgenitsy Rhopalopterum femorale Collin – Lelikovo, Lyudskoi Isl. Dicraeus fennicus Duda – Kurgenitsy Meromyza ornata Wiedemann – Lelikovo ? Meromyza pluriseta Peteri – Sennaya Guba Meromyza saltatrix L. – Lelikovo, Sennaya Guba Cetema cereris Fallén – Nizhneje Myagrozero, Podyelniki, Vorobyi Cetema myopinum Loew – Oyatevschina Chlorops frontosus Meigen – Lelikovo Chlorops hypostigma Meigen – Oyatevschina Chlorops limbata Meigen – Ernitskiy Isl., Klimenicy, Kurgenitsy, Lipovitsy, Polya, Sennaya Guba Chlorops meigenii Loew – Eglov Isl., Ernitskiy Isl., Khvost Isl., Klimenicy, Kuivakhda Isl., Lyudskoi Isl., Paleostrov Isl., Polya, Vikshezero Chlorops planifrons Loew – Khvost Isl. Chlorops ringens Loew – Vorobyi ? Chlorops rossicus Smirnov – Polya Chlorops scalaris Meigen – Kuzaranda, Sennaya Guba Chlorops speciosa Meigen – o. B.Klimeckiy, Eglov Isl., Klimenicy, Nizhneje Myagrozero, Podyelniki, Vikshezero Chlorops troglodytes Zetterstedt – o. B.Klimeckiy, Podyelniki, Vorobyi 326 Reports of the Finnish Environment Institute 40 | 2014 Thaumatomyia glabra Meigen – Kuzaranda, Sennaya Guba Thaumatomyia hallandica Anderson – Kuzaranda, Lelikovo, Sennaya Guba Thaumatomyia notata Meigen – Kuzaranda Thaumatomyia rufa Macquart – Lelikovo, Sennaya Guba Thaumatomyia trifasciata Zetterstedt – Kurgenitsy Aphanotrigonum trilineatum Meigen – Sennaya Guba Eribulus nana Zetterstedt – Sennaya Guba Incertella albipalpis Meigen – Kuzaranda Speccafrons halophila Duda – Sennaya Guba Milichiidae Phyllomyza equitans Hendel – Sennaya Guba Phyllomyza securicornis Fallén – Rogachev Isl., Vorobyi Neophyllomyza acyglossa Villeneuve – Lyudskoi Isl. Ephydridae Discomyza incurva Fallén – Lyudskoi Isl. ? Psilopa stackelbergi Nartshuk – Vikshezero Dichaeta caudata Fallén – Lelikovo, Oyatevschina, Sennaya Guba Notiphila aquatica Becker – Klimenicy Nostima picta Fallén – Bol. Lelikovskiy Isl. Limnellia stenhammari Zetterstedt – Myagrozero Coenia curvicauda Meigen – Rogachev Isl., Sennaya Guba, Vikshezero Coenia palustris Fallén – Lelikovo Drosophilidae Stegana baechlii Laštovka & Maca – Turastamozero Stegana furta L. – Ernitskiy Isl., Kizhi Isl., Lelikovo, Rogachev Isl., Sennaya Guba Chymomyza fuscimana Zetterstedt – Turastamozero Drosophila eskoi Lakovaara & Lankinen – Yu. Oleny Isl. Drosophila histrio Meigen – Kainos Isl., Uzkaya Salma, Vavlok Isl. Drosophila littoralis Meigen – Yu. Oleny Isl. Drosophila phalerata Meigen – Tambitsy, Verkhnee Myagrozero Drosophila testacea von Roser – Lipovitsy, Tipinitsy, Turastamozero, Verkhnee Myagrozero, Yu. Oleny Isl. Drosophila transversa Fallén – Kizhi Isl., Polya, Turastamozero, Uzkaya Salma, Verkhnee Myagrozero, Volkostrov Isl., Vorobyi Hirtorosophila trivittata Strobl – Lipovitsy Lordiphosa fenestrarum Fallén – Kizhi Isl. Lordiphosa hexasticha Papp – Podyelniki Lordiphosa nigricolor Strobl – Kizhi Isl. Scaptomyza consimilis Hackman – Tipinitsy, Turastamozero Scaptomyza graminum Fallén – Tipinitsy Scaptomyza pallida Zetterstedt – Kizhi Isl., Nizhneje Myagrozero, Vegoruksy, Vorobyi Diastatidae Diastata nebulosa Fallén – Lipovitsy Chamaemyiidae Chamaemyia aestiva Tanasijtshuk – Ernitskiy Isl., Lelikovo, Myagrozero Chamaemyia elegans Panzer – Ernitskiy Isl., Lelikovo, Lyudskoi Isl., Myal’ Isl., Sennaya Guba Chamaemyia geniculata Zetterstedt – Lelikovo Chamaemyia juncorum Fallén – Kurgenitsy, Lyudskoi Isl., Myagrozero, Sennaya Guba Chamaemyia polystigma Meigen – Kurgenitsy, Lelikovo Lauxaniidae Homoneura interstincta Fallén – Uzkaya Salma Homoneura lamellata Becker – Lipovitsy, Polya, Turastamozero Reports of the Finnish Environment Institute 40 | 2014 327 Homoneura tenera Loew – Khvost Isl., Lyudskoi Isl., Turastamozero, Vikshezero Minettia helvola Becker – Khvost Isl., Lipovitsy, Podyelniki, Polya, Tambitsy, Turastamozero, Verkhnee Myagrozero Minettia loewi Schiner – Ernitskiy Isl., Klimenicy, Lipovitsy, Polya, Tipinitsy Minettia longipennis Fabricius – Eglov Isl., Khvost Isl., Kizhi Isl., Kosmozero, Lipovitsy, Lyudskoi Isl., Myal’ Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Polya, Sennaya Guba, Vegoruksy, Vorobyi Minettia lupulina Fabricius – Kainos Isl., Khvost Isl., Kizhi Isl., Klimenicy, Nizhneje Myagrozero, Oyatevschina, Sennaya Guba, Shunevskiy Isl., Tipinitsy, Verkhnee Myagrozero, Vikshezero, Volkostrov Isl., Vorobyi Tricholauxania praeusta Fallén – Bol. Lelikovskiy Isl., Eglov Isl., Kopanets lake, Oyatevschina, Podyelniki, Shunevskiy Isl., Turastamozero, Verkhnee Myagrozero, Volkostrov Isl. Cnemacantha muscaria Fallén – Kizhi Isl., Sennaya Guba Meiosimyza afinis Zetterstedt – Klimenicy, Myal’ Isl., Verkhnee Myagrozero, Yu. Oleny Isl. Meiosimyza decempunctata Fallén – Eglov Isl., Ernitskiy Isl., Kainos Isl., Myal’ Isl., Nizhneje Myagrozero, Podyelniki, Tipinitsy, Vavlok Isl. Meiosimyza decipiens Loew – Khvost Isl., Klimenicy, Sennaya Guba, Uzkaya Salma Meiosimyza illota Loew – Kizhi Isl., Vikshezero Meiosimyza mihalyii Papp – Vorobyi Meiosimyza platycephala Loew – Lipovitsy, Lyudskoi Isl., Podyelniki Meiosimyza rorida Fallén – Bol. Lelikovskiy Isl., Eglov Isl., Ernitskiy Isl., Kainos Isl., Kizhi Isl., Klimenicy, Kopanets lake, Kuivakhda Isl., Kurgenitsy, Myal’ Isl., Podyelniki, Polya, Sennaya Guba, Shunevskiy Isl., Turastamozero, Vavlok Isl., Vegoruksy, Verkhnee Myagrozero, Volkostrov Isl., Yu. Oleny Isl. Meiosimyza subfasciata Zetterstedt – Kizhi Isl., Kurgenitsy, Vikshezero Poecilolycia vittata Walker – Ernitskiy Isl., Oyatevschina Sapromyza amabilis Frey – Polya Sapromyza basalis Zetterstedt – Lipovitsy, Oyatevschina, Podyelniki, Polya, Tambitsy, Turastamozero, Verkhnee Myagrozero, Yu. Oleny Isl. Sapromyza hyalinata Meigen – Bol. Lelikovskiy Isl., Ernitskiy Isl., Klimenicy, Kopanets lake, Lelikovo, Lipovitsy, Lyudskoi Isl., Myagrozero, Myal’ Isl., Oyatevschina, Paleostrov Isl., Podyelniki, Polya, Rogachev Isl., Sennaya Guba, Shunevskiy Isl., Turastamozero, Vavlok Isl., Velikaya Niva, Volkostrov Isl., Vorobyi, Yu. Oleny Isl. Sapromyza opaca Becker – Vorobyi Sapromyza sexpunctata Meigen – Khvost Isl., Kosmozero, Nizhneje Myagrozero, Oyatevschina, Podyelniki, Turastamozero, Vorobyi Sapromyza zetterstedti Hendel – Lipovitsy, Uzkaya Salma Calliopum aeneum Fallén – Kuzaranda Calliopum elisae Meigen – Kuzaranda, Nizhneje Myagrozero, Sennaya Guba, Tipinitsy, Turastamozero Lauxania cylindricornis Fabricius – Ernitskiy Isl., Kainos Isl., Kizhi Isl., Kurgenitsy, Kuzaranda, Lelikovo, Lyudskoi Isl., Nizhneje Myagrozero, Sennaya Guba, Tolvuya, Uzkaya Salma, Vavlok Isl., Vegoruksy, Vikshezero, Vorobyi Micropezidae Rainieria latifrons Loew – Lipovitsy Micropeza corrigiolata L. – Tolvuya Neriidae Neria cibaria L. – Eglov Isl. Neria commutata Czerny – Eglov Isl., Ernitskiy Isl., Lelikovo, Paleostrov Isl., Rogachev Isl., Tipinitsy Acartophthalmidae Acartophthalmus bicolor Oldenberg – Lyudskoi Isl. 328 Reports of the Finnish Environment Institute 40 | 2014 Anthomyzidae ? Anthomyza dissors Collin – Kopanets lake Anthomyza gracilis Fallén – Kizhi Isl. Clusiidae Hendelia beckeri Czerny – Lyudskoi Isl., Shunevskiy Isl., Vikshezero Clusiodes albimanus Meigen – Kopanets lake, Lipovitsy, Shunevskiy Isl., Turastamozero Clusiodes apicalis Zetterstedt – Ernitskiy Isl., Uzkaya Salma Clusiodes geomyzinus Fallén – Oyatevschina Clusiodes pictipes Zetterstedt – Oyatevschina, Vorobyi Clusiodes ruicollis Meigen – Lyudskoi Isl. Clusia lava Meigen – Klimenicy, Lipovitsy, Oyatevschina, Polya, Uzkaya Salma, Vikshezero Megamerinidae Megamerina dolium Fabricius – Kopanets lake, Kurgenitsy, Polya, Vikshezero Odiniidae Odinia ornata Zetterstedt – Turastamozero Opomyzidae Anomalochaeta guttipennis Zetterstedt – Shunevskiy Isl. Opomyza punctella Fallén – Podyelniki Geomyza hackmani Nartshuk – Nizhneje Myagrozero Geomyza tripunctata Fallén – Lyudskoi Isl. Pallopteridae Temnosira saltuum L. – Kizhi Isl., Myal’ Isl., Paleostrov Isl., Rogachev Isl., Sennaya Guba, Vikshezero Toxoneura modesta Meigen – Nizhneje Myagrozero Toxoneura trimacula Meigen – Podyelniki, Tipinitsy Dryomyzidae Dryomyza decrepita Zetterstedt – Ernitskiy Isl., Klimenicy, Vorobyi Neuroctena anilis Fallén – Bol. Lelikovskiy Isl., Kizhi Isl., Rogachev Isl., Yu. Oleny Isl. Phaeomyiidae Pelidnoptera fuscipennis Meigen – Turastamozero Sciomyzidae Pherbellia albocostata Fallén – Klimenicy, Lipovitsy, Oyatevschina, Podyelniki, Polya, Turastamozero, Uzkaya Salma Pherbellia alpina Frey – Lipovitsy Pherbellia argyra Verbeke – Lelikovo, Sennaya Guba Pherbellia brunnipes Meigen – Sennaya Guba Pherbellia dubia Fallén – Ernitskiy Isl., Kizhi Isl., Lipovitsy, Podyelniki, Vorobyi Pherbellia griseola Fallén – Bol. Lelikovskiy Isl., Kazhma, Lelikovo, Sennaya Guba Pherbellia obtusa Fallén – Kizhi Isl., Shunevskiy Isl., Uzkaya Salma, Vavlok Isl. Pherbellia pallidiventris Fallén – Kopanets lake, Kosmozero, Lipovitsy, Paleostrov Isl., Podyelniki, Velikaya Niva Pherbellia schoenherri Fallén – Kurgenitsy, Vorobyi Pherbellia sordida Hendel – Kurgenitsy, Sennaya Guba, Shunevskiy Isl. Pherbellia ventralis Fallén – Kurgenitsy Pteromicra angustipennis Staeger – Ernitskiy Isl. Pteromicra glabricula Fallén – Ernitskiy Isl., Sennaya Guba, Shunevskiy Isl., Vikshezero Colobaea distincta Meigen – Shunevskiy Isl. Renocera pallida Fallén – Ernitskiy Isl., Klimenicy, Shunevskiy Isl., Vikshezero Renocera strobli Hendel – Vikshezero Anticheta atriseta Loew – Shunevskiy Isl., Vikshezero Ectinocera borealis Zetterstedt – Uzkaya Salma Reports of the Finnish Environment Institute 40 | 2014 329 Tetanocera amurensis Hendel – Klimenicy Tetanocera arrogans Meigen – Ernitskiy Isl., Khvost Isl., Kizhi Isl., Klimenicy, Kurgenitsy, Lelikovo, Sennaya Guba, Tolvuya, Vegoruksy Tetanocera elata Fabricius – Bol. Lelikovskiy Isl., Kizhi Isl., Podyelniki, Sennaya Guba, Tipinitsy, Velikaya Niva, Volkostrov Isl., Vorobyi Tetanocera ferruginea Fallén – Kizhi Isl., Klimenicy, Tipinitsy, Vorobyi Tetanocera freyi Stackelberg – Kurgenitsy, Tipinitsy, Volkostrov Isl. Tetanocera fuscinervis Zetterstedt – Ernitskiy Isl., Lelikovo, Lyudskoi Isl. Tetanocera hyalipennis von Roser – Kurgenitsy, Vorobyi Tetanocera montana Day – Kazhma, Kurgenitsy Tetanocera phyllophora Melander – Ernitskiy Isl., Kizhi Isl., Myagrozero, Nizhneje Myagrozero, Tipinitsy, Verkhnee Myagrozero Tetanocera robusta Loew – Bol. Lelikovskiy Isl., Kurgenitsy, Rogachev Isl., Shunevskiy Isl., Tipinitsy Euthycera chaerophylli Fabricius – Nizhneje Myagrozero Trypetoptera punctulata Scopoli – Bol. Lelikovskiy Isl., Dianova Gora, Khvost Isl., Kurgenitsy, Lipovitsy, Myagrozero, Podyelniki, Tipinitsy, Turastamozero, Vegoruksy, Velikaya Guba, Velikaya Niva, Vorobyi, Yu. Oleny Isl. Pherbina coryleti Scopoli – Bol. Lelikovskiy Isl., Ernitskiy Isl., Kizhi Isl., Kurgenitsy, Tipinitsy Psacadina zernyi Mayer – Sennaya Guba Elgiva cucularia L. – Kurgenitsy, Sennaya Guba Ilione lineata Fallén – Kurgenitsy, Vorobyi Hydromya dorsalis Fabricius – Vikshezero Limnia paludicola Elberg – Kurgenitsy, Oyatevschina, Polya, Tipinitsy, Uzkaya Salma, Velikaya Guba, Verkhnee Myagrozero Limnia unguicornis Scopoli – Nizhneje Myagrozero, Rogachev Isl. Sepedon spinipes Scopoli – Kizhi Isl., Klimenicy, Lelikovo, Sennaya Guba, Volkostrov Isl. Dichetophora inlandica Verbeke – Volkostrov Isl. Tetanura pallidiventris Fallén – Klimenicy Sepsidae Themira annulipes Meigen – Kizhi Isl., Kuzaranda, Nizhneje Myagrozero, Oyatevschina, Vorobyi Themira germanica Duda – Bol. Lelikovskiy Isl. Themira leachi Meigen – Nizhneje Myagrozero Nemopoda nitidula Fallén – Rogachev Isl., Vikshezero Sepsis cynipsea L. – Kizhi Isl., Kuzaranda, Sennaya Guba Sepsis orthocnemis Frey – Myagrozero, Nizhneje Myagrozero Sepsis punctum Fabricius – Bol. Lelikovskiy Isl., Kizhi Isl., Nizhneje Myagrozero, Vikshezero Heleomyzidae ? Borboropsis puberula Zetterstedt – Vorobyi Neoleria ruiceps Zetterstedt – Myagrozero Morpholeria ruicornis Meigen – Bol. Lelikovskiy Isl. Scoliocentra amplicornis Czerny – Kurgenitsy, Turastamozero Suillia apicalis Loew – Khvost Isl., Turastamozero Suillia atricornis Meigen – Bol. Lelikovskiy Isl., Klimenicy, Lipovitsy, Paleostrov Isl., Polya, Tambitsy, Tipinitsy, Turastamozero, Verkhnee Myagrozero, Vikshezero, Yu. Oleny Isl. Suillia bicolor Zetterstedt – Bol. Lelikovskiy Isl., Klimenicy, Kopanets lake, Lipovitsy, Myagrozero, Paleostrov Isl., Polya, Tambitsy, Tipinitsy, Turastamozero, Uzkaya Salma, Vavlok Isl., Vegoruksy, Verkhnee Myagrozero, Volkostrov Isl., Yu. Oleny Isl. 330 Reports of the Finnish Environment Institute 40 | 2014 Suillia lava Meigen – Eglov Isl., Nizhneje Myagrozero, Oyatevschina, Turastamozero, Uzkaya Salma, Vorobyi Suillia lavifrons Zetterstedt – Bol. Lelikovskiy Isl., Klimenicy, Polya, Tambitsy Suillia fuscicornis Zetterstedt – Myal’ Isl., Paleostrov Isl., Podyelniki, Tambitsy, Turastamozero, Verkhnee Myagrozero, Yu. Oleny Isl. Suillia humilis Meigen – Bol. Lelikovskiy Isl., Lipovitsy, Uzkaya Salma, Verkhnee Myagrozero, Vorobyi Suillia laevifrons Loew – Bol. Lelikovskiy Isl., Myagrozero, Podyelniki, Polya, Tipinitsy, Turastamozero, Volkostrov Isl., Vorobyi Suillia mikii Pokorny – Paleostrov Isl. Suillia nemorum Meigen – Turastamozero Suillia parva Loew – Podyelniki, Tipinitsy Suillia quadrilineata Czerny – Verkhnee Myagrozero Sphaeroceridae Crumomyia pedestris Meigen – Klimenicy Psilidae Chamaepsila atra Meigen – Eglov Isl., Kizhi Isl., Klimenicy, Kuivakhda Isl., Lelikovo, Lyudskoi Isl., Sennaya Guba, Vikshezero, Vorobyi Chamaepsila humeralis Zetterstedt – Kizhi Isl., Rogachev Isl., Vorobyi ? Chamaepsila nigra Fallén – Kizhi Isl. Chamaepsila nigricornis Meigen – Vorobyi Chamaepsila pallida Fallén – Kurgenitsy Chamaepsila pectoralis Meigen – Kopanets lake, Podyelniki ? Chamaepsila rosae Fabricius – Kizhi Isl., Vorobyi Psila imetaria L. – Eglov Isl., Khvost Isl., Rogachev Isl. Psila merdaria Collin – Sennaya Guba, Vikshezero Loxocera nigrifrons Macquart – Myal’ Isl. Chyliza vittata Meigen – Kosmozero Tanypezidae Strongylophthalmyia pictipes Frey – Kopanets lake, Polya, Vavlok Isl. Strongylophthalmyia ustulata Zetterstedt – Bol. Lelikovskiy Isl., Kopanets lake, Lipovitsy, Podyelniki, Polya Tanypeza longimana Fallén – Kopanets lake, Nizhneje Myagrozero, Podyelniki, Tipinitsy Lonchaeidae ? Dasiops occultus Collin – Vavlok Isl. Lonchaea laxa Collin – Uzkaya Salma Lonchaea patens Collin – Verkhnee Myagrozero Ulidiidae Homalocephala angustata Wahlberg – Podyelniki, Vegoruksy, Verkhnee Myagrozero, Vikshezero Homalocephala biumbrata Wahlberg – Kurgenitsy, Podyelniki, Tambitsy Melieria crassipennis Fabricius – Bol. Lelikovskiy Isl. Herina frondescentiae L. – Kuzaranda Tephritidae Urophora cuspidata Meigen – Lelikovo Urophora jaceana Hering – Lelikovo, Rogachev Isl., Sennaya Guba ? Urophora mauritanica Macquart – Vikshezero ? Urophora solsticialis L. – Lelikovo, Nizhneje Myagrozero, Oyatevschina, Sennaya Guba, Vorobyi Urophora stigma Loew – Kuzaranda, Sennaya Guba Rhagoletis cerasi L. – Nizhneje Myagrozero, Oyatevschina, Podyelniki, Vorobyi Reports of the Finnish Environment Institute 40 | 2014 331 Euleia heraclei L. – Rogachev Isl. Myoleja lucida Fallén – Kainos Isl., Klimenicy, Rogachev Isl., Vavlok Isl. Cryptaciura rotundiventris Fallén – Eglov Isl., Rogachev Isl., Volkostrov Isl. Chaetorellia jaceae Robineau-Desvoidy – Eglov Isl., Kuzaranda, Lelikovo, Paleostrov Isl., Rogachev Isl., Sennaya Guba, Vikshezero, Vorobyi Chaetorellia loricata Rondani – Eglov Isl., Kizhi Isl., Kurgenitsy, Lelikovo, Lyudskoi Isl., Rogachev Isl., Sennaya Guba Chaetostomella cylindrica Robineau-Desvoidy – Bol. Lelikovskiy Isl., Eglov Isl., Khvost Isl., Kizhi Isl., Kosmozero, Kuzaranda, Lelikovo, Oyatevschina, Podyelniki, Rogachev Isl., Tolvuya, Turastamozero, Vertilovo, Vikshezero, Vorobyi ? Terellia gynaecochroma Hering – Rogachev Isl. Terellia plagiata Dahlbom – Volkostrov Isl., Vorobyi Terellia ruicauda Fabricius – Kurgenitsy Terellia tussilaginis Fabricius – Kazhma Terellia winthemi Meigen – Polya Orellia scorzonerae Robineau-Desvoidy – Lelikovo, Lyudskoi Isl., Sennaya Guba Xyphosia miliaria Schrank – Verkhnee Myagrozero ? Campiglossa doronici Loew – Vikshezero Tephritis angustipennis Loew – Tipinitsy Tephritis conura Loew – Kizhi Isl. Tephritis hyoscyami L. – Polya Hippoboscidae Ornithomya chloropus Bergroth – Klimenicy, Uzkaya Salma Lipoptena cervi L. – Tipinitsy Fanniidae Fannia parva Stein – Vorobyi Fannia polychaeta Stein – Polya Fannia posticata Meigen – Podyelniki Fannia ringdahlana Collin – Vikshezero Fannia rondanii Strobl – Vikshezero Fannia serena Fallén – Rogachev Isl. Fannia sociella Zetterstedt – Nizhneje Myagrozero, Podyelniki, Turastamozero, Verkhnee Myagrozero Fannia spathiophora Malloch – Lyudskoi Isl., Polya, Vikshezero Muscidae Mydaea afinis Myade – Polya, Uzkaya Salma Mydaea humeralis Robineau-Desvoidy – Eglov Isl. Mydaea orthonevra Macquart – Lipovitsy Mydaea ortonevra Macquart – Turastamozero Mydaea urbana Meigen – Turastamozero ? Helina depuncta Fallén – Podyelniki Helina evecta Harris – Eglov Isl., Khvost Isl., Nizhneje Myagrozero, Podyelniki, Polya, Vegoruksy Helina impuncta Fallén – Eglov Isl. Helina pubiseta Zetterstedt – Lipovitsy, Polya Helina subvittata Seguy – Eglov Isl. Graphomyia maculata Scopoli – Kurgenitsy ? Spilogona carbonella Zetterstedt – Lipovitsy Spilogona contractifrons Zetterstedt – Eglov Isl., Podyelniki, Polya, Vegoruksy ? Spilogona karelica Tiensuu – Podyelniki Coenosia intermedia Fallén – Lipovitsy, Podyelniki 332 Reports of the Finnish Environment Institute 40 | 2014 Coenosia mollicula Fallén – Podyelniki, Turastamozero, Uzkaya Salma, Verkhnee Myagrozero Coenosia ruipalpis Meigen – Khvost Isl., Podyelniki Coenosia trilineella Zetterstedt – Khvost Isl., Uzkaya Salma Thricops albibasalis Zetterstedt – Eglov Isl., Uzkaya Salma Thricops cunctans Meigen – Eglov Isl., Khvost Isl., Rogachev Isl., Verkhnee Myagrozero Thricops diaphanus Wiedemann – Turastamozero, Uzkaya Salma, Vikshezero Thricops genarum Zetterstedt – Podyelniki Thricops lividiventris Zetterstedt – Podyelniki Thricops longipes Zetterstedt – Eglov Isl. Thricops nigrifrons Robineau-Desvoidy – Eglov Isl. Thricops nigritellus Zetterstedt – Lyudskoi Isl. Thricops semicinereus Wiedemann – Eglov Isl., Lipovitsy, Nizhneje Myagrozero, Turastamozero, Vegoruksy ? Drymeia hamata Fallén – Nizhneje Myagrozero Hydrotaea borussica Stein – Lipovitsy, Polya, Turastamozero, Uzkaya Salma, Vorobyi Hydrotaea militaris Meigen – Lipovitsy Hydrotaea pandellei Stein – Eglov Isl., Kosmozero, Lipovitsy, Oyatevschina, Polya, Turastamozero, Uzkaya Salma Hydrotaea pellucens Portschinsky – Ernitskiy Isl., Kosmozero, Uzkaya Salma Hydrotaea velutina Robineau-Desvoidy – Turastamozero Muscina levida Harris – Eglov Isl., Podyelniki Phaonia angelicae Scopoli – Eglov Isl., Lipovitsy, Nizhneje Myagrozero, Polya, Turastamozero Phaonia errans Meigen – Lipovitsy, Polya, Uzkaya Salma Phaonia pallida Fabricius – Turastamozero ? Morellia hortorum Fallén – Podyelniki, Polya, Uzkaya Salma Morellia podagrica Loew – Lipovitsy, Polya, Uzkaya Salma Mesembrina mystacea L. – Lipovitsy Mesembrina resplendens Wahlberg – Bol. Lelikovskiy Isl., Klimenicy, Lipovitsy, Polya, Turastamozero, Uzkaya Salma Stomoxys calcitrans L. – Podyelniki Anthomyiidae Botanophila brunnelinea Zetterstedt – Nizhneje Myagrozero Botanophila fugax Meigen – Nizhneje Myagrozero Botanophila hucketti Ringdahl – Nizhneje Myagrozero Hydrophoria lancifer Harris – Eglov Isl., Lipovitsy, Turastamozero, Vegoruksy Zaphne ambigua Fallén – Podyelniki Zaphne caudata Zetterstedt – Eglov Isl., Podyelniki Anthomyia monilis Meigen – Ernitskiy Isl., Kizhi Isl., Kuivakhda Isl., Lelikovo, Lyudskoi Isl., Myal’ Isl., Sennaya Guba, Shunevskiy Isl., Turastamozero, Vorobyi Anthomyia plurisetosa Brullé – Oyatevschina Anthomyia pluvialis L. – Vorobyi Anthomyia procellaris Rondani – Rogachev Isl. Eutrichota frigida Zetterstedt – Polya Pegomya circumpolaris Ackland et Grifiths – Turastamozero Pegomya lavoscutellata Zetterstedt – Lipovitsy Pegomya fulgens Meigen – Podyelniki Pegomya geniculata Bouché – Lipovitsy, Polya, Uzkaya Salma Pegomya incisiva Stein – Podyelniki Pegomya maculata Stein – Lipovitsy, Turastamozero Pegomya pulchripes Loew – Podyelniki Reports of the Finnish Environment Institute 40 | 2014 333 Pegomya scapularis Zetterstedt – Polya, Turastamozero Pegomya zonata Zetterstedt – Lipovitsy Pegoplata inirma Meigen – Nizhneje Myagrozero Pegoplata juvenilis Stein – Eglov Isl. Heterostylodes pilifera Zetterstedt – Podyelniki Delia coarctata Fallén – Nizhneje Myagrozero Delia fabricii Holmgren – Nizhneje Myagrozero Delia lorilega Zetterstedt – Nizhneje Myagrozero Delia lophota Pandellé – Turastamozero Delia platura Meigen – Nizhneje Myagrozero, Turastamozero Scathophagidae Parallelomma vittatum Meigen – Kopanets lake, Lelikovo, Lyudskoi Isl., Paleostrov Isl., Turastamozero Leptopa iliformis Zetterstedt – Khvost Isl. Cordilura albipes Fallén – Eglov Isl., Kurgenitsy, Lipovitsy, Rogachev Isl., Velikaya Niva, Vikshezero Cordilura ciliata Meigen – Kopanets lake, Kurgenitsy, Rogachev Isl., Vorobyi Cordilura picipes Meigen – Bol. Lelikovskiy Isl., Eglov Isl., Ernitskiy Isl., Kizhi Isl., Lyudskoi Isl. Cordilura pubera L. – Kizhi Isl., Tipinitsy, Velikaya Niva Cordilura pudica Meigen – Klimenicy Megaphthalma pallida Fallén – Bol. Lelikovskiy Isl., Kopanets lake, Kurgenitsy, Lyudskoi Isl., Myagrozero, Tambitsy, Turastamozero, Uzkaya Salma, Velikaya Niva, Vikshezero, Volkostrov Isl., Vorobyi Hexamitocera loxocerata Fallén – Tolvuya Nanna armillata Zetterstedt – Vorobyi Nanna lavipes Fallén – Kizhi Isl., Lyudskoi Isl., Oyatevschina Nanna inermis Becker – Klimenicy Cleigastra apicalis Meigen – Kurgenitsy, Lelikovo Conisternum obscurum Fallén – Vorobyi Scathophaga furcata Say – Klimenicy, Lyudskoi Isl., Myagrozero Scathophaga inquinata Meigen – Rogachev Isl., Vorobyi Scathophaga stercoraria L. – Kizhi Isl., Kuzaranda Scathophaga suilla Fabricius – Ernitskiy Isl., Kizhi Isl., Oyatevschina, Tambitsy, Vorobyi Chaetosa punctipes Meigen – Kizhi Isl., Kopanets lake, Lelikovo, Sennaya Guba Microprosopa pallidicauda Zetterstedt – Kopanets lake, Tipinitsy Hydromyza livens Fabricius – Podyelniki Staegeria kunzei Zetterstedt – Klimenicy, Vorobyi Pogonota barbata Zetterstedt – Klimenicy, Kopanets lake, Kurgenitsy, Tipinitsy, Vegoruksy, Verkhnee Myagrozero Calliphoridae Bellardia viarum Robineau-Desvoidy – Kizhi Isl. Calliphora vomitoria L. – Podyelniki Cynomya mortuorum L. – Eglov Isl., Kizhi Isl. Eurychaeta palpalis Robineau-Desvoidy – Oyatevschina Lucilia bufonivora Moniez – Eglov Isl., Podyelniki Sarcophagidae Amobia oculata Zetterstedt – Podyelniki Metopia grandii Venturi – Podyelniki Agria mamillata Pandellé – Oyatevschina, Vorobyi Brachicoma devia Fallén – Eglov Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Vorobyi 334 Reports of the Finnish Environment Institute 40 | 2014 Sarcophaga albiceps Meigen – Nizhneje Myagrozero, Podyelniki, Vegoruksy Sarcophaga aratrix Pandellé – Eglov Isl., Klimenicy, Nizhneje Myagrozero, Vikshezero Sarcophaga caerulescens Zetterstedt – Eglov Isl., Nizhneje Myagrozero, Vorobyi Sarcophaga carnaria L. – Paleostrov Isl. Sarcophaga haemorrhoides Böttcher – Nizhneje Myagrozero Sarcophaga melanura Meigen – Rogachev Isl. Sarcophaga schuetzei Kramer – Eglov Isl. Sarcophaga sexpunctata Fabricius – Eglov Isl. Sarcophaga similis Meade – Kizhi Isl., Podyelniki Sarcophaga socrus Rondani – Sennaya Guba Sarcophaga subulata Pandellé – Podyelniki Sarcophaga uliginosa Kramer – Eglov Isl., Vikshezero Sarcophaga vagans Meigen – Oyatevschina Sarcophaga variegata Scopoli – Eglov Isl., Kizhi Isl., Oyatevschina, Rogachev Isl., Vikshezero, Vorobyi Tachinidae ? Paratryphera barbatula Rondani – Podyelniki ? Winthemia quadripustulata Fabricius – Turastamozero Bactromyia aurulenta Meigen – Podyelniki Aplomya coninis Fallén – Turastamozero Allophorocera ferruginea Meigen – Nizhneje Myagrozero Exorista larvarum L. – Podyelniki Medina collaris Fallén – Podyelniki Medina multispina Herting – Podyelniki Medina separata Meigen – Podyelniki ? Actia pilipennis Fallén – Podyelniki, Vorobyi Ceromya silacea Meigen – Eglov Isl., Lipovitsy, Podyelniki, Polya, Turastamozero, Uzkaya Salma Tachina fera L. – Nizhneje Myagrozero, Oyatevschina Tachina grossa L. – Turastamozero Nowickia marklini Zetterstedt – Eglov Isl., Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Turastamozero Ernestia rudis Fallén – Eglov Isl. Eurithia connivens Zetterstedt – Podyelniki Halidaya aurea Egger – Podyelniki Eriothrix rufomaculatus DeGeer – Vorobyi Voria ruralis Fallén – Eglov Isl. Thelaira nigripes Fabricius – Nizhneje Myagrozero, Podyelniki, Vegoruksy ? Thelaira solivaga Harris – Oyatevschina Subclytia rotundiventris Fallén – Turastamozero Gymnosoma nudifrons Herting – Paleostrov Isl. Phasia aurulans Meigen – Vorobyi Phasia hemiptera Fabricius – Klimenicy ? 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SТХПЯОrЛОrР, H. 1987. MКЩЩТЧР ЭСО FТЧЧТsС CСrвsШЦОХТНКО (CШХОШЩЭОrК). I. – NШЭЮХКО EЧЭШЦШХШРТМКО 67: 5–16. SТХПЯОrЛОrР, H. 2010. EЧЮЦОrКЭТШ rОЧШЯКЭК CШХОШЩЭОrШrЮЦ FОЧЧШsМКЧНТКО, DКЧТКО ОЭ BКХЭТКО. – SКСХЛОrРТК 16(2): 1–144. HОХsТЧФТ, FТЧХКЧН, ISSN 1237–3273. SТХПЯОrЛОrР, H. & BТsЭröЦ, O. 1981. KКrЭОrТЧР КЯ FТЧХКЧНs ХфЧРСШrЧТЧРКr (CШХОШЩЭОrК, CОrКЦЛвМТНКО). – NШЭЮХКО EЧЭШЦШХШРТМКО 61: 15–29. SЭКrý, J. & SКХЦОХК, J. 2004. RОНОsМrТЩЭТШЧ КЧН ЛТШХШРв ШП Limonia badia (АКХФОr) (DТЩЭОrК: LТЦШЧТТНКО). – EЧЭШЦШХШРТМК FОЧЧТМК 15 (1): 41–47. SöНОrЦКЧ, G. & LОТЧШЧОЧ, R. 2003. SЮШЦОЧ ЦОsТЩТsЭТТsОЭ УК ЧТТНОЧ ЮСКЧКХКТsЮЮs. – TrОЦОб PrОss Oв, HОХsТЧФТ..420 Щ. TТОЧsЮЮ, L. 1933. SШrЭКЯКХКЧ ЩТЭтУтЧ sЮНОЧФШrОЧЧШТsОЭ. – AЧЧКХОs SШМТОЭКЭТs ГШШХШРТМКО–BШЭКЧТМКО FОЧЧТМКО. VКЧКЦШ 14(4): 287–370. VКХХО, K. J. 1927. ГЮr KОЧЧЭЧТs НОr OНШЧКЭОЧПКЮЧК FТЧЧХКЧНs III. ErРтЧгЮЧРОЧ ЮЧН гЮsтЭгО. – AМЭК SШМТОЭКЭТs ЩrШ FКЮЧК ОЭ FХШrК FОЧЧТМК 56 (11): 1–36. VКХХО, K. J. 1952. DТО ШsЭПОЧЧШsФКЧНТОsМСОЧ OНШЧКЭОЧ (ГЮr KОЧЧЭЧТs НОr OНШЧКЭОЧПКЮЧК FТЧЧХКЧНs VI). – AМЭК EЧЭШЦШХШРТМК FОЧЧТМК 10: 1–59. VТrКЦШ, J. 1969. ГЮr KОЧЧЭЧТs НОr MТЧТОrОrПКЮЧК FТЧЧХКЧНs. оЛОr НТО АТrЭsЩlКЧгОЧ ЮЧН НТО VОrЛrОТЭЮЧР НОr ЦТЧТОrОЧНОЧ BХКЭЭаОsЩОЧ (HвЦ., TОЧЭСrОНТЧШТНОК). – AЧЧКХОs EЧЭШЦШХШРТМТ FОЧЧТМТ 35: 3−44. АШХП, H. 1967. DТО АОРаОsЩОЧ FТЧЧХКЧНs. – AМЭК EЧЭШЦШХШРТМК FОЧЧТМК 23: 1–46. 338 Reports of the Finnish Environment Institute 40 | 2014 3.7 Localities in Zaonezhye area used in species lists of vascular plants, bryophytes, lichens, fungi and insects, and their toponyms Alexei V. Kravchenko*#, Pertti Uotila** and Jevgeni Jakovlev*** * Forest Research Institute of the Karelian Research Center of Russian Academy of Sciences. Petrozavodsk, 11 Pushkinskaya St., RU-185910 Petrozavodsk, Karelia, Russia ** Botany Unit, Finnish Museum of natural History, P.O.Box 7, FI-00014 University of Helsinki, Finland ***The Finnish Enviroment Institute (SYKE) Mechelininkatu 34a. P.O.Box 140, FIN-00251 Helsinki, Finland #Corresponding author E-mail: alex.kravchen@mail.ru The accuracy of collection localities given on the labels of herbarium specimens and insect collections, as well in the literature, is very variable. In most cases the geographical names have been taken from maps in use during particular historical periods. Several place names have changed over time. All found localities, where species have been recorded in Zaonezhye area, are included in the table, with their known toponyms. At present, many villages in the table have been abandoned. All place names indicated on old labels could not be found from Mullonen et al. (2013) or other sources (printed papers, maps, internet sources), and such names are excluded from the table. In some cases two or more places have the same name, and they are excluded as well. Coordinates (if not otherwise mentioned) indicate the center of the settlement, lake, island, peninsula, etc. The actual collection place is located within the locality given and usually well-marked on the maps or in its more or less immediate vicinity (labels often include words like “near, “close”, “next to”, etc.). * RЮssТКЧ ЧКЦОs КrО РТЯОЧ КММШrНТЧР ЭШ: MЮХХШЧОЧ, I.I., AгКrШЯК, I.V. & GОrН, A.S. 2013. . ., . ., . . ДCКЭКХШР ШП РОШРrКЩСТМКХ ЩХКМО ЧКЦОs ШП ГКШЧОгСвОЖ. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 251 Щ. (IЧ RЮssТКЧ). English (shortened in parentheses) Azhepnavolok Russian name* Spelling variants Type of the place and Finnish names Decimal coordinates AгСОЛЧКЯШХШФ AsСОЛ 62.628826 N; 34.962074 E Peninsula Reports of the Finnish Environment Institute 40 | 2014 339 VТХХКРО 62.251903 N; 35.039493 E IsХКЧН 61.969199 N; 35.261581 E IsХКЧН 61.963382 N; 35.129745 E VТХХКРО 62.070505 N; 35.197037 E Bukolnikovskiy IsХКЧН 62.006502 N; 35.199783 E Butenevo VТХХКРО 62.532975 N; 35.363165 E Chelozero Lake 62.416746 N; 34.983793 E VТХХКРО 62.632001 N; 34.648367 E Dolgiy IsХКЧН 62.111704 N; 35.267761 E Eglov IsХКЧН 62.134774 N; 35.164249 E Ernitskiy IsХКЧН 61.989196 N; 35.168057 E FОНШЭШЯШ VТХХКРО 62.660191 N; 34.682274 E FШЦТЧШ VТХХКРО 62.561743 N; 34.887663 E TаТЧ ЯТХХКРО ШЧ B. Klim. 61.978328 N; 35.213344 E GКЛШsЭrШЯ IsХКЧН 62.483694 N; 34.557043 E Gizhozero Lake 62.469416 N; 35.084604 E Gryz IsХКЧН 62.022556 N; 35.222379 E Gryznavolok Cape on B. Klim. 62.022556 N; 35.222379 E IгЛЮsСОМСЧвТ IsХКЧН 62.111657 N; 34.954397 E Kainos IsХКЧН 62.584217 N; 35.405647 E Kalgostrov IsХКЧН 62.004324 N; 35.128652 E Kanev IsХКЧН 62.010591 N; 35.215688 E Karasozero VТХХКРО КЧН ХКФО 62.407075 N; 34.890936 E Kaskoselga VТХХКРО 62.246321 N; 35.467176 E Kazhma VТХХКРО 62.550795 N; 34.839851 E Bolnichnyi Limosaari KХТЦsФТУ Klimetskoi Klimenetskiy . Bolshoi Klimenetsky Bolshoi Klimetskiy (B. Klim., Bol. Klim.) Bolshoi Lelikovskiy (B. Lelik., Bol. Lelik.) Boyarstchina Boyarschina DТКЧШЯК-GШrК DТКЧШаК-GШrК Dianova Gora Garnitsy (Pervye & VЭШrвО) 340 ( ) Reports of the Finnish Environment Institute 40 | 2014 Garnitsa Limoluoto IsХКЧН 62.084754 N; 35.213453 E Khvost IsХКЧН 62.149371 N; 35.152435 E Klim Nos Peninsula 62.552257 N; 35.343228 E Klimenitsy VТХХКРО ШЧ B. Klim. (former monastery) 61.849696 N; 35.180698 E Lake 62.033892 N; 35.124841 E KШrЛШгОrШ Lake 62.206441 N; 35.287818 E Koselga VТХХКРО ШЧ B. Klim. 62.003596 N; 35.321121 E Kosmozero Lake 62.447286 N; 34.941034 E Kosmozero VТХХКРО 62.334634 N; 35.057163 E Krokhino VТХХКРО 62.363944 N; 35.270308 E Kuivakhda IsХКЧН 61.959308 N; 35.170975 E Kurgenitsy VТХХКРО ШЧ B. Klim. 62.071655 N; 35.286457 E VТХХКРО 62.374627 N; 35.525054 E Ladmozero Lake 62.536845 N; 34.683295 E Ladmozero VТХХКРО 62.56553 N; 34.664413 E VТХХКРО 62.287764 N; 34.876731 E LКЦЛТЧsФТО IsХОs 61.957767 N; 35.09107 E Lelikozero VТХХКРО КЧН ХКФО 62.303488 N; 34.93185 E Kizhi Kopanetz Kuzaranda LКЦЛКsrЮМСОв Kischi Kiischi Kishi Kopanets Kusaranda Kuusiranta LКЦЛКs RЮМСОТ Lichkov See: Lyudskoy Lizhma VТХХКРО 62.378977 N; 34.515067 E Lipovitsy VТХХКРО 62.115029 N; 35.060123 E Longasy VТХХКРО ШЧ B. Klim. 61.988603 N; 35.210739 E IsХКЧН 61.965502 N; 35.175376 E Lukova Bay on B. Klim. 61.913642 N; 35.188769v Medvedevo VТХХКРО 62.532611 N; 34.852555 E Medvezhia Gora HТХХ КЧ B. KХТЦ. 61.891034 N; 35.217605 E Megostrov IsХКЧН 62.563731 N; 35.42894 E MОХШТРЮЛК VТХХКРО КЧН ЛКв 62.512201 N; 34.588486 E Lyudskoi Lyudskoy LТМСФШЯ Reports of the Finnish Environment Institute 40 | 2014 341 VТХХКРО КЧН island 62.289042 N; 34.831215 E Motalovo VТХХКРО ШЧ B. Klim. 61.974821 N; 35.237151 E Myal’ IsХКЧН 62.000035 N; 35.147269 E Mysh’i IsХОs 62.013107 N; 35.080665 E Nikonova Gora VТХХКРО 62.573608 N; 34.824744 E Nizhnee Myagrozero VТХХКРО КЧН ХКФО 62.512977 N; 34.769135 E VТХХКРО 62.586729 N; 34.921611 E IsХКЧН 61.985826 N; 35.200828 E Mizhostrov Okatovstchina Mezhostrov Okatovschina Orozh Oyatevstchina Oyatevschina VТХХКРО 62.082301 N; 35.180677 E Padmozero Padmosero Lake 62.493025 N; 35.170732 E Paleostov IsХКЧН 62.565773 N; 35.252533 E Petry VТХХКРО ШЧ B. Klim. 62.026242 N; 35.247021 E Pod’elniki Podyelniki VТХХКРО 62.110299 N; 35.169004 E Polya VТХХКРО 62.304761 N; 35.299123 E VТХХКРО 62.492318 N; 35.283284 E Lake 62.497105 N; 35.090828 E Pryalichinskaya PШУКХТЭsТЧsФКУК Putkozero 342 Radkolie Radkolye Radkol’e Cape on B. Lelik. 61.943054 N; 35.098279 E Radkolie Radkol’e IsХКЧН 61.995407 N; 35.1872 E Rechka VТХХКРО 62.095981 N; 35.178617 E Rechnoy IsХКЧН 62.590887 N; 35.211506 E Regimatka VТХХКРО 62.515407 N; 34.887147 E Rogachev IsХКЧН 62.12555 N; 35.185621 E Rogostrov IsХКЧН 62.002221 N; 35.185387 E 62.15173 N; 34.94471 E Rugozero RЮЮСТУтrЯТ Lake SОЧЧКвК GЮЛК SОЧЧШРЮЛК HОТЧтХКСЭТ VТХХКРО ШЧ 61.995891 N; B. KХТЦ. КЧН ЛКв 35.208143 E Seredka VТХХКРО ШЧ B. Klim. 62.044124 N; 35.245565 E Severnyi Myshyi IsХКЧН 62.015097 N; 35.078784 E Severnyi Sokoliy IsХКЧН 62.371764 N; 34.749412 E Reports of the Finnish Environment Institute 40 | 2014 Shiltya VТХХКРО 62.411273 N; 35.174178 E Shunevskiy IsХКЧН 62.139556 N; 35.21371 E VТХХКРО 62.594115 N; 34.93187 E Schsuchia Bay on B. Klim. 61.856936 N; 35.207616 E Spirovka VТХХКРО 62.437613 N; 35.133151 E HТХХ 62.572901 N; 34.696694 E TКЦЛТЭsв VТХХКРО 62.229184 N; 35.55747 E TОХЩШгОrШ VТХХКРО КЧН ХКФО 62.613468 N; 34.885905 E TОХвКЭЧТФШЯШ VТХХКРО 62.047867 N; 35.20233 E TОrОФСШЯШ VТХХКРО 62.318605 N; 35.065858 E TТЩТЧТЭsв VТХХКРО 62.189107 N; 35.414819 E VТХХКРО 62.51028 N; 35.285149 E TШХЯЮвsФТв BШr VТХХКРО 62.503503 N; 35.241239 E TШХsЭвТ NКЯШХШФ Cape 62.298311 N; 35.575323 E Sunku Schungu Shun’ga Shunga - Sypun Gora TШХЯЮвК TЮХЯШУК TШХЯШУК TЮХаШУК TШХаШУК TЮrКsЭКЦШгОrШ TЮrКsЭКЦ VТХХКРО КЧН ХКФО 62.552306 N; 34.714546 E Unitsa Unitza VТХХКРО 62.597279 N; 34.460144 E Bay of Lake Onega 62.486782 N; 34.583397 E VТХХКРО 62.173124 N; 35.272083 E VТХХКРО 62.135474 N; 34.930992 E Uzkie VТХХКРО 62.437475 N; 34.958559 E VКЛХШФ IsХКЧН 62.575909 N; 35.410805 E VКЧМСШгОrШ Lake 62.529951 N; 34.800377 E VКrЧКЯШХШФ Cape 62.162788 N; 35.462198 E VТХХКРО 62.218831 N; 34.883711 E Lake 62.136668 N; 35.115797 E VТХХКРО КЧН ЛКв 62.251825 N; 35.068103 E UЧТЭsФКвК GЮЛК UsЭ’-ВКЧНШЦК Uzkie Salmy VОРШrЮФsК VОРШrЮФsв - UsЭУКЧНШЦК Uzkaya Salma VОРКrЮs АТРШrЮs VОФСФШгОrШ VОХТФКвК GЮЛК АОХТФКУК-РЮЛК VОХТФКУК GЮЛК Suurlahti Reports of the Finnish Environment Institute 40 | 2014 343 VОХТФКвК NТЯК VТХХКРО 62.362816 N; 35.223443 E VОrФСЧОО Myagrozero VТХХКРО КЧН ХКФО 62.482016 N; 34.819946 E VОrЭТХШЯШ VТХХКРО 62.00665 N; 35.181214 E VШТЧКЯШХШФ VТХХКРО КЧН peninsula 61.97791 N; 35.33571 E IsХКЧН 62.112554 N; 35.207836 E VШrШЛ´Т VШrШЛвТ VТХХКРО ШЧ B. Klim. 62.056191 N; 35.251095 E VШrШЧТЧsФШО VТХХКРО 62.471389 N; 35.205934 E VТХХКРО 62.519262 N; 35.366265 E Zimnyaya Mountain 62.386252 N; 35.052639 E Zharnikovo VТХХКРО 62.056789 N; 35.207882 E VТХХКРО 62.103317 N; 35.177155 E IsХКЧН 61.992243 N; 35.1928 E IsХКЧН 62.045831 N; 35.363579 E VШХФШsЭrШЯ Zaselezhye ГЮЛШЯШ VОХТФКУК NТЯК VШХФ OsЭrШЯ Susisaari ГКsОХОгУО ГЮЛШЯК ВКЦ ВЮгСЧвТ OХОЧТв (ВЮ. OХОЧТв) ВЮгСЧв OХОЧв Abandoned villages in Zaonezhye Peninsula (Photo Boris Rayevsky). 344 Reports of the Finnish Environment Institute 40 | 2014 Karelian and Finnish botanists and entomologists on the Ekolog ship. July 2004. In front: Alexei Kravchenko (left),and Pertti Uotila (right); behind, left to right: Andrei Humala, Alexei Polevoi, Jevgeni Jakovlev (Photo Tapio Lindholm). Reports of the Finnish Environment Institute 40 | 2014 345 Karelian botanists on the shore of Lake Onega. Losyi Islands. July 2004. Left to right: Elena Gnatyuk, Alexei Kravchenko and Oleg Kuznetsov (Photo Tapio Lindholm). 346 Reports of the Finnish Environment Institute 40 | 2014 Aconitum septentrionale – an eastern («Siberian») species which can be found from Zaonezhye close to the western limit of its distribution area (Photo Tapio Lindholm). Reports of the Finnish Environment Institute 40 | 2014 347 Polemonium caeruleum in blossom on meadows along the Kuzaranda shore of Lake Onega (Photo Tapio Lindholm). 348 Reports of the Finnish Environment Institute 40 | 2014 Luxuriant shore meadow of Allium schoenoprasum and Melampirum nemorosum on the shore of Lukova Bay (Photo Pertti Uotila). Reports of the Finnish Environment Institute 40 | 2014 349 Rauno Ruuhijärvi (in front) and Mikko Piiranen (behind) on the Kuzaranda shore of Lake Onega. The adults of Black-veined White butterly (Aporia crataegi) are very abundant on mineralized soils (Photo Pertti Uotila). 350 Reports of the Finnish Environment Institute 40 | 2014 Ecolog, the ship of the Karelian Research Center of Russian Academy of Sciences (Photo Tapio Lindholm). Reports of the Finnish Environment Institute 40 | 2014 351 Sunset in Vegoruksa Bay of Lake Onega (Photo Boris Rayevsky). 352 Reports of the Finnish Environment Institute 40 | 2014 Tapio Lindholm (Photo Jevgeni Jakovlev). Reports of the Finnish Environment Institute 40 | 2014 353 Olli Manninen (left) and Alexei Kravchenko (right) found a rare fungus, Piloporia sajanensis in herb-rich spruce forest in the vicinity of Uzkie Salmy (Photo Jevgeni Jakovlev). 354 Reports of the Finnish Environment Institute 40 | 2014 Andrei Humala (left) and Alexei Polevoi (right) in herb-rich spruce forest with Aconitum septentrionale (Photo Jevgeni Jakovlev). Reports of the Finnish Environment Institute 40 | 2014 355 356 Reports of the Finnish Environment Institute 40 | 2014 DOC U ME N TAT ION PAGE Publisher Finnish Environment Institute Author(s) Tapio Lindholm, Jevgeni Jakovlev and Alexei Kravchenko (eds.) Title of publication Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia Publication series and number Reports of the Finnish Environment Institute 40/2014 Date March 2015 Theme of publication Parts of publication/ other project publications The publication is available in the internet: www.syke.i/publications | helda.helsinki.i/syke | www.bpan.i Abstract Zaonezhye Peninsula (Zaonezhsky Peninsula; in Russian transcription) is situated on the northwestern coast of Lake Onega in the Republic of Karelia, Russia. The territory of Zaonezhye is unique in that it contains nearly every type of terrain and unconsolidated sediment known in the vast expanses of northwest Russia. It is also eastern part of Fennoscandian shield. It is characterized by a high diversity of basic limestone and carbonate rocks that determine the fertility of local soils as well as the unique diversity of habitats, lora and fauna. Numerous rare calciphile plant and lichen species are found here, as well as rich, eutrophic wetlands. Long-term farming and animal husbandry have led to a large number of grassland communities in the area. As a result, a mosaic structure of diverse habitats has evolved here. Europe’s second largest lake, Lake Onega, with its clear and deep waters also affect the local climate, making it milder. This report provides for the irst time detailed species lists of vascular plants, bryophytes, lichens, wood-growing fungi and insects covering the entire Zaonezhye Peninsula, Kizhi archipelago and other adjacent islands. The most important sites for protection were observed, and six new nature monuments in the southern and southerneast parts of Zaonezhye Peninsula are recommended to be established. This publication contents following articles characterizing nature of Zaonezhye area: 1. Geology and physical geography: 1.1.Geological description, 1.2. Geomorphology and Quaternary deposits, 1.3. Hydrological characteristics, 1.4. Soil cover, 1.5. Palaeogeography, 1.6. Existing and planned protected areas; 2. Landscapes and ecosystems: 2.1. Modern landscapes of Zaonezhye, 2.2. Landscape structure, 2.3. Structure of the forest covered land and forest stands, 2.4. Forest structures, 2.5. Mires, 2.6. Meadows; 3. Flora and fauna: 3.1.Vascular plants, 3.2. Bryophyte lora, 3.3 Species list of lichens and allied fungi, 3.4. Red listed and indicator lichens, 3.5. Aphyllophoroid fungi and 3.6. Insect fauna. 3.7. Localities in Zaonezhye area used in species lists of vascular plants, bryophytes, lichens, fungi and insects, and their toponyms. Keywords geology, palaeogeography, landscapes, forest, mires, meadows, vascular plants, bryophytes, lichens, wood-growing fungi, insects, biodiversity, nature conservation, Zaonezhye Peninsula, Kizhi archipelago, Onega Lake, Republic of Karelia Financier/ commissioner Nordic Council of Ministers; Ministries of the Environment of Finland, Norway, Sweden; Ministries for Foreign Affairs of Finland, Norway and Sweden, Directorate of regional protected areas of the Republic of Karelia ISBN 978-952-11-4404-2 (pbk.) ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 (print.) ISSN 1796-1726 (online) No. of pages 359 Language English Restrictions public Price (incl. tax 8 %) For sale at/ distributor Finnish Environment Institute (SYKE), neuvonta P.O. Box 140, FI-00251 Helsinki, Finland, Email: neuvonta.syke@ymparisto.i Financier of publication Finnish Environment Institute (SYKE), P.O. Box 140, FI-00251 Helsinki, Finland Phone +358 295 251 000 Printing place and year Juvenes Print, 2015 Reports of the Finnish Environment Institute 40 | 2014 357 И И ИЯ И ЦИИ И А 2015 , ( ) ( .) BТogОogrКpСy, lКnНscКpОs, ОcosystОms КnН spОcТОs oП ZКonОzСyО PОnТnsulК, Тn LКkО OnОgК, RussТКn KКrОlТК ( , , , ) 40 / 2014 Т / : , ааа.sвФО.i/puЛlТМКtТons е СОlНК.СОlsТnФТ.i/sвФО е ааа.ЛpКn.i Ч − , , .Э , , - . – . , , . . , , – , , , , 2.2. : 3.1. , 1.4. , 3.5. , К , Ф , - , 1.5. , 2.4. , 3.2. , 3.3 , 3.6. , , ( , , , , , . : 1. , 1.3. : 2.1. C , 2.5. 3.7. , , . , . ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 ( Ш ) Ц %) (SВKE), P.O. Boб 140, FI-00251 HОlsТnФТ, FТnlКnН, EmКТl: nОuЯontК.sвФО@вmpКrТsto.i JuЯОnОs PrТnt, 2015 358 Reports of the Finnish Environment Institute 40 | 2014 ( , , , ISSN 1796-1726 ( (SВKE), P.O. Boб 140, FI-00251 HОlsТnФТ, FТnlКnН FТnnТsС EnЯТronmОnt InstТtutО (SВKE), P.O. Boб 140, FI-00251 HОlsТnФТ, FТnlКnН : + 358 0295 251 000 Ф , ; 3. , 360 / ), 3.4. , 2.6. , , ; ; ) , 1.6. , . , , ISBN 978-95211-4404-2- ( , , Ш / ; 2. , 2.3. , 1.2. , . . : 1.1. , . , . , , , , . ) 8 KU VA I LU LEHTI Julkaisija Suomen ympäristökeskus Julkaisuaika maaliskuu 2015 Tekijä(t) Tapio Lindholm, Jevgeni Jakovlev ja Alexei Kravchenko (toim.) Julkaisun nimi Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia (Äänisenniemen alueen biogeograia, maisemat ja lajisto. Ääninen,Venäjän Karjala) Julkaisusarjan nimi ja numero Suomen ympäristökeskuksen raportteja 40/2014 Julkaisun teema Julkaisun osat/ muut saman projektin tuottamat julkaisut Julkaisu on saatavana internetistä: www.syke.i/julkaisut | helda.helsinki.i/syke | www.bpan.i Tiivistelmä Äänisenniemi, venäjäksi , sijaitsee Äänisen luoteisosassa Karjalan tasavallassa Venäjällä. Äänisenniemi on maaperällisesti monimuotoinen ja siellä on lähes kaikkia maaston tyyppejä ja irtaimia maalajeja, joita esiintyy laajalla Venäjän alueella. Se on myös itäistä osaa Fennoskandian kilvestä. Alueelle ovat tyypillisiä kalkkikivi ja muut emäksiset kivilajit, mistä johtuu maaperän rehevyys sekä elinympäristöjen ja lajiston rikkaus. Lukuisia kalkinvaatija putkilokasveja ja jäkäliä esiintyy täten alueella. Alueella on myös runsaasti lettosoita. Pitkäaikainen asutushistoria ja sen karja- ja maatalous on luonut alueelle runsaasti maatalousmaata, joka nyt on niittyinä. Tämä lisää Äänisenniemen elinympäristökirjoa. Euroopan toiseksi suurin järvi Ääninen, jossa on syvä ja kirkas vesi, tuo oman leudomman paikallisilmaston Äänisenniemelle. Tämä raportti sisältää runsaasti uutta tietoa putkilokasveista, sammalista, jäkälistä, käävistä ja hyönteisistä Äänisenniemeltä ja siihen liittyviltä saarilta, mukaan lukien Kiźin saarelta. Suojelun kannalta tärkeimpiä alueita inventoitiin ja kuutta uutta suojelualuetta ehdotetaan perustettavaksi Äänisenniemen eteläosiin. Tämä julkaisu käsittää seuraavat artikkelit Äänisenniemen alueelta. 1. Geologia ja fysikaalinen maantiede: 1.1. Geologinen kuvaus. 1.2. Geomorfologia ja jääkauden luomat kerrostumat, 1.3. Alueen hydrologinen luonnehdinta, 1.4. Maaperä, 1.5. Palaeomaantiede, 1.6. Suojelualueet ja ehdotetut suojelualueet; 2. Maisemat ja ekosysteemit: 2.1. Äänisenniemen nykyiset maisemat, 2.2. Maisemien rakenne, 2.3. Metsäpeitteisten alueiden rakenne ja metsiköt. 2.3. Metsien rakenne, 2.5. Suot, 2.6. Niityt; 3. Flora and fauna: 3.1. Putkilokasvit, 3.2. Sammalet, 3.3. Jäkälät ja jäkälänkaltaiset sienet, 3.4. Uhanalaiset ja indikaattorijäkälät, 3.5. Käävät, 3.7. Hyönteisfauna, 3.7. Paikat Äänisenniemellä, joissa tehtiin lajihavaintoja. Asiasanat geologia, muinaismaantiede, metsät, suot, niityt, putkilokasvit, sammalet, jäkälät, käävät, hyönteiset, luonnon monimuotoisuus, Äänisenniemi, Kizhin saaristo, Ääninen, Karjalan tasavalta Rahoittaja/ toimeksiantaja Pohjoismainen ministerineuvosto, Suomen, Norjan ja Ruotsin ympäristö- ja ulkoasiainministeriöt ISBN 978-952-11-4404-2 (pbk.) ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 (pain.) ISSN 1796-1726 (verkkoj.) Sivuja 360 Kieli Englanti Luottamuksellisuus julkinen Hinta Julkaisun jakelu Suomen ympäristökeskus (SYKE), neuvonta PL 140, 00251, Helsinki Sähköposti: neuvonta.syke@ymparisto.i Julkaisun kustantaja Suomen ympäristökeskus (SYKE), syke.i PL 140, 00251, Helsinki Puh. 0295 251 000 Painopaikka ja -aika Juvenes Print, 2015 Reports of the Finnish Environment Institute 40 | 2014 359 P R E SE N TATI ONSBLAD Utgivare Finlands miljöcentral Författare Tapio Lindholm, Jevgeni Jakovlev och Alexei Kravchenko (eds.) Publikationens titel Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia (Biogeograi, landskapen, ekosystem och arter av Zaonezhye halvön, i Onega Sjön, ryska Karelen) Publikationsserie och nummer Finlands miljöcentrals rapporter 40/2014 Datum mars 2015 Publikationens tema Publikationens delar/ andra publikationer inom samma projekt Publikationen inns på internet: www.syke.i/publikationer | helda.helsinki.i/syke | www.bpan.i Sammandrag Zaonezhie halvön, på ryska och i inska Äänisenniemi, ligger i Karelska republiken, på den östra delen av Fennoscandia skölden. Halvön omfattar den mellersta delen av den norra Onega kusten, och de närbelägna öarna. Zaonezhie är ett unikt naturområde med nästan alla typer av Kvartära tidens jordarter och jordformer som har formats i nordvästra Ryssland. Tack vare berggrundets höga halt av kalksten och andra alkalina bergarter är jorden i trakten särskild bördig. Till följd av det är naturet i området ovanligt rikt med en stor mångfald av lora av sällsynta växtarter och lavar och fauna. På Zaonezhie områden inns så artrika skogar, men också mycket myrar och dessutom rikmyrar. Närheten till Onega sjön, dess djup och klar vatten, den näst största sjön i Europa, har en gynnsam effekt på lokala klimatet. Tack vare den bördiga jorden och relativt milda klimatet har området en lång jordbrukshistoria. Många forna åkrar är nuförtiden naturnära ängar. Zaonezhie är ett särskilds mångfaldigt område tack för dess areal och belägenhet. I denna publikation inns de första detaljerade listor över arter av kärlväxter, mossor, lavar, svampar och insekter över hela territoriet i Zaonezhie halvön, Kizhi skärgård och andra närliggande öar. Inventeringen omfattar de största bevarandevärda områden av södra och sydöstra halvön, där det rekommenderas att grunda sex nya naturskyddsområden. Boken beskriver naturen på Zaonezhie halvön i följande avsnitt: 1. Geologi och geograi: 1.1.Geologisk beskrivning, 1.2. Geomorfologi och kvartära sediment, 1,3.Vattensystem, 1.4. Jordmån, 1.5. Paleogeograi, 1,6. Beintliga och planerade skyddsområden; 2. Landskap, ekosystem och biogeograi: 2.1. Moderna landskap, 2.2. Landskapets struktur, 2.3. Skogstäcke, 2.4. Skogarnas stånd struktur, 2,5. Myrar, 2,6. Ängar; 3. Flora och fauna 3.1. Kärlväxter, 3.2. Mossor, 3.3 Lavar och lavartade svampar 3.4. Sällsynta och sårbar lav arter, 3.5. Tickor och 3.6. Insekt fauna. och 3.7. Index för geograiska namn och ortnamn som nämnts i förteckningen över olika typer av förekomster av lora och fauna. Nyckelord geologi, paleogeograi, landskapen, skogar, myrar, ängar, kärlväxter, mossor, lavar, tickor, insekter, naturens mångfald, Naturskydd, Zaoneshie halvön, Kizhi skärgård, Onega sjön, Republiken Karelia Finansiär/ uppdragsgivare Nordiska ministerrådet, miljö- och utrikesministerierna i Finland, Norge och Sverige, Directorate of regional protected areas of the Republic of Karelia ISBN 978-952-11-4404-2 (pbk.) ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 (print) ISSN 1796-1726 (online) Sidantal 360 Språk engelska Offentlighet Offentlig Pris (inneh. moms 8 %) Beställningar/ distribution Finlands miljöcentral (SYKE), PB 140, 00251 Helsingfors, Epost: neuvonta.syke@ymparisto.i Förläggare Finlands miljöcentral (SYKE), PB 140, 00251 Helsingfors Tel. 0295 251 000 Tryckeri/tryckningsort -år Juvenes Print, 2015 360 Reports of the Finnish Environment Institute 40 | 2014 The BPAN project promotes and supports the establishment of a representative network of protected areas in the Barents Region. Protected area networks are an important tool for biodiversity conservation as well as climate change adaptation and mitigation. A representative network of protected areas safeguards biodiversity, supports natural ecosystems and maintains ecosystem services. The BPAN project started in 2011 as an initiative of the nature protection subgroup of the BEAC Working Group on Environment. The project has been implemented by nature conservation authorities, scientiic institutes and nature conservation NGOs in Finland, Sweden, Norway and Northwest Russia. Within the project, ive regional pilot projects have been implemented in high conservation value areas of Northwest Russia. All of these areas are under threat from human activities. In Karelia, the pilot project has been implemented on Zaonezhye Peninsula. Zaonezhye Peninsula has a distinctive and diverse natural heritage, which has been recognised for a long time. Although its unique habitats are included in regional nature conservation plans, documentation necessary for the establishment of a protected area has been lacking. At the same time high conservation value forests have been under threat from logging. This publication gives an overview of Zaonezhye Peninsula. It discusses geology, hydrology and landscapes. It also describes present-day species of vascular plants, bryophytes, lichens, wood-growing fungi and insects on the Zaonezhye Peninsula and its adjacent islands, as well as earlier records from the peninsula since the end of the 19th century. We hope that the information on these pages will promote the protection of hundreds of red-listed species and valuable habitats in the Zaonezhye area. ISBN 978-952-11-4404-2 (pbk.) ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 (print) ISSN 1796-1726 (online) 

RE PORTS O F THE FINNI S H E N V I RO N M E N T I N ST I TUTE 4 0 | 2 0 1 4 Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia Tapio Lindholm, Jevgeni Jakovlev & Alexey Kravchenko (eds.) Fi n n i sh E nv i ronme nt Ins t itu te REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 40 | 2014 Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia Tapio Lindholm, Jevgeni Jakovlev & Alexei Kravchenko (eds.) Helsinki 2014 Finnish Environment Institute REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 40 | 2014 Finnish Environment Institute Natural Environment Centre Layout: Pia Kauppinen Cover photo: Clouded Apollo, Parnassius mnemosyne and Rough Hawkbit, Leontodon hispidus meet in Zaonezhye. Andrei Humala. English revision: Minna Hartikainen The publication is also available in the internet: www.syke.i/julkaisut | helda.helsinki.i/syke Juvenes Print, 2015 ISBN 978-952-11-4404-2 (pbk.) ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 (printed) ISSN 1796-1726 (online) 441 729 Painotuote FOREWORD Anna Kuhmonen Zaonezhye Peninsula has a distinctive and diverse natural heritage, and its unique habitats are included in regional nature conservation plans. Although the value of its habitats and landscapes has been known for a long time, the documentation necessary for the establishment of a protected area has been lacking and high conservation value forests have been threatened by forest logging. The Barents Protected Area Network (BPAN) project promotes and supports the establishment of a representative network of protected areas in the Barents Region. Protected area networks are an important tool in biodiversity conservation as well as climate change adaptation and mitigation. A representative network of protected areas safeguards biodiversity, supports natural ecosystems and maintains ecosystem services. In addition to evaluating the network of protected areas in Northwest Russia, the BPAN project has implemented pilot projects in high conservation value areas in order to support the establishment of new protected areas. All the countries in the Barents Region - Russia, Finland, Sweden and Norway - are parties to the Convention on Biological Diversity. In 2010, the parties committed to halting the loss of biodiversity by 2020 and set the 20 Aichi Biodiversity Targets. The Aichi Target 11 calls for at least 17% protection of terrestrial and inland water areas, especially areas of particular importance for biodiversity and ecosystem services, by 2020. Protected areas cover 13.4 % of the Barents Region, while the level of protection in the Republic of Karelia is 4.7 % (2013). Regional and national conservation plans include 59 400 km2 of planned protected areas in the whole Barents Region. However, implementation of conservation plans takes time, and the global targets have been set for 2020. The results of the BPAN project show that the implementation of conservations plans should be quicker and more effective. In 2012, the BPAN project selected ive territories in Northwest Russia where nature conservation was to be promoted through ield studies as well as other activities. In the Republic of Karelia, a pilot project was implemented in the high conservation value forests of Zaonezhye Peninsula. Earlier studies on the peninsula showed that the area supported valuable habitats and species. However, even though forests were included in the regional conservation plan, they were at the same time leased by forestry companies and threatened by logging. Between 2013 and 2014, the BPAN project carried out ield work and documented natural values within the planned Zaonezhye nature park, focusing on high conservation value forests. These activities were conducted by the Finnish Environment Institute, Karelian Research Centre and the Directorate of regional protected areas of the Republic of Karelia in cooperation with experts from the Universities of Helsinki and Eastern Finland, and the Finnish Nature League. This publication presents information on hundreds of red-listed species and valuable habitats. Promoting the protection of high conservation value forests on Zaonezhye Peninsula has been an important part of the BPAN project. We are grateful to all researchers for their valuable input into the ield work as well as this publication. For inancing this work we thank the Nordic Council of Ministers, Ministry of the Environment and Ministry for Foreign Affairs of Finland, Sweden and Norway, and WWF-Russia. We hope that this publication contributes to establishing the valuable nature areas of Zaonezhye Peninsula as statutory protected areas. CONTENTS Foreword ............................................................................................................................ 3 Zaonezhye Peninsula – The pearl of Lake Onega ..........................................7 Introduction ........................................................................................................7 Old villages and traditional land use in Zaonezhye .................................... 9 Nature studies in Zaonezhye ......................................................................... 10 Conservation activities in Zaonezhye ........................................................... 12 Threatened species and proposals for their protection.............................. 13 Acknowledgements .........................................................................................14 1 Geology and physical geography of Zaonezhye Peninsula area ............17 1.1 1.2 1.3 1.4 1.5 1.6 Geological description of Zaonezhye Peninsula......................................17 Introduction ......................................................................................................17 Geomorphology and Quaternary deposits of Zaonezhye ........................ 26 Igneous rocks, mineralogeny and commercial minerals of Zaonezhye Peninsula ..................................................................................29 Geomorphology and Quaternary deposits of Zaonezhye .....................35 Introduction ......................................................................................................35 Geomorphology ...............................................................................................37 Hydrological characteristics of Zaonezhye Peninsula ............................ 41 Introduction ......................................................................................................41 Results................................................................................................................41 Soils and their characteristics on Zaonezhye Peninsula ........................ 53 Introduction ......................................................................................................53 Soil types and their characteristics ............................................................... 53 Conclusions ...................................................................................................... 55 Paleogeography of Zaonezhye Peninsula .................................................. 57 Introduction ......................................................................................................57 Geological Periods ........................................................................................... 60 Nature protected areas in Zaonezhye ......................................................... 75 Introduction ......................................................................................................75 Overview of protected areas in Karelia........................................................ 75 Protected areas on Zaonezhye Peninsula and its adjacent islands........... 76 Planned protected areas on Zaonezhye Peninsula .....................................77 2 Biomes and biogeography of Zaonezhye Peninsula area .........................81 2.1 Modern landscapes of Zaonezhye Peninsula ........................................... 81 2.2 Landscape structure of Zaonezhye Peninsula ........................................103 Introduction ....................................................................................................103 Results..............................................................................................................104 The structure of forest land and forest stands in Zaonezhye Peninsula ................................................................................... 111 Introduction .................................................................................................... 111 Results.............................................................................................................. 111 Forest structures and human impact on Zaonezhye Peninsula: a classiication and case studies ................................................................. 125 Introduction ....................................................................................................125 Methods........................................................................................................... 126 Results and discussion ..................................................................................126 Mires of the Zaonezhye Peninsula............................................................131 Introduction ....................................................................................................131 Study area ....................................................................................................... 132 Material and methods ...................................................................................132 Results and discussion ..................................................................................132 Mires conservation in Zaonezhye ............................................................... 137 Meadows in Zaonezhye ...............................................................................147 Introduction ....................................................................................................147 History of the study of the Zaonezhye’ grasslands ................................. 148 Future of grasslands in Zaonezhye ............................................................. 150 2.3 2.4 2.5 2.6 Reports of the Finnish Environment Institute 40 | 2014 5 3 Flora and fauna in Zaonezhye Peninsula area.............................................153 3.1 3.2 3.3 3.4 3.5 3.6 3.7 Vascular plant lora of Zaonezhye Peninsula ......................................... 153 Introduction ....................................................................................................153 History of loristic studies on the peninsula ............................................. 155 The following century ................................................................................... 156 Recent decades ...............................................................................................157 Present knowledge......................................................................................... 160 List of vascular plant species of Zaonezhye, with annotations for threatened and indicator species............................ 164 Bryophyte lora of Zaonezhye Peninsula ............................................... 193 Abstract ...........................................................................................................193 Introduction ....................................................................................................193 Conclusions .....................................................................................................198 Appendix List of mosses from Zaonezhye Peninsula .............................. 200 List of lichens and allied fungi collected on Zaonezhye Peninsula ...................................................................................207 History of the studies of lichens in Zaonezhye Peninsula and adjacent islands ............................................... 207 Acknowledgements .......................................................................................209 Red-listed and indicator lichens of Zaonezhye Peninsula...................223 Introduction ....................................................................................................223 Material and methods ...................................................................................224 Results..............................................................................................................224 Epiphytes of deciduous trees ....................................................................... 224 Usnea lichens and other fruticose epiphytes ............................................ 226 Epiphytes of spruce ....................................................................................... 227 Lichens on dead wood ................................................................................. 228 Basic and siliceous cliffs................................................................................229 Discussion .......................................................................................................230 Aphyllophoroid fungi of Zaonezhye Peninsula.....................................233 Introduction ....................................................................................................233 Mycological studies in Zaonezhye Peninsula and adjacent areas ..........233 Results..............................................................................................................234 Species conined to pine................................................................................236 Species conined to spruce............................................................................ 236 Species conined to aspen ............................................................................. 236 The most noteworthy indings of threatened and rare species of saproxylic fungi ...........................................................237 Appendix......................................................................................................... 244 Insect fauna of Zaonezhye Peninsula and adjacent islands ................ 257 Introduction ....................................................................................................257 History of entomological studies on Zaonezhye Peninsula .................... 257 Study area and methods ............................................................................... 258 Results..............................................................................................................260 Conclusions .....................................................................................................262 Acknowledgements .......................................................................................263 Annotated list of the insect species included in Red Data Book of the Republic of Karelia (Ivanter & Kuznetsov 2007) and other noteworthy insect species .................................................................................................. 263 List of insect species recorded in Zaonezhye and adjacent islands ....... 275 Localities in Zaonezhye area used in species lists of vascular plants, bryophytes, lichens, fungi and insects, and their toponyms .............. 339 Document page ........................................................................................................ 357 Ли и ия и ции ................................................................................... 358 Kuvailulehti ..............................................................................................................359 Presentationsblad.....................................................................................................360 6 Reports of the Finnish Environment Institute 40 | 2014 Zaonezhye Peninsula – The pearl of Lake Onega Tapio Lindholm*, Jevgeni Jakovlev * and Alexei Kravchenko** * The Finnish Environment Institute (SYKE), P.O.Box 140, 00251 Helsinki, Finland. ** * Forest Research Institute of the Karelian Research Center of the Russian Academy of Sciences, Petrozavodsk, 11 Pushkinskaya St., RU-185910 Petrozavodsk, Karelia, Russia Introduction The Republic of Karelia is located mostly in the eastern part of the Baltic shield, which is composed of Precambrian crystalline rock. However, it includes areas that differ markedly in their geological background, soils and vegetation. Zaonezhye Peninsula is a particularly interesting area in terms of the variety of landscapes, habitats and species. Zaonezhye Peninsula (Zaonezhsky Peninsula; in Russian transcription) is situated on the northwestern coast of Lake Onega. Its eastern shores are washed by the Gulf of Zaonezhye. In the north the peninsula is bordered by Povenetskiy Bay, while to the west it is bounded by Lizhma Bay and the Gulf of Bolshoe Onego (Fig. 1). “Zaonezhye” is used here in a wider sense to include Zaonezhye Peninsula as well as two adjacent peninsulas, Lizhma and Sjar, which are separated by the long and narrow bays of Lake Onega. In the south, Zaonezhye Peninsula shelters an archipelago of numerous islands, also known as Kizhi skerries or the Kizhi archipelago. The archipelago includes two relatively large islands, Bolshoy Klimenetsky and Bolshoy Lelikovsky, which have several old villages, fertile valleys of unique grassland and patches of old-growth forest. The most famous among the islands is Kizhi Island where monumental 17th century churches, included in the UNESCO World Heritage List, are preserved. Often the whole area on the opposite shore of Lake Onega is called Zaonezhye. It is separated from the city of Petrozavodsk by a mere few dozen kilometers of water and has therefore good connections by boat. Zaonezhye is considered a separate biogeographic region (Ramenskaya 1983). According to modern estimates (e.g. Elina et al. 2010), the territory of Zaonezhye is unique in that it contains nearly every type of terrain and unconsolidated sediment known in the vast expanses of northwest Russia. It is characterized by a high diversity of basic limestone and carbonate rocks that determine the fertility of local soils as well Reports of the Finnish Environment Institute 40 | 2014 7 as the unique diversity of habitats, lora and fauna. Numerous rare calciphile plant and lichen species are found here, as well as rich, eutrophic wetlands. Long-term farming and animal husbandry have led to a large number of grassland communities in the area. As a result, a mosaic structure of diverse habitats has evolved here. Europe’s second largest lake, Lake Onega, with its clear and deep waters also affect the local climate by making it milder. Fig.1. Geographical location on Zaonezhye Peninsula 8 Reports of the Finnish Environment Institute 40 | 2014 Old villages and traditional land use in Zaonezhye The late-medieval villages of Zaonezhye Peninsula and the Kizhi archipelago maintained a vibrant rural society until the middle of the 20th century. According to the census of 1887 (Census of population 1904), in the end of the 19th century the population of Zaonezhye Peninsula consisted of 47 000 people. At the time, the population density of the peninsula was at its highest at 13.4 people per km2, while the population density of the entire Olonets Province (present-day Republic of Karelia) was only 2.8 people per km2. Nowadays most of the villages have been abandoned. However, extraordinary pieces of Russian wooden architecture remind us of their past glory. Many old churches are still standing thanks to summer residents who continue to repair them. Fig. 2. Old wooden church in the village of Tambitsy on the southeastern coast of Zaonezhye Peninsula (Photo: Andrei Humala) The southeastern parts of Zaonezhye Peninsula, together with the northern shores of Lake Ladoga, have the longest history of traditional land use in Karelia. The peninsula has been permanently inhabited for thousands of years. The irst traces of pollen of crop plants such as wheat, oat and rye appeared nearly 1 000 years ago (Lavrova et al. 2005). In the past, slash-and-burn-cultivation was the main type of agriculture in Zaonezhye. However, despite a gradual increase in the proportion of cultivated land, a large part of the area has stayed relatively intact. At present, Zaonezhye Peninsula incorporates near-natural landscapes in its central part and areas showing traces of past agricultural activities along the coast of Lake Onega. The central parts of Zaonezhye Peninsula consist of almost unpopulated ridge landscapes that have not been easily accessible for forestry or agriculture. Contrastingly, lowland areas on the southern and southeastern shores of Zaonezhye Peninsula as well as the islands of the Kizhi archipelago have been profoundly affected by slashand-burnt cultivation over time. The present distribution of forest types is mainly the result of the earlier human activities. Originally, lowland areas were covered with coniferous forests that were growing in close to optimal conditions and were therefore characterized by their high quality. Nowadays, near-natural coniferous forest stands Reports of the Finnish Environment Institute 40 | 2014 9 are preserved only in few places where logging is dificult, including paludiied areas and steep, rocky slopes close to the shoreline. A part of the preserved old-growth forests is located within the protected belts of water bodies. For example, the protected belt along the shores of Lake Onega is one kilometre wide. According to the Soviet classiication of forests (1943), which was used until the recent Forest Code (2006), forests along water bodies belonged to water protective forest group and were automatically excluded from logging. The rest of the forests have been affected by selective cuttings. Especially close to the villages, these forests have formed naturally on abandoned hay meadows and ields. According to the forest inventory of 1999 (Gromtsev & Krutov 2000), pine and spruce forests occupy nearly 60 percent of the forest cover, in approximately equal proportions. The remaining area is covered by forests, dominated by birch (ca. 30%), aspen (5%) or grey alder (6%). Intact mires are preserved mainly in the central part of the peninsula where they cover depressions between long and narrow ridges. In lowland areas, numerous small, eutrophic fens occupy narrow bays along the shoreline. In the past, the local population used the lowlands for haymaking. At present these areas combine mire and meadow vegetation, including many red-listed species. However, the hydrology of many mires and brookside forests is affected by the Canadian beaver (Castor canadensis), which is relatively common in the area. The native beaver species, Castor iber, has become extinct here. Nature studies in Zaonezhye There is a long history of nature studies in Zaonezhye that date back to the 19th century. At that time, Finnish researchers prepared and published detailed lists of plants, lichen (Norrlin 1871, 1876) and beetles (Poppius 1899) that are of international importance. Around the same time, Alexander Günther from Petrozavodsk collected and documented hundreds of plant and insect species that have later been recorded from Zaonezhye also by other researchers (See Chapters 3.1, 3.3 and 3.6). After a long break in the irst half of the 20th century, studies resumed irst by Finnish researchers in the 1940s and then by the Karelian Research Centre of the Russian Academy of Sciences (hereinafter KRC RAS) in Petrozavodsk. Until very recently, the lora and fauna of the area have remained largely unexplored. The Atlas of the distribution of vascular plants in northern Europe (Hulten 1971) fails to mention a number of local calciphile and other plants that require fertile soils. There are several scientiic publications on the Kizhi archipelago (e.g. Elina et al. 1999, Ieshko & Protasov 2005, etc) and the central part of Zaonezhye Peninsula (e.g. Gromtsev 2013). However, the irst report on the biodiversity inventories and studies of Zaonezhye (Gromtsev & Krutov 2000) still remains the only publication that covers the entire Zaonezhye Peninsula and the adjacent islands. Mire and meadow vegetation studies have been conducted during several expeditions of the Laboratory for mire ecosystems of the Institute of biology in the past 30 years. These studies have resulted in the establishment of several nature monuments for the protection of mires. Also new data on mire and meadow vegetation and dynamics have been created (See Chapters 2.5 and 2.6). Between 2nd and 8th July 2004, leading Finnish and Russian botanists and entomologists carried out the irst Finnish-Russian expedition on the “Ecolog” research vessel of the KRC RAS. Its goal was to visit hotspots of rare and threatened plant, lichen and insect species. The expedition included 12 participants: Alexei Kravchenko (vascular plants), Oleg Kuznetsov (mire vegetation), Margarita Boychuk (mosses), Margarita Fadeeva (lichens), Alexei Polevoi and Andrei Humala (insects) from the KRC RAS; Elena 10 Reports of the Finnish Environment Institute 40 | 2014 Fig. 3. Intact forest landscapes and mires on Zaonezhye Peninsula and the adjacent areas (after: Kobyakov & Jakovlev (2013), areas visited in 2013 and proposed nature monuments, 1-6. Reports of the Finnish Environment Institute 40 | 2014 11 Gnatyuk from the Petrozavodsk State University (vascular plants), Pertti Uotila and Mikko Piirainen from the Botanical Museum of the Finnish Museum of Natural History in Helsinki (vascular plants); Professor Emeritus Rauno Ruuhijärvi from the University of Helsinki (mire vegetation); Tapio Lindholm (mire vegetation and vascular plants) and Jevgeni Jakovlev (insects) from the Finnish Environment Institute. The following localities were studied: 1. Islands Paleostrov, Rechnoi and Meg-Ostrov near the northern tip of Zaonezhye Peninsula. Different grassland and forest biotopes (old spruce stands, black alder swamps). A large abandoned monastery on Paleostrov Island as well as its old meadows and tree alleys. 2. The southeastern shore of Zaonezhye Peninsula (in the vicinity of the villages of Kuzaranda and Tipinitsy) and the islands of Khedostrov, Shunevsky and Yuzhny Oleniy. High-quality spruce forests with Tilia cordata in the undergrowth. Yuzhny Oleniy Island is the only island in the area. It is also one of three islands in Karelia that are entirely formed of dolomite. 3. Bolshoi Klimenetsky and Bolshoi Lelikovsky Islands, Cape Radkolye. Oldgrowth spruce-dominated forests of Oxalis-Myrtillys type, spruce mires and forested lowland mires as well as grasslands in previously settled areas. Many regionally rare and threatened species of vascular plants, bryophytes, lichens and insects have been found here. The members of the expedition concluded that Zaonezhye contains unique biotopes and habitats of threatened species. They recorded a number of vascular plant, bryophyte, lichen and insect species that are considered rare or threatened in the Republic of Karelia and concluded that more detailed research is required. In the summer of 2013, another international nature expedition was carried out in the southern lowlands of Zaonezhye Peninsula in the framework of the Barents Protected Area Network (BPAN) project. The experts Alexei Kravchenko, Margarita Fadeeva, Andrei Humala, Alexei Polevoi, Boris Rayevsky and Anna Ruokolainen from the KRC RAS, Jevgeni Jakovlev and Kimmo Syrjänen from the Finnish Environment Institute, Timo Kuuluvainen from the University of Helsinki, Olli-Pekka Tikkanen from the University of Eastern Finland and Olli Manninen and Jyri Mikkola from the NGO Finnish Nature League studied natural forests and mires along the southern coast of Zaonezhye Peninsula as well as old-growth forests on Sjar Peninsula on the opposite shore of Lizhma Bay. The expedition aimed to study high conservation value forests (Fig.3) that were identiied between 2007 and 2011 within the “Gap analysis in northwest Russia” (Kobyakov & Jakovlev 2013). As a result of this expedition, new nature monuments were proposed (See Fig 3 and Chapter 1.6). Conservation activities in Zaonezhye Currently planned protected areas in the Republic of Karelia cover an area of 59 400 km2. However, the status of planned protected area alone does not secure nature values. The establishment of protected areas is a long process and in many cases valuable areas have been lost to forestry before the areas have been protected. In Zaonezhye, conservation activities began between 1965 and 1969. Initially, old wooden buildings of historical interest were transported to Kizhi Island where the Kizhi state open-air museum of history, architecture and ethnography was established. 12 Reports of the Finnish Environment Institute 40 | 2014 Later the federal Kizhi zoological nature reserve (Kizhskiy zakaznik) was established (22nd September 1989), based on the recommendations of Tatyana Khokhlova and Oleg Kuznetsov from the Institute of Biology of the KRC RAS. Between 1989 and 1998, ten nature monuments were established in Zaonezhye for the protection of mires (Khokhlova et al. 2000). These regional protected areas cover 1 512 hectares, including Lizh Peninsula, and contain both unique and characteristic Eastern European mire ecosystems. They were established on the basis of the recommendations by the Laboratory of mire ecosystems of the Institute of biology of the KRC RAS. In 1992 KRC RAS produced a feasibility study for the establishment of a nature park with an area of 115 000 ha on Zaonezhye Peninsula (Gromtsev et al. 1992). After detailed ield studies, KRC RAS published an assessment of the protected area (Gromtsev 2013). The proposed Zaonezhsky landscape reserve (zakaznik) covers 106 373 ha, of which 86 839 ha is on land. At the same time, the Karelian NGO “SPOK” prepared recommendations for the protection of southern and eastern Zaonezhye Peninsula (SPOK 2013) (See Chapter 2.3). In the Republic of Karelia, protected areas are created only in accordance with programmes approved by the Russian government. Therefore, planning the establishment of new protected areas is feasible only in cases where such plans are already included in the programmes of the Russian government (protected areas of federal importance: strict nature reserves and national parks) or the government of the Republic of Karelia (protected areas of regional importance: nature parks, nature reserves or zakazniks and nature monuments). The list of planned protected areas in the Republic of Karelia is a part of the Land use plan of the Republic of Karelia until 2030, approved by the government of the republic (Scheme 2012; directive № 102-P from 6th July 2007). It contains two lists concerning the establishment of new protected areas: The irst list includes protected areas that are planned to be established in the irst stage before 2020. Regional nature conservation authorities are presented with all necessary background material for the establishment of these protected areas, including detailed information about the area and its borders as well as ecological values, economic and social characteristics, and the proposed protection regime of the planned protected area. The second list includes perspective new protected areas where red-list species or other natural objects of high conservation value have been recorded. However, the necessary background material for their establishment has not been compiled yet. These protected areas are planned to be established in the second stage between 2020 and 2030. According to the latest changes to the Land use plan of the Republic of Karelia from July 2014 (Regulation 2014), Zaonezhsky landscape reserve, covering 106 373 ha in the northwestern part of Zaonezhye Peninsula, is included in the list of protected areas to be established before 2020. KRC RAS has prepared the background material necessary for the establishment of this protected area (Gromtsev et al. 2013). Another protected area, Zaonezhye nature park, which has been included in the Land use plan of the Republic of Karelia since 2007, is planned to be established in the second stage between 2020 and 2030. It covers 119 600 ha in the southeastern part of Zaonezhye Peninsula (partly overlapping the Zaonezhsky landscape reserve). Threatened species and proposals for their protection There is more than one concept of biodiversity but it is generally accepted that the basic unit of biodiversity is the species. For that reason, biodiversity studies provide the background for conservation. Records of threatened species, included in the Rus- Reports of the Finnish Environment Institute 40 | 2014 13 sian and regional red data books, are therefore of great importance. Establishing new protected areas or expanding existing ones to cover habitats of rare and threatened species is the main legislative tool to protect species and habitats. During the expeditions, the southeastern lowlands of Zaonezhye Peninsula were identiied as important for the conservation of biodiversity. The list of species recorded during these expeditions is impressive: it includes approximately 130 species that are red-listed in the Republic of Karelia (Ivanter & Kuznetsov 2007), more than 100 indicator species of valuable natural forests (according to Andersson et al. 2009) as well as numerous otherwise interesting or rare species, included in international lists of threatened species, such as the IUCN Red List (2014) and the Red Data Book of European Bryophytes (1995), or the 2010 Red List of Finnish species (Rassi et al. 2010). Furthermore, several species of fungi such as Ganoderma lucidum, lichens such as Lobaria pulmonaria and Bryoria fremontii and vascular plants such as Littorella unilora, Lobelia dortmanna and Isoetës lacustris are included in the latest Red list of plants and fungi of the Russian Federation (Trutnev 2008). Also, one butterly species, Clouded Apollo (Parnassius mnemosyne), is included in the Red list of animals of the Russian Federation (Danilov-Danilyan et al. 2001). Detailed descriptions of distributions and ecology of threatened species of federal and regional importance are presented in Chapter 3. The identiied habitats of these species serve as grounds for the establishment of nature monuments (see Chapter 1.6). Besides promoting conservation, the purpose of this book is to gather basic knowledge of the nature on Zaonezhye Peninsula and the adjacent islands. This publication consists of 19 articles on paleogeography, geology and geomorphology as well as the soils and hydrology of Zaonezhye Peninsula. It also includes descriptions of the landscapes and main ecosystems in the area, including forests, mires and meadows. In this book we present for the irst time full lists of vascular plant, bryophyte, lichen, wood-growing fungi and insect species recorded from the area to date. Acknowledgements This book has been prepared owing to great efforts by several researchers from the Karelian Research Centre of the Russian Academy of Sciences as well as the Finnish Environment Institute, Universities of Helsinki and Eastern Finland. We are grateful for all the researchers who took part in the ield work and the preparation of this publication. Professor Pertti Uotila from the University of Helsinki has made useful comments about the manuscript. Grigory Sokolov (Petrozavodsk) has translated some of the articles into English and Minna Hartikainen (London) has made linguistic corrections to this work. The maps (Fig. 1 and 3) have been prepared by Denis Dobrynin from the WWF Russia, Arkhangelsk. The Finnish-Russian working group on nature conservation, chaired by Aimo Saano (Parks & Wildlife Finland, Metsähallitus) and Tapio Lindholm (Finnish Environment Institute), inanced the ield work in 2004. The ield studies in 2013 were implemented by the BPAN pilot project, coordinated by Anna Kuhmonen and Jevgeni Jakovlev (Finnish Environment Institute) in cooperation with the Directorate of regional protected areas of the Republic of Karelia, lead by Denis Maksimov. This book is prepared and published as a part of the BPAN project, inanced by the Nordic Council of Ministers, governments of Finland, Sweden and Norway, and WWF-Russia. This support is cordially acknowledged. 14 Reports of the Finnish Environment Institute 40 | 2014 REFERENCES AЧНОrssШЧ, L., AХОбООЯК, N. M. & KЮгЧОЭsШЯК, E. S. (ОНs). 2009. ., . ., . . . ДSЮrЯОв ШП ЛТШХШРТМКХХв ЯКХЮКЛХО ПШrОsЭs ТЧ NШrЭС-АОsЭОrЧ EЮrШЩОКЧ RЮssТК. − VШХ. 2.IНОЧЭТiМКЭТШЧ ЦКЧЮКХ ШП sЩОМТОs ЭШ ЛО ЮsОН НЮrТЧР sЮrЯОв КЭ sЭКЧН ХОЯОХЖ. SЭ-PОЭОrsЛЮrР.258 Щ. (IЧ RЮssТКЧ). CОЧsЮs ШП ЩШЩЮХКЭТШЧ. 1904. , 1897 . ББVII. . 3( ). ДCОЧsЮs ШП ЭСО ЩШЩЮХКЭТШЧ ШП RЮssТКЧ EЦЩТrО. TСО ЭСТrН ЧШЭОЛШШФ (ЭСО ХКsЭ ШЧО), , 1897 . ББVII.Ж − SЭ.-PОЭОrsЛЮrР. 172 . DКЧТХШЯ-DКЧТХвКЧ ОЭ КХ. (ОНs.). 2001 . . . ( .). ( ). ДRОН DКЭК BШШФ ШП RЮssТКЧ FОНОrКЭТШЧ (КЧТЦКХs)Ж. – AsЭrОХ. MШsМШа. 862 Щ. (IЧ RЮssТКЧ). СЭЭЩ://ЛТШНКЭ.rЮ/НЛ/rЛ/ EХТЧК, G. A., IОsСФШ, E. P., KrКsТХЧТФШЯ, P. V., KЮгЧОЭsШЯ, O. L., LЮФКsСШЯ, A. D. & KСШФСХШЯК, T. ВЮ. (ОНs). 1999. . ., . ., . ., . ., . ., . . . ДKТгСТ ArМСТЩОХКРШ ТsХКЧНs. 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ДBТШНТЯОrsТЭв ТЧЯОЧЭШrТОs КЧН sЭЮНТОs ТЧ ЭСО КrОКs ШП ГКШЧОгСвО PОЧТЧsЮХК КЧН NШrЭСОrЧ LКНШРК sСШrО (ОбЩrОss ТЧПШrЦКЭТШЧ ЦКЭОrТКХs)Ж. − KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 344 Щ. (IЧ RЮssТКЧ). GrШЦЭsОЯ, A. N., GШХЮЛОЯ, A. I., ГСЮrКЯХОЯ, A. P. & IОsСТЧК A. V. 1992. . ., . ., . ., . . К « К ». ДГКШЧОгСвО NКЭЮrО PКrФЖ. 1992. − PrОЩrТЧЭ ШП К presentation at a Presidium session of the Karelian Research Center of Russian Academy of Sciences. PetrozaЯШНsФ. 35 Щ. (IЧ RЮssТКЧ). HЮХЭцЧ, E. 1971. AЭХКs öЯОr ЯтбЭОrЧКs ЮЭЛrОНЧТЧР Т NШrНОЧ. FКЧОrШРКЦОr ШМС ШrЦЛЮЧФsЯтбЭОr. − 2ЧН ОН. – SЭШМФholm. 56+531 p. IОsСФШ, E. P. & PrШЭКsШЯ, ВЮ. G.(ОНs.) 2005.TОЧ вОКrs ШП ЭСО ОМШХШРТМКХ ЦШЧТЭШrТЧР ТЧ ЭСО KТгСТЦЮsОЮЦ-rОsОrЯО. RОsЮХЭs, ЩrШЛХОЦs, ЩОrsЩОМЭТЯОs.KКrОХТКЧ. − RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs, PОЭrШгКЯШНsФ.177 Щ. (IЧ RЮssТКЧ). IUCN 2014: IUCN RОН LТsЭ ШП TСrОКЭОЧОН SЩОМТОs. VОrsТШЧ 2014.3. URL: <СЭЭЩ://ааа.ТЮМЧrОНХТsЭ.ШrР>. DШаЧloaded on 22.10.2014. IЯКЧЭОr, E. V. & KЮгЧОЭsШЯ, O. L. (ОНs.). 2007. . ., . . ( .). ДRОН DКЭК BШШФ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТКЖ. − PОЭrШгКЯШНsФ. KКrОХТК. 368 Щ. (IЧ RЮssТКЧ). KСШФСХШЯК, T. ВЮ., AЧЭТЩТЧ, V. K. & TШФКrОЯ, P. N. 2000. . ., . ., . . ДNКЭЮrО ЩrШЭОМЭОН КrОКs ШП KКrОХТКЖ. − KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs, PОЭrШгКЯШНsФ. 300 Щ. (IЧ RЮssТКЧ). KШЛвКФШЯ, K & JКФШЯХОЯ, J. (ОНs.). 2013. AЭХКs ШП СТРС МШЧsОrЯКЭТШЧ ЯКХЮО КrОКs, КЧН КЧКХвsТs ШП РКЩs КЧН rОЩrОsОЧЭКЭТЯОЧОss ШП ЭСО ЩrШЭОМЭОН КrОК ЧОЭаШrФ ТЧ ЧШrЭСаОsЭ RЮssТК: ArФСКЧРОХsФ,VШХШРНК, LОЧТЧРrКН, КЧН MЮrЦКЧsФ RОРТШЧs, RОЩЮЛХТМ ШП KКrОХТК, КЧН CТЭв ШП SЭ. PОЭОrsЛЮrР. − FТЧЧТsС EЧЯТrШЧЦОЧЭ IЧsЭТЭЮЭО. HОХsТЧФТ. 517Щ. СЭЭЩ://ааа.sвФО.i/ОЧ-US/RОsОКrМС KЮСЦШЧОЧ, A., AФsОЧШЯ, D., DШЛrвЧТЧ, D., FШssЮЦ, K., HöУОr, O., JШЧssШЧ, B-G., JЮЯШЧОЧ, S-K., KСrвsЭКХОЯК, J., LТЧНСШХЦ, T., MКФsТЦШЯ, D., PОЭrШЯ, V., SСТЛОФШ, V., SШЛШХОЯ, N., SЮЭФКТЭТs, O. & TвЮЩОЧФШ, T. 2013: BКrОЧЭs PrШЭОМЭОН ArОК NОаШrФ. RОМШЦЦОЧНКЭТШЧs ПШr sЭrОЧРЭСОЧТЧР ЭСО PrШЭОМЭОН КrО NОЭаШrФ ТЧ ЭСО BКrОЧЭs RОРТШЧ - BPAN ЩШХТМв ЛrТОП. 4 ЩЩ. FТЧЧТsС EЧЯТrШЧЦОЧЭ IЧsЭТЭЮЭО. LКЯrШЯК, N. B., DОЦТНШЯ, I. N., SЩТrТНШЧШЯ . ., GОrЦКЧ K. E., & MОХЧТФШЯ I. V. 2007. . ., . ., . ., . ., . . ДOЧ ЭСО ЛОРТЧЧТЧР ШП КРrТМЮХЭЮrО ТЧ ЭСО ЧШrЭСОrЧ LКФО OЧОРК КrОК. PКХвЧШХШРТМКХ НКЭКЖ. − IЧ: GОШХШРв КЧН МШЦЦОrМТКХ ЦТЧОrКХs ШП KКrОХТК. IssЮО 10. PОЭrШгКЯШНsФ. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. P. 194-206. (IЧ RЮssТКЧ). NШrНТЧ, I. 1972. CКХШЩХКМК, sОМЭ. GКsЩКrrТЧТК ТЧ NШrНОЮrШЩК. − TКбШЧШЦТsФК ШМС ОФШХШРТsФК SЭЮНТОr. UЩsКХК, 184 Щ. NШrrХТЧ, J. P. 1871: FХШrК KКrОХТКО ШЧОРОЧsТs. PКrs I. − NШЭТsОr Юr SтХХsФКЩОЭs ЩrШ FКЮЧК ОЭ FХШrК FОЧЧТМК FörСКЧНХТЧРКr. 12: 1–183. NШrrХТЧ, J. P. 1876: FХШrК KКrОХТКО ШЧОРОЧsТs. PКrs II. LТМСОЧОs. − MОННОХКЧНОЧ. SШМТОЭКЭТs FКЮЧК FХШrК FОЧЧТМК (1): 146 PШЩЩТЮs, B. 1899. FörЭОМФЧТЧР öПЯОr RвsФК KКrОХОЧs CШХОШЩЭОrК. − AМЭК SШМТОЭКЭТs ЩrШ FКЮЧК ОЭ FХШrК FОЧЧТМК 34 (9):1-59. RКЦОЧsФКвК, M. L. 1983. . . ДAЧКХвsТs ШП lШrК ШП ЭСО MЮrЦКЧsФ PrШЯТЧМО КЧН KКrОХТКЖ. − LОЧТЧРrКН. 216 Щ. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 15 RКssТ, P., HвЯтrТЧОЧ, E., JЮsХцЧ, A. & MКЧЧОrФШsФТ, I. (ОНs.) 2010. TСО 2010 RОН LТsЭ ШП FТЧЧТsС SЩОМТОs. ВЦЩтrТsЭöЦТЧТsЭОrТö & SЮШЦОЧ вЦЩтrТsЭöФОsФЮs. HОХsТЧФТ. 685 Щ. RОН DКЭК BШШФ ШП EЮrШЩОКЧ BrвШЩСвЭОs. 1995. – TrШЧНСОТЦ. 291 Щ. RОРЮХКЭТШЧ 2014. . 7 2014 № 88- . 6 2007 № 102. . . ДRОРЮХКЭТШЧ ШП ЭСО GШЯОrЧЦОЧЭ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК 07.04.2014, №88-P. OЧ ЭСО МСКЧРОs ЭШ ЭСО RОРЮХКЭТШЧ ШП GШЯОrЧЦОЧЭ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК 06 .07.2007 № 102- . PОЭrШгКЯШНsФЖ. (IЧ RЮssТКЧ). СЭЭЩ://РШЯ.ФКrОХТК.rЮ/LОРТsХКЭТШЧ/ХКаЛКsО.СЭЦХ?ХТН=11393 SМСОЦО (2012). К , 06.07.2007 № 102- . . . ДSМСОЦО ШП SЩКЭТКХ ЩХКЧЧТЧР ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК. 06.07.2007 № 102- . PОЭrШгКЯШНsФЖ. (IЧ RЮssТКЧ). СЭЭЩ://ааа.РШЯ.ФКrОХТК.rЮ/PШаОr/CШЦЦТЭЭОО/BЮТХН/PХКЧ/ SPOK NGO 2013 , « » ДDШМЮЦОЧЭКЭТШЧ ШП ЭСО МШЦЩХОб ОМШХШРТМКХ ТЧЯОЧЭШrв УЮsЭТПвТЧР ОsЭКЛХТsСЦОЧЭ ШП ЭСО ГКШЧОгСsФв sЭКЭО ЧКЭЮrО ЩКrФЖ. − PОЭrШгКЯШНsФ.108Щ. (IЧ RЮssТКЧ). TrЮЭЧОЯ JЮ. P. ОЭ КХ. (ОНs.). 2008. . . . ( .). ( ). ДRОН DКЭК BШШФ ШП RЮssТКЧ FОНОrКЭТШЧ (ЩХКЧЭs КЧН ПЮЧРТ)Ж. − AsЭrОХ. MШsМШа. 855 Щ. (IЧ RЮssТКЧ). СЭЭЩ://ЛТШНКЭ.rЮ/НЛ/rЛЩ/ТЧНОб.СЭЦ ГСЮrКЯХОЯ, A. I. & OriЧsФв, S. N. 1993. ., . . . ДГКШЧОгСвОЖ. − KТгСsФв VОsЭЧТФ 2. PОЭrШгКЯШНsФ. 217 Щ. (IЧ RЮssТКЧ). 16 Reports of the Finnish Environment Institute 40 | 2014 1 Geology and physical geography of Zaonezhye Peninsula area 1.1 Geological description of Zaonezhye Peninsula Anatoly I. Golubev*, Dmitry V. Rychanchik*, Alexander E. Romashkin* and Alexander K. Polin* *Institute of Geology of Karelian Research Center of Russian Academy of Sciences, 11 Pushkinskaya St., 185610 Petrozavodsk, Karelia, Russia Corresponding author: Alexander E. Romashkin E-mail: roma@krc.karelia.ru Introduction Geologically, Zaonezhye Peninsula is located in the centre of the synclinorial Paleoproterozoic1 Onega structure, which is referred to by some authors as the Onega trough. It is conined to southeastern Fennoscandian Shield and rests on an Archean2 granite gneiss basement. The basement rocks on the peninsula are not exposed. Most of the igneous (effusive and intrusive) and sedimentary rocks (sandstone, siltstone, argillite and carbonate) of the bedrock were formed between 2300–1800 Ma. In the regional Paleoproterozoic stratigraphy these rocks are situated in the Jatulian (2300 – 2100 Ma), Ludicovian (2100 – 1920 Ma) and Kalevian (1920 – 1800 Ma) superhorizons. The positions of the Zaonezhye Peninsula bedrocks in the stratigraphic column of Karelia are shown in Figure 1. The relief of Zaonezhye Peninsula is affected by a system of predominantly NW-trending faults. (Lake Onega bays are also elongated NW.) The area is formed of a series of gently dipping synclines3, separated by narrow anticlines4 with steeply dipping limbs. These have resulted in seven different zones of folding and faulting zones on the Peninsula (Bulavin 1999), also described as linear anticlinal uplifts with longitudinal folds and faults (Fig. 2). The Paleoproterozoic geological and tectonic structure of the area as well as the types and chemical and mineral composition of its bedrocks are described in detail in literature (Glushanin et al. 2011, Reading… 2013) and are discussed briely below. 1 Paleoproterozoic – a period in the Earth’s evolution 2.5 to 1.6 Ga; rocks that formed at that time 2 Archean – a period in the Earth’s evolution older than 2.5 Ga; rocks that formed at that time 3 Syncline – a fold of which the core contains stratigraphically younger rocks; generally concave upward 4 Anticline – a fold, generally convex upward, whose core contains stratigraphically older rocks Reports of the Finnish Environment Institute 40 | 2014 17 Thickness, m Horizon Superhorizon Eonothema Acrothem Absolute age, Ma Sandstone, quartzitic sandstone, siltstone, schist, conglomerates, conglobreccia. Basic sills and lava. 1500 Vepsian 1650 Interbedding of graywacke sandstone, siltstone and carbonaceous argillite with ine-pebble conglomerate interbeds. 1000 Kalevian 1800 700 Suisarian Tuffs, tufites and lava of basalt, picrobasalt and metabasalt composition. Feldspar-quartz sandstone, siltstone, krivozerite, shungite-bearing siltstone and argillite with dolomite, limestone and lydite interbeds. Basic lava and sills. 1200 TransOnega Lower (Karelian) 2100 Dolomite, marbled limestone, quartz sanstone with dolomite matrix, siltstone, schist, basalt. Onega 500 Jatulian Proterozoic Ludicovian 1920 1100 Segozerian Sandstone, quartzitic sandstone, schist, tufite, scarce carbonate rock interbeds, conglomerates and basalt. 2500 500 2400 1000 Sumian Sariolian 2300 Polymictic and granite conglomerates, arkose, graywacke, lava of andesite-basalt composition. Conglomerates, tuff conglomerates, gravelstone, arkose, quartz porphyry of dacite-rhyolite composition. Intermediate and felsic volcanic tuffs, schist, iron formations, carbonaceous and carbonate rocks, conglomerates, basalt, komatiite and andesite. 2000 Upper (Lopian) 3200 >3000 Archean Lithological composition Biotite- and epidote-biotite gneiss, amphibole and kyanite-bearing gneiss and granite gneiss. Fig. 1. General stratigraphic column of Karelia (black line indicates the position of Zaonezhye Peninsula rocks in the column). 18 Reports of the Finnish Environment Institute 40 | 2014 Sedimentary rocks. Jatulian superhorizon, Tulomozero suite. The rocks of the Jatulian superhorizon are the oldest on the Zaonezhye Peninsula.They are only exposed in the centre of the anticlines, which are aligned SE–NW. TСОв ШММЮr КХШЧР ЭСО ЧШrЭСОКsЭ sСШrО ШП ЭСО ЩОЧТЧsЮХК КЧН КrО ШММКsТШЧКХХв ОЧМШЮЧЭОrОН Кs ОХШЧРКЭОН sЭrЮМЭЮrОs КХШЧР ЭСО TКЦЛТЭsв ЯТХХКРО-LКФО PКНЦШгОrШ ХТЧО КЧН ТЧ ЭСО КrОК ЛОЭаООЧ LКФО ВКЧНШЦШгОrШ КЧН ЭСО ЯТХХКРО ШП VОХТФКвК GЮЛК. TСОsО rШМФs СКЯО КХsШ ЛООЧ rОЩШrЭОН ПrШЦ ВЮгСЧв OХОЧв IsХКЧН КЧН ЧШrЭСОrЧ ЩКrЭs ШП SЯвКЭЮФСК BКв (FТР. 2). Fig. 2. Diagram of the geological structure of Zaonezhye Peninsula (made using the maps of Sevzapgeologia (Mikhailyuk et al. 1988), and by USSR Ministry of Geology, PGO Nevskgeologia (Bulavin 1999). Reports of the Finnish Environment Institute 40 | 2014 19 20 Reports of the Finnish Environment Institute 40 | 2014 Fig. 3. Mode of occurrence of carbonate rocks, Tulomozero suite, Yuzhny Oleny Island (Photo Vladimir Makarikhin). Reports of the Finnish Environment Institute 40 | 2014 21 Fig. 4. Diagram of the geological structure of South Oleny Island (6): 1 = Quaternary sediments; 2 = red bed- dolomite unit; 3 = limestone-dolomite unit; 4 = stratigraphic boundaries; 5 = fault lines; 6 = quarry contours; 7 = mode of occurrence; 8-15 = organic residue: 8 = Klimetia, 9 = Butinella, 10 = Calevia olenica (Rjab), 11 = Stratifera ordinata Mak., 12 = oncolites, 13 = Kareliana zonata Korde, 14 = nodular stromatolites, 15 = Olenia rasus But. 22 Reports of the Finnish Environment Institute 40 | 2014 Fig. 5. Limestone kilning furnace, South Oleny Island (Photo Vladimir Makarikhin). Fig. 6. Carbonate pseudomorphs after gypsum, core sample from the Onega Parametric Borehole. The sample is about 8 cm wide. At this level the rocks are dominated by partly marbled dolomite interbedded with limestone, sandstone, phyllite and carbonate breccia. Carbonate rocks contain relics of biogenic stromatolites produced by the vital activity of lower organisms, mainly cyanobacteria, and occur now as carbonate or, occasionally, secondarily siliciied deposits with different forms of internal layering. A distinctive feature of the rocks that occur in this part of the geological column is the anomalously heavy isotope composition of carbonate carbon δ13 (+10 – +18‰, while the isotope composition of carbon in both old and modern carbonates is commonly about 0‰). It should be noted that this anomaly is considered global and carbonates of similar age, displaying the same anomalous isotope composition of carbon, have been reported from several regions of the earth (Melezhik et al. 2005, Melezhik et al. 2010, Reading…2013). The largest exposures of Tulomozero carbonate rock can be found on South Oleny Island (with the area of 0.7x2.5 km), which lies 12 km east of Kizhi Island. It is a unique area of geological and archaeological signiicance (Makarikhin 1992) where quarries and other land use have exposed calcareous-dolomitic rocks that contain an abundance of organic fossils (stromatolites and microphytolites) dating back circa 2 Ga. The carbonate rock deposits are up to 70 m thick, dipping SW and making up the Reports of the Finnish Environment Institute 40 | 2014 23 limb of the NW-trending anticline. In the limb, rocks exhibit small-scale dome-shaped folding. Limestone is commonly conined to the cores of the dome-shaped folds, whereas dolomite constitutes the fold arches. In addition, accumulated dolomite displays small-scale plication (Fig. 3). These rocks have been described in detail in several publications and geological guidebooks (Sokolov & Butin 1961). V.V. Makarikhin and G. . Kononova (1983) provide the most complete and detailed description of the organic fossils. Bedding patterns and spatial relationships of rocks and organic fossils (old algae) can be seen in the rock exposures on the northeast shore of the island and in the quarry walls in the northern and central parts of the island (Fig. 4). On the southwest shore of the island, one can learn more about limestone kilning carried out before 1956 near the Main Quarry where fragments of two furnaces, illed with raw material for kilning, and other traces of past activities have been preserved (Fig. 5). The extensive evidence obtained in the last few years shows that the rocks of the Tulomozero suite were formed in an evaporative environment (in a hot, dry climate). Examples include carbonate pseudomorphs, lesser talc and quartz pseudomorphs after gypsum, nodular and cloud-like (chicken-wire) deposits typical of gypsum aggregates (Fig. 6), carbonate beds after gypsum deformed locally by the volumetric effects of gypsum-anhydrite transitions and scarce pseudomorphs5 after cubic and skeletal halite (rock salt) crystals. Carbonate breccia, which often occurs in this layer, has some features indicating that they have been produced as a result of collapsed salt karst (Melezhik et al. 2005). Fig. 7. Rock salt (halite) with anhydrite inclusions (light and grey). Core sample from the Onega Parametric Borehole. The sample is about 5 cm wide. Fig. 8. Brecciated krivozerites. Lower Zaonezhye subsuite, Svyatukha Bay of Lake Onega (Photo Vladimir Makarikhin). 5 PsОЮНШЦШrЩС Тs К ЦТЧОrКХ аСШsО ШЮЭаКrН МrвsЭКХ ПШrЦ Тs ЭСКЭ ШП КЧШЭСОr ЦТЧОrКХ sЩОМТОs; К ЩsОЮНШЦШrЩС Тs НОsМrТЛОН Кs ЛОТЧР КПЭОr ЭСО ЦТЧОrКХ аСШsО ШЮЭаКrН ПШrЦ ТЭ СКs, О.Р. ХТЦШЧТЭО КПЭОr ЩвrТЭО, qЮКrЭг КПЭОr lЮШrТЭО, etc.). 24 Reports of the Finnish Environment Institute 40 | 2014 Fig. 9. Krivozerite of the Lower Zaonezhye subsuite, core sample from the Onega Parametric Borehole. The sample is about 8 cm wide. Fig. 10. Brecciated maksovite, Berezovets Island (Photo Vladimir Makarikhin). Fig. 11. Maksovite pebble beach, Berezovets Island (Photo Vladimir Makarikhin). Reports of the Finnish Environment Institute 40 | 2014 25 Fig. 12. Anthraxolite, village of Shunga. The sample is about 6 cm long. Geomorphology and Quaternary deposits of Zaonezhye At this level the rocks are dominated by partly marbled dolomite interbedded with limestone, sandstone, phyllite and carbonate breccia. Carbonate rocks contain relics of biogenic stromatolites produced by the vital activity of lower organisms, mainly cyanobacteria, and occur now as carbonate or, occasionally, secondarily siliciied deposits with different forms of internal layering. A distinctive feature of the rocks that occur in this part of the geological column is the anomalously heavy isotope composition of carbonate carbon δ13C (+10 – +18‰, while the isotope composition of carbon in both old and modern carbonates is commonly about 0‰). It should be noted that this anomaly is considered global and carbonates of similar age, displaying the same anomalous isotope composition of carbon, have been reported from several regions of the earth (Melezhik et al. 2005, Melezhik et al. 2010, Reading…2013). The largest exposures of Tulomozero carbonate rock can be found on South Oleny Island (with the area of 0.7x2.5 km), which lies 12 km east of Kizhi Island. It is a unique area of geological and archaeological signiicance (Makarikhin 1992) where quarries and other land use have exposed calcareous-dolomitic rocks that contain an abundance of organic fossils (stromatolites and microphytolites) dating back circa 2 Ga. The carbonate rock deposits are up to 70 m thick, dipping SW and making up the limb of the NW-trending anticline. In the limb, rocks exhibit small-scale dome-shaped folding. Limestone is commonly conined to the cores of the dome-shaped folds, whereas dolomite constitutes the fold arches. In addition, accumulated dolomite displays small-scale plication (Fig. 3). These rocks have been described in detail in several publications and geological guidebooks (Sokolov & Butin 1961). V.V. Makarikhin and G.M. Kononova (1983) provide the most complete and detailed description of the organic fossils. Bedding patterns and spatial relationships of rocks and organic fossils (old algae) can be seen in the rock exposures on the northeast shore of the island and in the quarry walls in the northern and central parts of the island (Fig. 4). On the southwest shore of the island, one can learn more about limestone kilning carried out before 1956 near the Main Quarry where fragments of two furnaces, illed with raw material for kilning, and other traces of past activities have been preserved (Fig. 5). 26 Reports of the Finnish Environment Institute 40 | 2014 The extensive evidence obtained in the last few years shows that the rocks of the Tulomozero suite were formed in an evaporative environment (in a hot, dry climate). Examples include carbonate pseudomorphs, lesser talc and quartz pseudomorphs after gypsum, nodular and cloud-like (chicken-wire) deposits typical of gypsum aggregates (Fig. 6), carbonate beds after gypsum deformed locally by the volumetric effects of gypsum-anhydrite transitions and scarce pseudomorphs6 after cubic and skeletal halite (rock salt) crystals. Carbonate breccia, which often occurs in this layer, has some features indicating that they have been produced as a result of collapsed salt karst (Melezhik et al. 2005). The presence of salt-bearing and sulphate beds in this part of the column is indicated by the so-called “grandfather’s salt pits”, located two kilometres north of Velikaya Guba. Salt-rich water accumulates in these man-made pits, which are about 2x2 m in size. Slightly altered sulphate and salt rock beds have been found also at a depth of 2.5-3 km during the drilling of the Onega parametric hole near Ulitina Novinka, Kondopoga District, west of the Onega Peninsula (Fig. 7). Ludicovian superhorizon, Trans-Onega suite. On the Zaonezhye Peninsula the Trans-Onega suite consists of exposed sedimentary, volcanic-sedimentary and volcanogenic rocks. A characteristic feature of these rocks is the presence, from several percent to dozens of percent, of organic matter (shungite) (Filippov et al. 2007). These exposures are conined to the limbs of the anticlines. The Trans-Onega suite falls into two subsuites, lower and upper, that differ in their mineralogical composition. Rocks of the lower subsuite occur as narrow bands in the northern and southern parts of the peninsula. These bands consist of sandstone, siltstone and argillite interbedded with arenaceous dolomite. In the lower subsuite horizontal bedding is predominant. Occasionally, siltstone and argillite interbeds contain up to 3% (mass) of organic matter. The lower subsuite is characterized by the presence of clay-carbonate and carbonate-clay (marl) rocks with distinctive microrhythmic lamination often referred to in literature as krivozerite (Fig. 8, 9). They occur in all known examples of the lower subsuite of the Zaonezhye suite and can be used as a good marker horizon. In Zaonezhye, he upper subsuite rocks are far more common than the lower subsuite rocks. However, they are also conined to the limbs of NW-trending anticlines. All the rocks in this subsuite are enriched in various amounts of organic matter (shungite) and are therefore dark gray or black. Their organic matter content varies from less than 1 per cent to 70% (mass). The subsuite consists of dark-gray and black tuffaceous-sedimentary and sedimentary rocks bearing sand-, silt- and pelite-sized shungite with carbonate interbeds and predominantly dolomite lenses, often including disseminated sulphide. Also, lenticular, dome-shaped structures with elevated carbon concentrations (at least 20% mass) are encountered in this part of the geological column (Melezhik et al. 2004). This type of rock, often referred to in literature as maksovite (Fig. 10, 11), is now being querried near the Tolvuya in northeastern Zaonezhye Peninsula. It is used predominantly as a substitute for metallurgic coke but is also commonly used in medicine and as an absorbent in water-puriication ilters (Filippov et al. 2007). The rock horizon, referred to in literature as the shungite-lydite-dolomite complex, is well deined in this part of the column of the Paleoproterozoic Onega structure (Melezhik et al. 2009). It is formed of alternating dolomite, lydite and shungite-bearing rock beds (lenses). Dolomite commonly contains organic matter between crystals and within the cores of rhomboid grains. Lydite is a hard dark-gray to black cherty 6 Pseudomorph is a mineral whose outward crystal form is that of another mineral species; a pseudomorph is described as being after the mineral whose outward form it has, e.g. limonite after pyrite, quartz after luorite, etc.). Reports of the Finnish Environment Institute 40 | 2014 27 rock that contains 1-5% (mass) organic matter. There have been attempts to use these rocks as touchstone7, but they have been found too fractured and brecciated. The shungite-lydite-dolomite complex also contains veins of metamorphosed natural bitumens known as anthraxolite (Fig. 12, 13). Practically all the lithotypes of sedimentary rocks in this layer of the column contain fossiled organic remnants such as carbonate rocks – Litophyta (stromatolites and microphytolites); terrigenous, mainly pelite-sized rocks known as acrotarchs; cherty rocks such as styriolite and microfossils; and shungite-bearing rocks termed chemofossils (Makarikhin & Kononova 1983). Kalevian superhorizon, Kondopoga suite. These bedrock exposures cover a large area of up to 10 km wide bands of synclines with gently dipping limbs, extending from southeast to northwest. The column of the Kondopoga suite is a lyschoid sequence in which terrigenous rocks of different particle sizes and mineral compositions (conglomerates, gravelstone, sandstone, siltstone and argillite) are interbedded monotonically to form rhythms, varying from several centimetres to tens of metres in thickness, that are dominated by sedimentary rocks of different particle sizes. Occationally, also thin carbonate intercalations, lenses and concretions are encountered. Conglomerates are conined to the base of the elementary rhythms and occur more in the lower part and less in the upper part of the Kondopoga suite. Sandstones are divided into greywacke and polymictic types, depending on their composition. These stones are light gray to dark gray in colour and display parallel, horizontal and minor undulating cross-bedding. Siltstones are predominantly dark gray to black. The incorporated clasts consist of quartz, feldspar, ine-grained chlorite aggregates and lesser carbonates. Argillites are dark gray to black in colour, with a brownish shade, and they are commonly interbedded with siltstone. Like siltstones, argillites display well-deined horizontal and parallel bedding. Also diastems8, current folds and intrastratal faults are occasionally encountered. Rocks of the Kondopoga suite are characterized by the presence of organic matter (several per cent), which imparts a dark colour to the terrigenous sedimentary rocks (Fig. 14). The suite also contains lens-shaped (oblate) anthraxolite9 aggregates up to dozens of centimeters in diameter and up to 5 cm in thickness. Cyanobacterial (Cyathotes nigoserica Mak.) buildups in terrigenous rocks have been found in the carbonaceous siltstone of the Kondopoga suite. These buildups are morphologically similar to mud cracks and current ripple marks, although different in other features (Makarikhin & Kononova 1983). Kalevian superhorizon, Munozero suite. In the central part of the study area, near Lake Munozero, the bedrock of the Munozero suite is exposed. This is the core of the Munozero syncline. The lower part of the suite consists of dark-gray clastic limestone with thin siltstone and argillite intercalations. The calcite content of these rocks varies from 30 to 80%. The upper portion of the suite contains gray arenaceous dolomite with chert intercalations, siltstone, quartz-feldspathic sandstone with carbonate matrix and arkose. Dolomite commonly displays ine undulation and oblique lamination. Microphytolites of the genus Glebosites (Reitl.) have been found in limestone and oncolites of the genus Osagia (Twenh.) have been reported from dolomite (Makarikhin & Kononova 1983). 7 Touchstone – a black, linty stone, such as a siliciied shale or slate, whose smooth surface was formerly used in testing the purity or ineness of alloys of gold and silver by comparing the streaks left on the stone by rubbing with the metal with the streaks left by an alloy of predetermined composition. 8 Diastem – a relatively short interruption in sedimentation, with little or no erosion before deposition is resumed 9 Anthraxolite – natural bitumen at the metaanthracite stage of coaliication 28 Reports of the Finnish Environment Institute 40 | 2014 Igneous rocks, mineralogeny and commercial minerals of Zaonezhye Peninsula On Zaonezhye Peninsula volcanic rocks can be found in numerous basaltic lava lows and sheets. These dark-gray rocks were produced by volcanic activity (Fig. 15, 16). As a result of paleovolcanological studies of Zaonezhye, areas subjected to the most active volcanism have been identiied and described. Lava lows, varying from 5–7 m to 35–40 m in thickness, are divided into ine-grained varieties at the base, medium- and coarse-grained varieties at the centre and ine-to medium-grained amygdaloidal varieties at the top. Rocks in these lava lows are fairly homogeneous in their petrographic composition, texture and structure. Predominantly, basalts consist of ine plagioclase laths and isomorphic tabular pyroxene in strongly chloritized matrix. Commonly the amygdales are illed with chlorite, lesser quartzite and quartz. Flow bedding at the top of lava lows is characterized by an abundance of chlorite and chlorite-calcite amygdales, extending as “layers” for dozens of metres along the strike. Ore minerals are represented by pyrite and leucoxenized titanomagnetite and lesser chalcopyrite. Brecciation is occasionally observed at the top of the lava low; hydrothermal quartz-calcite veins and veinlets evolve in these zones. Due to the highly hematized (oxidized) lava in the area, the colour of its rocks is often brown. Gabbro-dolerite sills represent sub-volcanic rocks. In composition these rocks are identical to lava deposits but differ in their degree of recrystallization and, hence, structure (Golubev & Svetov 1983). Gabbro-dolerite sills form at least 40–45 m thick structures with distinct crystallization, from ine-grained varieties at the margins to coarse-grained and occasionally pegmatoid varieties at the centre of the structure. The rocks are dark gray to brown in colour and fairly dense, often forming a conspicuous relief of high scarps or ridges. They are easily traceable for dozens of kilometres along the strike, folding together with host rocks. The volcanic breccia on Radkolye Point in the Zaonezhye Peninsula is fairly exotic. The relics of the Radkolye volcanic ediice were mapped in 1972 during paleovolcanological studies on the southwestern shore of Bolshoi Lelikovsky Island (Svetov & Golubev 1978). Due to erosion, only a small portion of the volcanic neck is preserved. Eruptive channel rocks can be found in rocky scarps at its northeastern and southern endocontacts, while its entire western and northern parts are under the Lake Onega water level. The preserved part of the volcanic neck is described as a rocky, two-peaked roches moutonnée created by the glacier. It is 8–10 m higher than the surrounding rocks (Fig. 17). Morphologically, the volcanic neck is a round body, presumably about 200 m in diameter. The base of the volcanic structure on Radkolye Point consists of volcanogenic sedimentary-effusive rocks of the Zaonezhye volcanic complex. It forms a gently dipping syncline with a well-exposed northeastern limb that extends along the southwestern shore of the island. On the island the volcanogenic structure forms a series of narrow and gently dipping anticlines and synclines elongated towards northwest. In southeastern parts of the island, effusive rocks are crosscut by coarse- to medium-grained gabbro-dolorite sill that forms a sheeted body, folded with host rocks. The fold axes generally plunge northwest. Direct contacts between the neck and the host rocks of the Zaonezhye suite have only been reported from its southern parts, while in the rest of the area the contact zone is buried under deluvial piles of rocks and unconsolidated Quaternary sediments. Near the water’s edge, in the steep scarp located in the southern endocontact zone, vertically dipping eruptive breccia cuts gently dipping basaltic lava. The rough contact surface can be traced for over several metres. In both cases, the contact plane dips steeply north to northwest at about 80–85º. Reports of the Finnish Environment Institute 40 | 2014 29 Coarse clastic rocks, morphologically similar to the eruptive breccia described above, have been encountered 3.5 km northwest of Point Radkolye, on one of nameless islands of the Lambinskie Islands. The various rocks of the peninsula are a treasure trove for nature lovers. Semi-quantitative and quantitative spectral analyses were carried out to study minor elements and their concentrations in the mineralogical composition of the rocks. In addition these analyses determined the genesis, conditions of formation and the position of horizons where nonferrous metals may occur. All the above rock varieties contain low concentrations of ore-bearing elements, carbonate and cherty (lydite-like) rocks containing the lowest concentrations. However, certain elements are conined to certain rock varieties in certain structures, indicating geochemical specialization (Golubev et al. 1984). Ore-bearing elements of nonferrous metals are present in carbonaceous rocks mainly as sulides. Although all the rocks of the Zaonezhye suite are contaminated with sulides, ore matter is conined to second-member rocks, i.e. shungitic tufites. Depending on the metamorphic grade, ore mineralization is of the pyrite type and ore matter is either pyrite or pyrrhotite. Formation of pyrite with smaller quantities of chalcopyrite, sphalerite and pyrrhotite is characteristic of greenschist facies. Sulides occur as beds, lit-par-lit intrusions, pockets, concretions, globules, coating around rock and mineral fragments, veins and veinlets. Conditions during their formation determine the mineralization of primary sedimentary and metamorphogenetic-hydrothermal ore in mineralized schist. Spectral and chemical analyses have shown that the ores contain Zn, Ni, Co and Cu as well as smaller quantities of Ag, Mo, Pb and Au. Nonferrous metal concentrations are at least one order of magnitude higher in concretions than in host tufites with lit-par-lit ore injections. Studies of sulphide mineralization have shown that Cu, Co, Ni, Zn, Pb, Ag and Au are concentrated in secondary sulphide redistribution during epigenesis and metamorphism. Pyrrhotite mineralization is not characteristic of the carbonaceous rocks in the Onega trough. Pyrrhotite is formed when ine-grained pyrite is recrystallized into massive pyrite interbeds. It also occurs in tectonically active zones where graphite is formed instead of shungite and pyrite is replaced by pyrrhotite. Volcanic emanations during the three phases of Zaonezhye volcanism are the source of ore matter in Karelian carbonaceous rocks. The hydrothermal ield of the most active second phase of Zaonezhye volcanism has been identiied by facies and paleovolcanological reconstructions in the active submarine volcanic area of the Onega trough. In the Zaonezhye suite column, this zone consists of shungite rocks as well as overlying shungite tuffs that are most likely to contain nonferrous metals. Among other evidence, correlation between ore-forming processes and volcanic events, sheeted shapes of ore bodies, preserved primary structures of rocks and ores as well as the pattern of sulphide mineralization suggest that ore-forming processes were similar in the black shales of the Zaonezhye complex and the Baltic Shield (Golubev et al. 1984). Clearly the geochemical characteristics of the study area are affected by structural dislocation and faulting zones, to which complex Cu-U-Mo-V ore deposits are conined. These zones contain from elevated to anomalous concentrations of Cu, Co, Ni, Cr, Zn, Mo, Bi, Au, Ag, Se, Pt, Pd as well as other elements. Ore-forming processes are indicated mainly by near-fault sodium metasomatism, micatization and the above spectrum of anomalous element concentrations. Ore-forming processes are determined by axial fauls and shear zones, as well as alternating dolomite, siltstone, schist, basalt and gabbro-dolerite deposits of considerably different physical, mechanical and geochemical properties. Structural dislocation and fault zones are described in detail in A.V. Bulavin’s monograph “Metallogeny of Karelia” (Bulavin 1999). 30 Reports of the Finnish Environment Institute 40 | 2014 For commercial mining, most promising are the ore-bearing deposits associated with the formation of uranium, noble metal and vanadium in structural dislocation and faulting zones. Such deposits occur in the Kosmozero, Padma and Shulginovskoe ore ields in the Onega Ore Province of the Onega-Belozero mineralogenic zone. During the past few decades Nevskgeologia GGP has discovered vanadium-rich deposits in Srednyaya Padma, Tsarevskoe, Vesenneye, Verkhnyaya Padma and Kosmozero as well as other deposits in metasomatised rocks - the carbonaceous siltstone and schist occurring at the base of the Zaonezhye suite of the Ludicovian superhorizon. The total reserves of vanadium pentoxide in the Onega Ore Province, including prospective reserves of all deposits and occurrences, are estimated at 556 000 tons. Most of these deposits (C1+C2 resources of 332 500 tons), are concentrated in the active reserves of the Padma and Kosmozero ore ields (Bulavin 1999). Fig. 13. Anthraxolite, village of Shunga. Fig. 14. Mode of occurrence of Kondopoga suite rocks, Nigozero quarry (Photo Vladimir Makarikhin). Reports of the Finnish Environment Institute 40 | 2014 31 Fig. 15. Contact between globular-pillow lava (above) and silty sandstone (below). Lambas-Ruchei (Photo Vladimir Makarikhin). Fig. 16. Globular-pillow unit in lava, Lambas-Ruchei (Photo Vladimir Makarikhin). 32 Reports of the Finnish Environment Institute 40 | 2014 Fig. 17. Diagram of the geological structure of the Radkoila volcanic ediice (14): 1 = plagioclase-pyroxene basalt dykes; 2 = eruptive breccia; 3 = globular-pillow basalt lava; 4 = basalt lava-breccia; 5 = amygdaloidal basalt; 6 = massive chilled basalt; 7 = cluster of amygdales in basalt lows; 8 = tuff siltstone and tuffaceous siliceous schist; 9 = tuffaceous sandstone; 10 = low direction; 11 = mode of occurrence (a – bedding, b – jointing); 12 = dominant exposure contours; 13 = geologic boundaries (a – assumed, b – traced); 14 = cliff scarps; 15 = sulphide mineralization zones. Reports of the Finnish Environment Institute 40 | 2014 33 REFERENCES BЮХКЯТЧ, .V. 1999. . . . CШЦЩХОб МШЩЩОr-ЮrКЧТЮЦ-ЦШХвЛНОЧЮЦ-ЯКЧКНТЮЦ ШrО ПШrЦКЭТШЧ ТЧ ЭСО ПШХНТЧР-КЧН-ПКЮХЭТЧР гШЧОs ШП ЭСО OЧОРК sЭrЮМЭЮrОЖ. − MОЭКХХШРОЧв ШП KКrОХТК. PОЭrШгКЯШНsФ. Щ. 246–261. (IЧ RЮssТКЧ). GХЮsСКЧТЧ, L.V., SСКrШЯ, N.V. & SСМСТЩЭsШЯ, V.V. (ОНs.), 2011. . ., . ., . . ( . ). ( , , ) ДPКХОШЩrШЭОrШгШТМ OЧОРК sЭrЮМЭЮrО (РОШХШРв, ЭОМЭШЧТМs, НООЩ sЭrЮМЭЮrО КЧН ЦТЧОrКХШРОЧвЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 431 Щ. (IЧ RЮssТКЧ). GШХЮЛОЯ, .I., AФСЦОНШЯ, . ., & GКХНШЛТЧК, L.P. 1984. . ., . ., . . . ДGОШМСОЦТsЭrв ШП ЭСО LШаОr PrШЭОrШгШТМ ЛХКМФ sСКХО МШЦЩХОбОs ТЧ ЭСО KКrОХТК-KШХК rОРТШЧЖ. – LОЧТЧРrКН. 192 Щ. (IЧ RЮssТКЧ). GШХЮЛОЯ, .I. & SЯОЭШЯ, A.P. 1983. . ., . . . ДGОШМСОЦТsЭrв ШП ЛКsКХЭs ЩrШНЮМОН Лв ЩХКЭПШrЦ ЯШХМКЧТsЦ ТЧ KКrОХТКЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 191 Щ. (IЧ RЮssТКЧ). FТХТЩЩШЯ, M.M. ОЭ КХ. (ОНs.), 2007. . . . ( .). ). ДAЭХКs ШП ЭСО sСЮЧРТЭО-ЛОКrТЧР rШМФ ЭОбЭЮrОs КЧН sЭrЮМЭЮrОs ШП ЭСО OЧОРК sвЧМХТЧШrТЮЦЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 80 Щ. (IЧ RЮssТКЧ). MКФКrТФСТЧ, V.V. 1992. . . . ДSТЭОs ШП РОШХШРТМКХ sТРЧТiМКЧМОЖ. – IЧ: GОШХШРв КЧН ЩrШЭОМЭТШЧ ШП ЦТЧОrКХ rОsШЮrМОs ТЧ KКrОХТК. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ, Щ. 60–98. (IЧ RЮssТКЧ). MКФКrТФСТЧ, V.V. & KШЧШЧШЯК, G. . 1979. . ., . . . ДLШаОr PrШЭОrШгШТМ ЩСвЭШХТЭОs ШП KКrОХТК. –LОЧТЧРrКН. 208 Щ. (IЧ RЮssТКЧ). MОХОгСТФ, V. A., FТХТЩЩШЯ, M. M. & RШЦКsСФТЧ A. E. 2004. A РТКЧЭ PКХКОШЩrШЭОrШгШТМ НОЩШsТЭ ШП sСЮЧРТЭО ТЧ NА RЮssТК. − OrО РОШХШРв rОЯТОаs 24: 135–154. MОХОгСТФ,V.A., FКХХТМФ, A.E., FТХТЩЩШЯ, M.M., LОЩХКЧН, A., RвМСКЧМСТФ, D.V., DОТЧОs, ВЮ.E., MОНЯОНОЯ, P.V., RШЦКsСФТЧ, A.E. & SЭrКЮss, H. 2009. PОЭrШХОЮЦ sЮrПКМО ШТХ sООЩs ПrШЦ К PКХКОШЩrШЭОrШгШТМ ЩОЭrТiОН РТКЧЭ ШТХiОХН. − TОrrК NШЯК 21: 119–126. MОХОгСТФ, V.A., FКХХТМФ, A.E., RвМСКЧМСТФ, D.V. & KЮгЧОЭsШЯ, A.B. 2005. PКХКОШЩrШЭОrШгШТМ ОЯКЩШrТЭОs ТЧ FОЧЧШsМКЧНТК: ТЦЩХТМКЭТШЧs ПШr sОКаКЭОr sЮХЩСКЭО, ЭСО rТsО ШП КЭЦШsЩСОrТМ ШбвРОЧ КЧН ХШМКХ КЦЩХТiМКЭТШЧ ШП ЭСО δ13C ОбМЮrsТШЧ . − TОrrК NШЯК 17 (2): 141–148. MОХОгСТФ, V.A., HЮСЦК, H., CШЧНШЧ, D.J., FКХХТМФ, A.E. & АСТЭОСШЮsО, M.J. 2007. TОЦЩШrКХ МШЧsЭrКТЧЭs ШЧ ЭСО PКХОШЩrШЭОrШгШТМ LШЦКРЮЧНТ-JКЭЮХТ МКrЛШЧ ТsШЭШЩТМ ОЯОЧЭ. − GОШХШРв 35: 655–658. MОХОгСТФ, V., LОЩХКЧН, A., RШЦКsСФТ,Ч A., RвМСКЧМСТФ, D., MОsХТ, M., FТЧЧО, T. E. & CШЧгО, R. 2010. TСО GrОКЭ OбТНКЭТШЧ EЯОЧЭ RОМШrНОН ТЧ PКХОШЩrШЭОrШгШТМ RШМФs ПrШЦ FОЧЧШsМКЧНТК. − SМТОЧЭТiМ DrТХХТЧР 9: 23–29. MТФСКТХвЮФ, . . ОЭ КХ. 1988. 1:200 000 МШЦЩШsТЭО ЦКЩ ШП ЭСО OЧОРК sЭrЮМЭЮrО. − 1984–1987 rОЩШrЭ ШЧ PrШУОМЭ -12–48. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ, SСКrШЯ, N.V. & SСМСТЩЭsШЯ, V.V. (ОНs.), KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. – PОЭrШгКЯШНsФ 431 Щ. (IЧ RЮssТКЧ). RОКНТЧР ЭСО ArМСТЯО ШП EКrЭС’s OбвРОЧКЭТШЧ. 2013. VШХЮЦО 3: GХШЛКХ ОЯОЧЭs КЧН ЭСО FОЧЧШsМКЧНТКЧ ArМЭТМ RЮssТК – DrТХХТЧР EКrХв EКrЭС PrШУОМЭ. – IЧ: MОХОгСТФ, V.A., KЮЦЩ, L.R., FКХХТМФ, A.E., SЭrКЮss, H. HКЧsФТ, E.J., PrКЯО, A.R. & LОЩХКЧН, A. (ОНs.), SОrТОs: FrШЧЭТОrs ТЧ EКrЭС SМТОЧМОs. SЩrТЧРОr, HОТНОХЛОrР. Щ. 1049–1552. SЯОЭШЯ, .P. КЧН GШХЮЛОЯ, .I. 1978. RКНФШТХК ЯШХМКЧТМ ОНТiМО. – IЧ: PrШЭОrШгШТМ ЯШХМКЧТМ ОНТiМОs ШП KКrОХТК. LОЧТЧРrКН. Щ. 128–132. SШФШХШЯ, V. . & BЮЭТЧ, R.V. 1961. . ., . . . ДGОШХШРТМКХ iОХН ЭrТЩ ЭШ SШЮЭС OХОЧв IsХКЧН КЧН VШХФШsЭrШЯЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ, 58 Щ. (IЧ RЮssТКЧ). 34 Reports of the Finnish Environment Institute 40 | 2014 1.2 Geomorphology and Quaternary deposits of Zaonezhye Tatyana S. Shelekhova Institute of Geology of Karelian Research Center of Russian Academy of Sciences, 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia E-mail: shelek@krc.karelia.ru Introduction The geomorphology and Quaternary deposits of Zaonezhye Peninsula have been described extensively in literature (Biske et al. 1971, Lukashov et al. 1993, Demidov & Lavrova 2000, Lukashov 2000, Demidov 2005 a,b,c, Demidov 2006, Shelekhova 2013). Zaonezhye is a unique area that has no equivalent in Karelia, or Russia. The mosaic structure of its crystalline basement and the diverse composition of its bedrock are responsible for its highly rugged topography. The unique tectonic structure of Zaonezhye, together with the multiple advances of glaciers and the distinctive evolution of the area after ice retreat gave rise to genetically and compositionally diverse Quaternary rock complexes and unique landforms – the basis for the biologically diverse landscapes of today. Precambrian crystalline rocks are covered by thin Quaternary deposits, formed from rocks carried by the last Scandinavian ice sheet during the Late Valdai glaciation (Fig. 1.). Holocene peat, lake, seismogravitational aeolian and alluvial sediments occur locally. Considerable variations in altitude (up to 100 m) are due to the alternation of narrow NW-trending selkä ridges and interridge depressions occupied by lakes, deep bays and bogs. Older Quaternary deposits may have been preserved in these depressions and, if found, should be further studied. Glacial deposits, consisting of moraine covering highly weathered and fractured Precambrian rocks, are widespread in the area. The most common glacial deposits are gabbro-dolerites, crosscut by at least 3–5 m deep fractures. Since fractured gabbro-dolerites are less resistant to glacial erosion, the resulting moraine consists of coarse local clasts. There are two types of moraine in Zaonezhye. Type I is formed of bedrocks poorly resistant to glacial exaration, such as gabbro-dolerite or slightly fractured and mildly weathered schist, occurring in a rugged relief. Coarse clasts make up 85–90% of this local moraine, produced by the destruction and short-distance redeposition of local bedrocks. The distance of glacial transport varies from hundreds of metres to several kilometers. Coarse clastic fractions (> 1 cm) account for at least 40–50%. Type II is schistose moraine, containing 25–40% of coarse clasts, composed of granite, granite-gneiss and other rock clasts. It has been transported by the glacier from the Onega-Segozero watershed and it rests on either bedrock or local coarse clastic moraine. In sand fractions, quartz dominates over feldspar. These deposits are better Reports of the Finnish Environment Institute 40 | 2014 35 sorted than the moraines of Type I. Up to 25–30% of clasts have been transported for over dozens of kilometres. The petrographic, mineralogical and chemical composition of the moraine depends completely on the mineralogical composition of the basement rock. It varies in thickness from dozens of centimeters on top of selkä ridges to 3–10 m in depressions between the selkäs. In spite of its sandy and sandy loam composition, the moraine displays poor iltrating properties. As a result, such areas are paludiied. Fluvioglacial deposits consist of well-sorted sand, gravel, pebble and sand. These deposits form esker ridges, luvioglacial deltas and debris cones that indicate the locations of major glacial meltwater systems and periglacial lakes resulting from the deglaciation of the area. Fluvioglacial deposits include 10–15 m thick deposits resting on moraine and bedrock, displaced and folded by the movements of the ice margin. Also esker ridges and abraded luvioglacial deltas occur. The mineral and petrographic composition of the luvioglacial deposits relects the bedrock and moraine from which they have been derived. Lacustrine-glacial deposits are widespread in Zaonezhye and consist of periglacial Lake Onega sediments, including seasonally accumulated varved clay and sandy-silty sediments. As a result of the melting ice sheet as well as the irregular glacial isostatic adjustment of the earth’s crust, most of Zaonezhye Peninsula was looded by the periglacial Lake Onega. During this time, water levels reached altitudes of 100–110 m in northern parts and about 80–90 m in southern parts of the peninsula. Varved clay, unaffected by the washout caused by the stadial drop in the Lake Onega water level in late and post-glacial times, is encountered in topographic lows at altitudes below 50–60 m. In some lakes, e.g. Lake Isaevo, the top of the varved clay lies at an absolute altitude of 80 m. Clay, varying from dozens of centimeters to 7–10 m in thickness, rests on moraine and is often conined to distal portions of luvioglacial deltas (Glinyanoe bog near the village of Bor Pudantsev). Continuous varved clay beds, covering an area of more than 1–2 km2, are known from southeastern shores of Lake Kosmozero, south of the village of Lambasruchei, and from the bottoms of all large lakes of Zaonezhye Peninsula. Due to its poor iltration properties and water resistance, clay contributes to the paludiicationc of the area. The mineral and chemical composition of varved clay depends on the composition of the bedrock and the overlying moraine (Demidov 2000, 2005). Lacustrine deposits, consisting of sand, loamy sand and pebble, occur on the shores of Lake Onega at an absolute altitude of 50–60 m. Lacustrine deposits form short beaches, aggradation terraces (Peski special landscape area on the southwest shore of Lake Padmozero) and beach barriers (Lambasruchei). There are also small beaches, composed of older luvioglacial sand and gravel deposits on the shores of Ladmozero, Vanchozero, Padmozero and other lakes. Sediments are accumulated at the bottom of numerous lakes and bays where glacial lacustrine varved clay is covered by a ca. 3-m-thick layer of homogeneous gray silt, followed by sapropel and sometimes diatomites. Organic deposits can be up to 7 m thick (Nizhneye Myagrozero). Also bog iron ore (limonite) has been encountered at the bottom of some lakes. Bottom sediments in lakes located near large-scale paleoseismic dislocations in bedrocks, such as Lake Putkozero and Svyatukha Bay, display folding caused by post-glacial earthquakes. Post-glacial earthquakes have also produced seismocolluvial deposits, consisting of coarse clastic talus and collapse. Seismocolluvial deposits occur on a limited scale and are conined to big cliffs of tectonic origin. Some seismic collapses are up to 100 km wide and 10 m thick, extending 2 km. Peat-bog deposits ill up paludiied interridge depressions of tectonic origin, which in the past would have formed 2–4 km long and 200–400 m wide lakes or bays with their shores. Peat-bog deposists consist of woody-grass and grass lowland peat that 36 Reports of the Finnish Environment Institute 40 | 2014 varies from several metres to over 8 m in thickness. In some lakes, grass and grassmoss bogs occur as loating mats. Aeolian deposits consist of well-sorted ine-to medium-grained sand and occur as small, narrow strips on lakeshores. As the river network is young and poorly developed, alluvial deposits consist of coarse clastic sand-pebble streambed alluvium. Geomorphology Zaonezhye has a highly diverse relief. Denudation, tectonic, glacial and luvioglacial landforms are common. Folding and faulting of crystalline rocks as well as intense neotectonic movements have affected the present-day relief of Zaonezhye. Old structural forms are responsible for the morphology and orientation of elementary surfaces. Elevated surfaces are elongated and exposed, with an orientation parallel to fold and fault structures. Multiple tectonic movements have formed a distinctive, obsequent relief in Zaonezhye. The obsequent relief is a result of the geological structure of Zaonezhye caused by wide-open synclines and narrow, heavily deformed anticlines that are interrupted by longitudinal faults. Synclines form elevated ridges and mountain massifs with relatively high plateaus, while anticlines form valleys occupied by rivers or lakes. Conined to some of the anticlines are structurally complex folding and faulting zones that host uranium-vanadium-rare metal deposits and occurrences (Bilibina et al. 1991). In parts of Zaonezhye Peninsula, individual crustal blocks have been scattered vertically along the faults as a result of neotectonic movements. Therefore, the Zaonezhye relief can be divided into three tiers: upper tier with an absolute altitude of 107–147 m; middle tier with an altitude of 60–100 m; and lower tier with an altitude of 33–60 m (Lukashov 2000). Topographically Zaonezhye can be subdivided into western and eastern parts as well as the elevated Svyatukha Bay – Lake Putkozero watershed. Western Zaonezhye is an elevated massif with a highly rugged surface. Its highest surfaces are narrow, elongated ridges. These linear ridges are 1.6–14 km long and 0.6– 1.4 km wide with 5–40 m high scarp-like slopes. Lake basins occupy piedmonts and lowlands. There is a distinctive pattern of topographic tiers: The upper tier occupies the largest area with altitudes of up to 147 m, while the middle and lower tiers form narrow strips at the rims of the elevated massif. Boundaries between these tiers consist of a series of step-like scarps and steep slopes. Western Zaonezhye is characterized by high vertical (67–101 m) and horizontal ruggedness due to the rugged shoreline of Lake Onega basins and bays. There are few river valleys, although lake basins are common. Crystalline rocks occur over a large area. There are no unconsolidated Quaternary sediments, therefore crystalline rocks are covered by a 1–2 cm layer of modern eluvium. In topographic depressions, such as the Lake Kosmozero – Unitsa Bay basin, crystalline rocks are covered by a 1.5–3 m layer of moraine. There is an esker ridge here with a delta extending northwest. Eastern parts of Zaonezhye Peninsula differ substantially from its western parts. There is no upper tier in the relief, while its middle and lower tiers form extensive structures, rather than narrow strips. In southeastern parts of the peninsula, the middle tier occupies an area of about 380 km2. Its highest surfaces are located at an absolute altitude of 60–100 m. Vertical ruggedness varies from 44 to 60 m. The middle tier consists of a plain with gently sloping lat-topped ridges without a well-deined foot of the hill. These ridges are 2.8–16.4 km long, 0.8–2.0 km wide and up to 5–15 m high. They are separated by large 1.5–2.5 km wide and 5–10 km long depressions with a lat bottom and indistinct boundaries. The lower and middle tiers cover roughly equal areas, while the lower tier is conined to the coastal zones of the peninsula. Reports of the Finnish Environment Institute 40 | 2014 37 This type of relief is most common in the northern parts of Zaonezhye Peninsula, near Padmozero and Tolvuya villages. In southern parts of Zaonezhye Peninsula, the lower tier is found near Lake Yandomozero. In general, Southern Zaonezhye is characterized by gently undulating plains with gently sloping, poorly deined ridges and bars. Watersheds are located at an absolute altitude of 60 m and vertical ruggedness is 6–18 m. The hydrographic network of eastern Zaonezhye is markedly different from western Zaonezhye. There are only two large lakes here, Putkozero and Padmozero, but river systems are more developed. Crystalline rocks of eastern Zaonezhye, unlike those of western Zaonezhye, are almost completely covered by a 6–10 m thick layer of Quaternary rocks. The middle tier is dominated by moraine, formed of boulder and loamy sand, as well as luvioglacial esker ridges and deltas, formed of sand, gravel and pebble. In the lower tier, sand, silt and clay form lacustrine-glacial and lacustrine plains. The elevated Svyatukha Bay − Lake Putkozero watershed represents a typical tectonic-denudation selkä landscape, completely lacking Quaternary deposits or covered by up to 1-m-thick moraine. The thickness of the moraine increases to at least 10 m in depressions between selkäs, where it is often covered by varved clay, glacial lacustrine loamy sand or inequigranular sand. Tectonic scarps and seismocolluvial debris cones surround western and eastern parts of the watershed. These cones are up to 2 km long chaotic piles of sharply angular blocks, which vary in size from dozens of centimeters to 5 m along the long axis (e.g. Mount Zimnyaya, Mount Gorodok, Mount Sypun and the Paltega area). Near Unitsa Bay, towards Kazhma-Velikaya Guba, the area is traversed by luvioglacial systems of esker ridges and deltas, composed of a circa 20–30 m thick layer of sand and gravel, that extend from northwest to southeast and from north to south near Padmozero-Tipinitsy and Gankovskoe-Kuzaranda. Glacial lacustrine sediments such as varved clay, loamy sand and sand occur along the shores of large lakes and in topographic depressions at absolute altitudes below 70 m. In Velikaya Guba, Yandomozero and Glinyanoe Mire near the village of Bor Pudantsev, varved clay is 6–7 m thick. Beaches, consisting of pre-Holocene luvioglacial sand and gravel deposits, stretch along the shores of Lakes Ladmozero and Vanchozero. REFERENCES BТsФО, G.S., LКФ, G.Ts., LЮФКsСШЯ, .D., GШrвЮЧШЯК, N.N. & IХвТЧ V. . 1971. . ., . ., , . ., . ., . . ДSЭrЮМЭЮrО КЧН ОЯШХЮЭТШЧ ШП LКФО OЧОРК ЛКsТЧЖ. – PОЭrШгКЯШНsФ: KКrОХТК.74 Щ. (IЧ RЮssТКЧ). DОЯвКЭШЯК, E. I. 1972. . . . ДPКХвЧШХШРТМКХ НОsМrТЩЭТШЧ ШП ЭСО UЩЩОr QЮКЭОrЧКrв НОЩШsТЭs ШП KКrОХТКЖ. – IЧ: QЮКЭОrЧКrв РОШХШРв КЧН РОШЦШrЩСШХШРв ШП ЭСО ОКsЭОrЧ BКХЭТМ SСТОХН. LОЧТЧРrКН. Щ. 59–96. (IЧ RЮssТКЧ). DОЦТНШЯ, I.N. 1993. . . . Д ЯШХЮЭТШЧ ШП РХКМТКЭТШЧ КЧН ЭСО ПШrЦКЭТШЧ ШП QЮКЭОrЧКrв НОЩШsТЭs ШЧ ЭСО ГКШЧОгСsФв PОЧТЧsЮХКЖ. – KТгСsФв ЯОsЭЧТФ.ГКШЧОгСвО 2: 13–23. (IЧ RЮssТКЧ). DОЦТНШЯ, I.N. & LКЯrШЯК, N.B. 2000. . ., . . . ДCСКrКМЭОrТsЭТМs ШП QЮКЭОrЧКrв НОЩШsТЭs КЧН QЮКЭОrЧКrв РОШХШРТМКХ ОЯШХЮЭТШЧЖ. – IЧ: IЧЯОЧЭШrв КЧН sЭЮНв ШП ЛТШНТЯОrsТЭв ШЧ ЭСО ГКШЧОгСsФв PОЧТЧsЮХК КЧН ТЧ NШrЭСОrЧ PrТХКНШгвО. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 28–40. DОЦТНШЯ, I.N., LКЯrШЯК, N.B., SСОХОФСШЯК, .S. & VКsФШ .V. 2003. . ., . ., . ., . . . ДOЧ ЭСО HШХШМОЧО lЮМЭЮКЭТШЧs ШП LКФО OЧОРКЖ. – IЧ: TСОШrОЭТМКХ КЧН КЩЩХТОН ЩrШЛХОЦs ТЧ ЦШНОrЧ ХТЦЧШХШРв. BОХКrЮs SЭКЭО UЧТЯОrsТЭв. MТЧsФ. Щ. 151–152. DОЦТНШЯ, I.N. 2004. . . . ДBШЭЭШЦ sОНТЦОЧЭs КЧН ЯКrТКЭТШЧs ТЧ LКФО OЧОРК ХОЯОХ ТЧ ЭСО LКЭО GХКМТКХ PОrТШНЖ. –IЧ:GОШХШРв КЧН ЮsОПЮХ ЦТЧОrКХs ШП KКrОХТК. IssЮО 7. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 207–218. (IЧ RЮssТКЧ). 38 Reports of the Finnish Environment Institute 40 | 2014 DОЦТНШЯ, I.N. 2005 К. . . . ДQЮКЭОrЧКrв НОЩШsТЭs ШП ГКШЧОгСвОЖ. – IЧ: EЧЯТrШЧЦОЧЭКХ ЩrШЛХОЦs ТЧ ЭСО ЦТЧТЧР ШП ЭСО SrОНЧвКвК PКНЦК НОЩШsТЭ. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 14–19. (IЧ RЮssТКЧ). DОЦТНШЯ, I.N. 2005 Л. . . . DОРrКНКЭТШЧ ШП ЭСО LКЭО VКХНКТ РХКМТКЭТШЧ ТЧ LКФО OЧОРК ЛКsТЧЖ. – IЧ: GОШХШРв КЧН ЮsОПЮХ ЦТЧОrКХs ШП KКrОХТК. IssЮО 8. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ.134–142. DОЦТНШЯ, I.N. 2005 М. . . . ДDОРrКНКЭТШЧ ШП ЭСО LКЭО VКХНКТ РХКМТКЭТШЧ ТЧ LКФО OЧОРК ЛКsТЧ. – QЮКrЭОr-2005, SвФЭвЯФКr. GОШЩrТЧЭ. Щ. 115–117. (IЧ RЮssТКЧ). DОЦТНШЯ, I.N. 2006. . . , . ДOЧ К ЦКбТЦЮЦ sЭКРО ТЧ ЭСО ОЯШХЮЭТШЧ ШП ЩОrТРХКМТКХ LКФО OЧОРК, ЯКrТКЭТШЧs ТЧ ТЭs аКЭОr ХОЯОХ КЧН РХКМТШТsШsЭКЭТМ sСШrО ЮЩХТПЭ ШП ЭСО sСШrО ТЧ ЭСО LКЭО GХКМТКХ PОrТШНЖ. – GОШХШРв КЧН ЮsОПЮХ ЦТЧОrКХs ШП KКrОХТК. IssЮО 9. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 171–182. (IЧ RЮssТКЧ). EХТЧК, G. ., LЮФКsСШЯ, .D. & ВЮrФШЯsФКвК .K. 2000. . ., . ., . . ( . ДTСО LКЭО GХКМТКХ КЧН HШХШМОЧО ТЧ EКsЭОrЧ FОЧЧШsМКЧНТК (ЩКХОШЯОРОЭКЭТШЧ КЧН ЩКХОШРОШРrКЩСвЖ. – PОЭrШгКЯШНsФ. Karelian Research Center of Russian Academy of Sciences. 242 p. GrТРШrвОЯ, S.V. & GrТЭsОЯsФКвК, G.L. 1959. , . ., . . ДA МКЭКХШРЮО ШП KКrОХТК’s ХКФОsЖ. – .-L. 239 Щ. (IЧ RЮssТКЧ). LЮФКsСШЯ, .D. & IХвТЧ, V. . 1993. . ., . . . ДRОХТОП КЧН QЮКЭОrЧКrв НОЩШsТЭs ШП ЭСО ГКШЧОгСвО PОЧТЧsЮХКЖ. – KТгСsФв ЯОsЭЧТФ. ГКШЧОгСвО. 2:23–34. (IЧ RЮssТКЧ). LЮФКsСШЯ, .D. 2000. . . . ДGОШЦШrЩСШХШРТМКХ МСКrКМЭОrТsЭТМs ШП ЭОrrТЭШrвЖ. – IЧ: IЧЯОЧЭШrв КЧН sЭЮНв ШП ЛТШНТЯОrsТЭв ШЧ ЭСО ГКШЧОгСвО PОЧТЧsЮХК КЧН ТЧ NШrЭСОrЧ PrТХКНШгСвО. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 16–28. (IЧ RЮssТКЧ). SСОХОФСШЯК, .S. 2013. . . . ДGОШЦШrЩСШХШРТМКХ МШЧНТЭТШЧs КЧН QЮКЭОrЧКrв НОЩШsТЭsЖ. – IЧ: SОХФК ХКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ Characteristics, Land Use, Conservation (Gromtsev, A.N, ed.). Karelian Research Center of Russian Academy ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 29–36. (IЧ RЮssТКЧ). SККrЧТsЭШ, M., GröЧХЮЧН, T. & EФЦКЧ, I. 1995. LКЭО GХКМТКХ ШП LКФО OЧОРК - МШЧЭrТЛЮЭТШЧ ЭШ ЭСО СТsЭШrв ШП ЭСО ОКsЭОrЧ BКХЭТМ ЛКsТЧ. – QЮКЭОrЧКrв ТЧЭОrЧКЭТШЧКХ 27:111–120. Reports of the Finnish Environment Institute 40 | 2014 39 Fig. 1. Quartenary deposits of Zaonezhye Peninsula (Demidov 2005, with minor changes). 40 Reports of the Finnish Environment Institute 40 | 2014 1.3 Hydrological characteristics of Zaonezhye Peninsula Alexander V. Litvinenko* and Maria S. Bogdanova* *Institute of Water Problems in the North of the Karelian Research Center of Russian Academy of Sciences, 50 Alexandra Nevskogo St., 185003 Petrozavodsk, Karelia, Russia Corresponding author: Alexander V. Litvinenko E-mail: litvinenko@nwpi.krc.karelia.ru, aleks-litvinenko@mail.ru Introduction The irst fragmentary information about the rivers and lakes of Zaonezhye was obtained in the 1920s and 1940s. In the early 1960s, hydrographic studies of Zaonezhye were carried out by the water problem unit of the Karelian Branch of the USSR Academy of Sciences (now the Institute of Water Problems in the North, Karelian Research Center of Russian Academy of Sciences, KarRC, RAS), including integrated ield studies and the irst cartographic analysis of the area. The results of the studies were published in the “Problems in the hydrology, limnology and water management of Karelia” (1965) and the “Catalogue of Karelia’s Lakes” (Grigoryev & Gritsevskaya 1959) as well as a hand-written catalogue of Karelia’s Rivers. Today most of this data is outdated. Morphometric information about the Zaonechye water bodies has subsequently been presented in the “Catalogue of Karelia’s Lakes and Rivers” (Filatov & Litvinenko 2001). Hydrochemical studies and bottom sediment analyses were carried out as a part of monitoring Zaonezhye lakes and rivers in 1991 and between 1999 and 2001. Nevertheless, there is little information available about water bodies in the region. Due to the lack of hydrometeorological stations on Zaonezhye Peninsula, there are no reliable data on the hydrological regimes of the rivers and lakes. Results Geological structures and the relief of the peninsula deine the distinctive hydrographic network of Zaonezhye. Alternating long, narrow ridges and long, narrow depressions characterize the topography. Nowadays Lakes and Lake Onega bays (Unitsa, Svyatukha, Lizhma, Velikaya and Keften bays) occupy these depressions (Litvinenko 2000). Practically all the basins are elongated from northwest to southeast. Zaonezhye covers an area of 1900 km2. According to inventories conducted in 1950s (Grigoryev & Gritsevskaya 1959), there are 251 lakes in Zaonezhye, covering a total area of 212 km2 (Freindling & Polyakov 1965). The ratio of total lake surface to Reports of the Finnish Environment Institute 40 | 2014 41 drainage area in Zaonezhye is about 12 %. However, recent inventories have shown even greater values. The water bodies of Zaonezhye differ considerably in their morphometric and hydrological indices. Most of them are formed by tectonic subsidence, glacial tectonics or other glacial processes (Freindling & Polyakov 1965). Water area of the water bodies varies from less than 0.01 to 30 km2. Commonly the basins are highly elongated, sometimes dozens of kilometers long and no more than several hundred metres wide. The index of elongation (ratio of length of the lake to width of the lake) can be up to 43.5 (Lake Kosmozero). Extremely elongated lakes are relatively uncommon, occurring only in northern Scotland, northwestern England (Camberland Plateau) and northwestern Central Siberia (Putoran Plateau) (Semyonov 1993). The deepest lakes in the study area are Lakes Ladmozero (52 m) and Putkozero (42 m), which form cryptodepressions, i.e. their maximum depth is below sea level (Semyonov 1993). Because the lake basins in Zaonezhye are typically small, also their watershed values (ratio of basin area to lake area) are low. A speciic watershed value describes the volume of solid, liquid and ionic runoff supplied into the water body as well as the amount of heat supplied by tributaries. Therefore it relects the effects of the watershed on all processes in the water body (Litvinenko 2000). This is a small effect, also indicated by the low water exchange index (ratio of volume of long-term average lake runoff to lake volume), which varies from one year to 10 years (Freindling & Polyakov 1965). Despite the predominantly tectonic origins of the lake basins and the complex structures of the lake bottoms, littoral zones, mainly occupied by solid sand and gravel sediments with clay lenses, are relatively well developed. Ore deposits mixed with mud are conined to deep layers (Vlasova 1965, Belkina 2005). The thermal conditions of water bodies are different. Shallow lakes are warmer during the summer months (up to 25° C) when temperatures in their bottom layers may be only 2–3°Ccolder than the surface layer, whereas deep lakes remain thermally stratiied during the summer months: their surface layer may warm up to 26° C while the bottom layer has temperatures of 8–10° C (Semyonov 1993). Apart from southeastern Zaonezhye, which is dominated by small streams, the hydrographic network is relatively uniform over the entire area. There are only few small rivers on the peninsula. According to inventories in the mid-20th century, there were 56 rivers in Zaonezhye (each over 2 km long) with a combined length of 594 km. Their lake zones were 113 km long. Small rivers and creeks (which are less than 5 km long) make up only 11% of the length and 37% of the number of the rivers. Longitudinally, most streams have a terraced proile, which is most pronounced in the rivers Kuloma, Muna, Putka and Pigmozerka (Nature park…1992). The terraces are formed of rapids, or groups of rapids, separated by deeper slow portions of the rivers. The hydrographic network of the peninsula is characterized by lake and river systems whose linear ratio of lake area length to total length of the system can be as high as 70%. The distribution of river runoff throughout the year is affected considerably by the physical and geographical characteristics of Zaonezhye, especially the high ratio of lake surface area to drainage area of the basins as well as the linear ratio of lake surface area to drainage area of the river and lake systems. As the ratio of river area to drainage area decreases, the amount of spring loods declines and the amount of runoff during low-water periods increases. Spring looding in rivers begins in the second third of April. In rivers with a high ratio of river area to drainage area, spring loods last for 70–100 days, whereas in small rivers looding continues for 50–70 days. Usually there is one peak runoff during the loods. In rivers minimum runoff occurs twice a year: during the summer-autumn and winter low-water periods. On average, the long-term minimum runoff for a 30-day period is 42 Reports of the Finnish Environment Institute 40 | 2014 over 5 l/s*km2 during the summer-autumn low-water period and 2–3 l/s km2 during the winter low-water period. It increases to 4–5 l/s*km2 in rivers with a high ratio of river area to drainage area (Surface water resources… 1972 a). The distinctive hydrochemical characteristics of Zaonezhye include elevated mineralization (occasionally up to several hundred mg/l), alkalinity and nutrient supply. There are also low concentrations of predominantly autochthonous organic substances in lakes, but high concentrations in rivers (Maslova 1965, Kharkevich 1965, Startsev 1993, Present condition…1998; Lozovik et al. 2005). The hydrographic network of Zaonezhye, including the planned Zaonezhsky landscape reserve (zakaznik) is described in more detail in Litvinenko & Bogdanova 2013. In the present paper we discuss the southeastern and southern parts of the area that have not been described previoously. We have divided the study area into four hydrographic regions (Table 1). Lakes form the basis of the hydrographic network. As shown in the 1:50 000 map below, there are 101 water bodies, covering a total area of 1007 km2, located in their entirety in the study area (Fig.1). Table 1. Suggested hydrographic regions. Hydrographic region Total lake area, km2 Ratio of lake area to drainage area, % River network density, m/km2 Number in Fig. 1 Name I Zaonezhye Peninsula 813 7.2 237 II Lel Peninsula 119 0.3 361 III Lizh Peninsula 32 9.9 81 IV Syar Peninsula 43 9.0 356 Total 1007 6.6 252 Fig. 1. Water bodies in the study area (lakes are numbered in Table 2). Reports of the Finnish Environment Institute 40 | 2014 43 Table 2. Major lakes in the study area. Number in Fig. 1 Name of the lake Lake area, km2 Number in Fig. 1 Name of the lake Lake area, km2 I. Zaonezhye Peninsula 1 44 Varezh 0.086 45 No name 0.001 2 Munozero 0.040 46 Podmalinnoye 0.012 3 Korbozero 2.000 47 Podbereznoye 0.008 4 Kalozero 0.021 48 Beloye 0.052 5 Yandomozero 30.654 49 Chernoye 0.014 6 Korytovo 0.005 50 Bolshoye Khmelozero 3.971 7 Limozero 0.625 51 Gagarye 0.007 8 Glukhoye 0.007 52 Gankovskoye 0.526 9 Palevskoye 0.454 53 Kandozero 0.129 10 No mame 0.002 54 No name 0.003 11 No name 0.002 55 Maloye Pertozero 0.029 12 Keratskoye 1.969 56 Posulskoye 0.037 13 Kalye 0.033 57 No name 0.045 14 Gahkozero 0.125 58 Shumyacho 0.005 15 No name 0.004 59 Vilozero 0.714 16 No name 0.016 60 Bolshoye Pertozero 0.870 17 No name 0.003 61 Kovshozero 0.549 18 Palozero 0.261 62 Uzkoye 0.029 19 No name 0.003 63 Podcheremush0.029 noye 20 Matveyevo 0.007 64 Verkhneye Myagozero 0.032 21 No name 0.004 65 Krivoye 0.025 22 Degtozero 0.030 66 Mokhovoye 0.020 23 No name 0.002 67 Glubokoye 0.006 0.173 24 Driskozero 0.038 68 Nizhneye Myagozero 25 No name 0.019 69 Pelekozero 0.259 26 Koryukhozero 3 0.018 70 Gizhozero 0.453 27 Shibrozero 0.232 71 No name 0.002 28 No name 0.077 72 Nikonovo 0.079 29 Kalgozero 0.008 73 No name 0.035 30 Palozero 4 0.034 74 Nizhneye Torozero 0.044 31 Savozero 0.010 75 Sredneye Torozero 0.084 32 No name 0.006 76 No name 0.062 0.156 33 Koryukhozero 2 0.082 77 Verkhneye Torozero 34 Palozero 3 0.060 78 Gahkozero 5.311 35 Maloye Khmelozero 0.250 79 No name 0.008 Reports of the Finnish Environment Institute 40 | 2014 36 Yasakovo 0.040 80 No name 0.007 37 Palozero 2 0.010 81 Chuzhmozero 6.204 38 Munozero 0.044 82 No name 0.006 39 Zimneye 0.052 83 Karasevo 0.016 40 Koryukhozero 1 0.080 84 No name 0.009 41 No name 0.007 85 No name 0.007 42 Palozero 1 0.264 86 No name 0.021 43 Kimozero 0.736 87 No name 0.014 44 No name 0.003 88 Khudoye 0.019 89 Zdvizhenskoye 0.079 II. Lel Peninsula 90 Vozhmozero 0.009 94 Rugozero 0.223 91 No name 0.004 95 Pizhei 0.054 92 Bezdonnoye 0.105 96 No name 0.003 93 No name 0.006 97 No name 0.009 III. Lizh Peninsula 98 Pivgozero 3.163 IV. Syar Peninsula 99 Syargozero 3.388 100 Maloye Syargozero 0.121 101 Tulozero 0.341 In the study area, the ratio of lake surface area to drainage area is 6.6 %, which is much lower than the average for Karelia (12 %) or the estimate for the Onega and Ladoga lake area in Karelia (21 %) (Litvinenko et al. 1998). Most of the water bodies (93%) are small or very small (lambas), covering an area of less than 1 km2. Only seven water bodies are large. The largest lakes are Chuzhmozero (6.2 km2), Gahkozero (5.3 km2), Bolshoye Khmelozero (4.0 km2), Syargozero (2.4 km2), Pivgozero (3.2 km2) and Keratskoye (2.0 km2). Lake Yandomozero is the largest lake on Zaonezhye Peninsula with a surface area of 30.1 km2. It is 11.4 km long. Its maximum width is 4.3 km and its average width is 2.6 km, whereas its maximum depth is 6.0 m and its average depth is 4.3 m. Its shoreline is 47.5 km long. The water volume of the lake is 130 M m3. The Lake Yandomozero basin is of glacial origin. Its slopes are low and gradual and its bottom is smooth. The littoral zone of the lake consists of sand and gravel, whereas brown mud is common in the central part of the bottom. The study area is ajoined by three relatively large lakes: Putkozero (surface area 21.1 km2), Kosmozero (20.6 km2) and Padmozero (10.0 km2). The southern parts of Lake Putkozero border the study area in the northeast. Lake Putkozero has a surface area of 21.1 km2. It is 24.2 km long with a maximum width of 2.1 km and an average width of 0.9 km, as well as a maximum depth of 42.0 m and an average depth of 15.6 m. The water volume of Lake Putkozero is 330 M m3 and the shoreline extends 62.4 km. The lake basin is a deep elongated depression formed by tectonic subsidence. Generally its slopes are steep or moderately steep and up to 20 m high. However, in the western parts of the lake steep slopes can be up to 40–50 m high. The lakeshores are elevated and predominantly stony, or occasionally rocky. There are 16 islands on Lake Putkozero that cover an area of 0.38 km2. The bottom of the lake has a mildly rugged relief. Underwater the slope is mostly steep. In the littoral zone, rocky or rocky and sandy ground is common, while muddy ground with small quantities of clay, sand and ore are common in the deep. Reports of the Finnish Environment Institute 40 | 2014 45 The southern parts of Lake Kosmozero adjoin the western boundary of the study area. Lake Kosmozero has a surface area of 20.6 km2. It is 30.9 km long with a maximum width of 2.1 km and an average width of 0.7 km as well as a maximum depth of 25.0 m and an average depth of 7.8 m. Its shoreline is 76.6 km long. The lake basin is also been formed by tectonic subsidence. Its slopes are 50–80 m high, steep in the west but low (15–20 m) and gradual in the east and southeast. In the north, the slopes are low and paludiied. The shores are predominantly gently sloping and their height varies. There are 10 islands on the lake that cover a total area of 0.56 km2. The bottom of the lake is rugged. A deep groove extends across the entire lake. The bottom is muddy in the deep but argillaceous or rocky in the shallow zone. Bog ore is encountered occasionally. The study area is also adjoined by the eastern shore of Lake Padmozero. The lake has a surface area of 10.0 km2. It is 10.1 km long with a maximum width of 2.0 km and an average width of 1.0 km as well as a maximum depth of 14.9 and an average depth of 4.0 m. The water volume of the lake is 40.0 M m3 and its shoreline is 24.7 km long. Glacial tectonic processes have formed the Lake Padmozero basin. Its slopes are predominantly steep. Most of the slopes are about 10 m high, althought the highest slopes are up to 20 m high. Most of the lakeshores are low and rocky, although some shores are gently sloping. The bottom of Lake Padmozero is an elongated depression with a predominantly muddy ground, apart from the sandy and muddy littoral zone. The lake is deepest in its northern parts. (Surface water resources...1972 b). In the study area, the average density of the river network is 252 m/km2, varying from 81 to 361 m/km2 in parts of the river network (Table 1). It consists of small rivers and creeks as well as short tributaries between lakes. Watersheds of major water systems are shown in Fig. 2 and their basic characteristics are described in Table 3. The largest streams are the rivers Kalei (25.9 km), Padma (24.9 km), Tambitsa (22.1 km) and Putka (21.2 km). Practically all the river basins have been affected by human activities, long-term agricultural development (1960–1980), land reclamation and clear cutting in particular. As a result, there have been changes in their water regimes. The Putka, Padma and Kalei river basins are most heavily affected, while the Tambitsa and Tsarevka river basins are least affected by human activities. 46 Reports of the Finnish Environment Institute 40 | 2014 Fig. 2. Major streams in the study area (Major river watersheds are numbered in Table 3). Table 3. Major rivers in the study area. Name of the river Number of the drainage area in Fig. 2 Limozerka I Blizhnyaya I Name of the drainage area Height of mouth, m asl Stream gradient, m/km (‰) 5.3 119.6 37 15.6 21.2 54.6 33 1.02 16.2 River mouth Lake Limozero Polevskoye 4.3 Putka Mire Polevskoye 5.4 Putka Lake Bolshoye Khmelozero Lake Putkozero Putka Drainage area, km2 Ratio of lake surface area to drainage area, % Height of source, m asl Recognised source River length, km Spirovsky Creek I Putka I Putka Keratskoye Lake Onega No name I Putka Lake Kondozero Lake Putkozero 6.8 No name I Putka Lake Korjuhozero Putka 2.1 Chugmuksa II Chugmuksa Lake Chuzhmozero Lake Onega, Svyatukha Bay 39.7 2.3 56.9 33 10.47 32.3 No name III Lake Vilozero Lake Degtozero Lake Onega, Svyatukha Bay 29.9 16.1 148 33 7.13 9.8 231.7 Reports of the Finnish Environment Institute 40 | 2014 47 Pigmarya IV Padma 2.9 Padma IV Padma Padamokh mire Lake Onega 109.5 24.9 72.4 33 1.58 10.4 Tsarevka V Tsarevka mire Lake Onega, Karguba Bay 46.5 10.2 60 33 2.66 0.00 Sarandzha V Tsarevka Sarandzha mire Tsarevka Kalei VI Kalei Kalei Lake Onega, Tolvuya Bay 92.6 33 2.30 0.8 Kurgilov VII Tambitsa mire Tambitsa 103.2 22.1 72.7 33 1.80 0.00 2.5 85.5 25.9 6.4 Tambitsa VII Tambitsa mire Lake Onega, Rechnaya Bay Nulitsa VIII Nulitsa mire Lake Onega, Tipinitsy Bay 28.4 9.2 61.6 33 3.10 0.00 Korezhruchei IX Korezhruchei mire Lake Onega, Tipinitsy Bay 16.1 4.0 46 33 3.22 0.00 Jandoma X Jandoma Lake Jandomozero Lake Onega 119.9 4.0 42.4 33 2.32 27.3 No name XI Lake Palozero mire Lake Onega, Svyatukha Bay 9.1 6.5 150 30 18.37 4.1 No name XII Lake Kosmozero – Onega Lake Kosmozero Lake Onega, Svyatukha Bay 104.1 1.1 38.4 33 4.75 22.4 Karasozerka (Melnichnyj) XII Lake Kosmozero – Onega Lake Karasozero Lake Kosmozero 7.5 98 38.4 7.95 Sudma XIII Sudma mire Lake Onega, Velikaya Bay 18.8 8.6 45 33 1.40 0.00 Antonovshchina XIV Antonovshchina mire Lake Onega, Velikaya Bay 28.3 4.8 50 33 3.52 1.3 Lelrechka XV Lelrechka Lake Lelikozero Lake Onega, Velikaya Bay 27.5 11.4 86.4 33 4.70 6.0 Chernyj XVI Ust-Reka (Lake Matkozero) Lake Nizhneye Kontozero Ust-Reka (Lake Matkozero) Ust-Reka (Lake Matkozero) XVI Ust-Reka (Lake Matkozero) Lake Matkozero Lake Onega, Vegoruksa Bay 47.5 33 1.74 1.3 Pizhei XVII Pizhei Pizhei Lake Onega, Velikaya Bay No name XVII Vegoruksa Lake Rugozero Lake Onega, Vegoruksa Bay 17.4 8.6 55.5 33 2.62 1.4 No name XIX Lake Vekhkozero Lake Vekhkozero Lake Onega 6.4 5.9 68.7 33 6.07 0.9 XX Vozhmarikha mire Lake Onega, Vozhmarikha Bay 19.0 10.8 105.2 33 6.68 0.05 XXI Lake Pivgozero Lake Pivgozero Lake Onega, Bolshaya Lizhemskaya Bay 26.4 1.8 38.2 33 0.11 12.0 Vozhmariha No name 48 2.6 61.1 8.3 4.6 Reports of the Finnish Environment Institute 40 | 2014 No name XXII Lake Tulozero mire Lake Onega, Tulguba Bay 13.4 5.3 68 33 6.56 2.5 No name XXIII Lake Syargozero Lake Syargozero Lake Onega, Ilemguba Bay 12.1 0.02 34.3 33 68.99 28.1 No name XXIV Lake Maloye Syargozero Lake Maloe Syargozero Lake Onega, Zimnyayya Bay 5.6 2.0 40 33 3.43 2.1 Thus, the hydrographically distinctive Zaonezhye Peninsula is a particularly picturesque area even by Karelian standards. However, due to its high ratio of lake surface area to drainage area, its relatively low drainage density and its diversity of water bodies, the area is particularly sensitive to human impact. Therefore, a strictly protected area is urgently needed on Zaonezhye Peninsula. REFERENCES BОХФТЧК, N. . 2005. К . . К К ДBШЭЭШЦ sОНТЦОЧЭs ШП ЭСО ХКФОs ШЧ ЭСО ГКШЧОгСвО PОЧТЧsЮХК.Ж – IЧ: EЧЯТrШЧЦОЧЭКХ ЩrШЛХОЦs ТЧ ЭСО НОЯОХШЩЦОЧЭ ШП ЭСО SrОНЧвКвК PКНЦК НОЩШsТЭ. PОЭrШгКЯШНsФ. Щ. 65–71. (IЧ RЮssТКЧ). FТХКЭШЯ, N.N. &.LТЭЯТЧОЧФШ, A.V. (ОНs.), 2001. К . ., . . ( .) К К К ДA МКЭКХШРЮО ШП KКrОХТК’s ХКФОs КЧН rТЯОrs.Ж – PОЭrШгКЯШНsФ. 290 Щ. (IЧ RЮssТКЧ). FrОТЧНХТЧР, V. . & PШХвКФШЯ, ВЮ. K. 1965. , . ., . . ДMШrЩСШХШРв КЧН СвНrШХШРв ШП ЭСО ХКФОs.Ж – IЧ: PrШЛХОЦs ТЧ ЭСО СвНrШХШРв, ХТЦЧШХШРв КЧН аКЭОr ЦКЧКРОЦОЧЭ ШП KКrОХТК. IssЮО ББIII. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 61–78. (IЧ RЮssТКЧ). GrТРШrвОЯ, S.V. & GrТЭsОЯsФКвК, G.L. 1959. , . ., К . . К К К ДA МКЭКХШРЮО ШП KКrОХТК’s ХКФОsЖ. – ШsМШа–LОЧТЧРrКН. 239 Щ. (IЧ RЮssТКЧ). KСКrФОЯТМС, N.S. 1965. К . . К ДHвНrШМСОЦТsЭrв ШП ЭСО ХКФОs ТЧ ОКsЭОrЧ ГКШЧОгСвО.Ж – IЧ: PrШЛХОЦs ТЧ ЭСО СвНrШХШРв, ХТЦЧШХШРв КЧН аКЭОr ЦКЧКРОЦОЧЭ ШП KКrОХТК. IssЮО ББIII. PОЭrШгКЯШНsФ. Щ. 110–139. (IЧ RЮssТКЧ). LТЭЯТЧОЧФШ, . V. 2000. . . К ДHвНrШРrКЩСТМ МСКrКМЭОrТsЭТМs ШП ЭСО ЭОrrТЭШrв.Ж – IЧ: IЧЯОЧЭШrв КЧН sЭЮНв ШП ЛТШХШРТМКХ НТЯОrsТЭв ШЧ ЭСО ГКШЧОгСвО PОЧТЧsЮХК КЧН ТЧ NШrЭСОrЧ PrТХКНШгСвО. PОЭrШгКЯШНsФ. Щ. 41–44. (IЧ RЮssТКЧ). LТЭЯТЧОЧФШ, .V. & BШРНКЧШЯК, .S. 2013. . ., К К . . К К ДHвНrШРrКЩСТМ ЧОЭаШrФ.Ж – IЧ: SОХФК ХКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ CСКrКМЭОrТsЭТМs, LКЧН UsО, Conservation (Gromtsev, A.N. (ed.). Karelian Research Center of Russian Academy of Sciences. Petrozavodsk. Щ. 36–46. (IЧ RЮssТКЧ). LТЭЯТЧОЧФШ, .V., FТХКЭШЯ, N.N., LШгШЯТФ, P. . & KКrЩОМСФШ, V. . 1998. . ., К . ., . ., К . . К К : К К К К ДRОРТШЧКХ ОМШХШРв: ОМШХШРТМКХ КЧН ОМШЧШЦТМ ПЮЧНКЦОЧЭКХs ШП ЭСО rКЭТШЧКХ ЮsО ШП KКrОХТК’s аКЭОr rОsШЮrМОs.Ж − IЧгСОЧОrЧКвК ОФШХШРТК 6: 3–13. (IЧ RЮssТКЧ). LШгШЯТФ, P. ., BКsШЯ, . I. & ГШЛФШЯ, . B. 2005. . ., К . ., . . К К. К ДSЮrПКМО аКЭОrs ШП ЭСО ГКШЧОгСвО PОЧТЧsЮХК. CСОЦТМКХ МШЦЩШsТЭТШЧ ШП ЭСО аКЭОr.Ж – IЧ: EЧЯТrШЧЦОЧЭКХ ЩrШЛХОЦs ТЧ ЭСО НОЯОХШЩЦОЧЭ ШП ЭСО SrОНЧвКвК PКНЦК НОЩШsТЭ. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 20–34. (IЧ RЮssТКЧ). MКsХШЯК, N.P. 1965. К К . . К К К ДАКЭОr СвНrШМСОЦТsЭrв ШП аОsЭОrЧ ГКШЧОгСвО.Ж – IЧ: PrШЛХОЦs ТЧ ЭСО СвНrШХШРв, ХТЦЧШХШРв КЧН аКЭОr ЦКЧКРОЦОЧЭ ШП KКrОХТК. IssЮО ББIII. PОЭrШгКЯШНsФ. Щ. 141–154. (IЧ RЮssТКЧ). ДPrОsОЧЭ МШЧНТЭТШЧ ШП ЭСО аКЭОr ЛШНТОs ТЧ ЭСО RОЩЮЛХТМ ШП KКrОХТК.Ж 1998. К . – PОЭrШгКЯШНsФ. 188 Щ. (IЧ RЮssТКЧ). ДRОsШЮrМОs КЧН РОШМСОЦТsЭrв ШП KКrОХТК’s ЮЧНОrРrШЮЧН аКЭОr Ж. 1987. К . KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. – PОЭrШгКЯШНsФ. 151 Щ. (IЧ RЮssТКЧ). SОЦвШЧШЯ, V.N. 1993. . . К ДCХТЦКЭО КЧН sЮrПКМО аКЭОr СвНrШХШРв.Ж – KТгСsФв ЯОsЭЧТФ. ГКШЧОгСвО.2:33–59. (IЧ RЮssТКЧ). SЭКrЭsОЯ, N.S. 1993. К . . К К ДNКЭЮrКХ аКЭОrs ШП ЭСО ГКШЧОгСвО PОЧТЧsЮХК.Ж –KТгСsФв ЯОsЭЧТФ. ГКШЧОгСвО. 2:59–74. PОЭrШгКЯШНsФ. (IЧ RЮssТКЧ). ДSЮrПКМО аКЭОr rОsШЮrМОs ШП ЭСО USSRЖ 1972 К. . VШХ. 2. KКrОХТК КЧН ЧШrЭСаОsЭ RЮssТК. PКrЭ 1. – LОЧТЧРrКН. 528 Щ. (IЧ RЮssТКЧ). ДSЮrПКМО аКЭОr rОsШЮrМОs ШП ЭСО USSRЖ 1972 Л. . VШХ. 2. KКrОХТК КЧН ЧШrЭСаОsЭ RЮssТК. PКrЭ 3. – LОЧТЧРrКН. 960 Щ. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 49 VХКsШЯК, .S. 1965. К К . . К ДBШЭЭШЦ sОНТЦОЧЭs ТЧ ЭСО ХКФОs ШП ГКШЧОгСвО.Ж – IЧ: PrШЛХОЦs ТЧ ЭСО СвНrШХШРв, ХТЦЧШХШРв КЧН аКЭОr ЦКЧКРОЦОЧЭ ШП KКrОХТК. IssЮО ББIII. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 93–103. (IЧ RЮssТКЧ). ДГКШЧОгСвО NКЭЮrО PКrФЖ. 1992. К « К ». – PrОЩrТЧЭ ШП К ЩrОsОЧЭКЭТШЧ КЭ К PrОsТНТЮЦ sОssТШЧ ШП ЭСО KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 35 Щ. (IЧ RЮssТКЧ). Fig. 3. Lake Bolshoe Khmelozero (Photo Maria Bogdanova). Fig. 4. Lake Kovshozero (Photo Maria Bogdanova). 50 Reports of the Finnish Environment Institute 40 | 2014 Fig. 5. Lake Korytovo (Photo Maria Bogdanova). Fig. 6. Putka River (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 51 Fig. 7. Spirovsky Creek (Photo Maria Bogdanova). 52 Reports of the Finnish Environment Institute 40 | 2014 1.4 Soils and their characteristics on Zaonezhye Peninsula Olga N. Bakhmet* and Natalya G. Fedorets* *Forest Research Institute of the Karelian Research Center of Russian Academy of Sciences 11 Pushkinskaya St., 185610 Petrozavodsk, Karelia, Russia E-mail: obahmet@krc.karelia.ru Introduction The soil cover of Zaonezhye Peninsula is very distinctive. It differs considerably from other parts of Karelia due to the unique nature of the region. Soil patterns are mainly determined by a variety of landforms, including high, narrow ridges that alternate with narrow depressions. The macrorelief is also responsible for the climatic conditions in the area: Zaonezhye is protected against northerly winds, which makes its climate milder than in adjacent areas. The unconsolidated Quaternary sediment cover, produced by glacial abrasion, is either thin or completely absent. Soil-forming rocks are represented mainly by basic bedrocks, such as gabbro-diabase and amphibole, overlain by Leptosols and Cambisols (World reference base.. 2006). Due to widespread shungite schist and schist-enriched moraine, the soils are regionally and globally unique. Soil types and their characteristics The irst deinition of soils on shungite-bearing, soil-forming rocks was proposed by the academic F.Yu. Levinson-Lessing (Levinson-Lessing 1889) who named them “Olonets black soil”. Their place in the Russian soil classiication (1997, 2004) as well as in international soil classiications remains a subject of debate. Some researchers consider them as soils with well-developed sod-forming processes, which is inaccurate for several reasons. First, sodden soils develop under meadow plant communities, whereas virgin soils on shungite-bearing soil-forming rocks are formed under forest vegetation with decomposed mull litter. Secondly, in sodden soils humus typically accumulates in the sod horizon and its content in the underlying horizons decreases abruptly. However, in soils formed on shungite-bearing rocks, humus can be traced to a great depth in the proile and occasionally its concentration at the boundary with parent rock can be up to 2%. Thirdly, in the taiga zone, sodden soils are formed in an acid environment, whereas soils resting on shungite-bearing rocks are developed in neutral or subacid environments. Some researchers classify soils formed on shungite Reports of the Finnish Environment Institute 40 | 2014 53 rocks as lithogenic. However, this is also inaccurate since biological processes in these soils are vigorous. Thus, their place in soil classiication remains uncertain. Shungite-bearing rocks include shungite and shungite schist deposits as well as glacial and aqueo-glacial deposits. These deposits have different mechanical compositions but all contain a high percentage of black coaly shale, which gives them their black colour. As a soil-forming rock, shungite differs markedly from other parent rocks in its high carbon and hygroscopic moisture content. It also has a high absorptive capacity due to the presence of ine-grained carbon. The carbon content of shungite rocks varies between 5% and 95%; the higher the carbon content, the more intensely the rocks are eroded and weathered and the higher the mineral nutrient content of the soil. The mechanical compositions of soil-forming rocks are highly diverse, including gravelly sand, loamy sand, loam and ine clay. The silica content (of particles over 1 mm in diameter) can be over 80%. Genuine shungitic soils are common in areas covered by shungite eluvium-deluvium and shungitic moraine. With increasing distance from shungite deposits, the shungite content of moraine decreases and the moraine acquires a composition in which basic and shungite rocks are mixed with silicate rocks in equal proportions. Shungitic soils are common in such areas. These soils are darker and less acidic than Cambisols. They are also enriched with iron and mineral nutrients. Shungitic soils are usually combined with poorly developed Leptosols that are conined to slopes and podzolised Albic Cambisols, occupying low landforms. Soils on shungite-bearing rocks are formed under forest vegetation, dominated by small-leaved forests and a well-developed grass cover. Despite large quantities of plant residues accumulating at the surface, thick forest litter does not form due to the high biological activity of soil animals and microorganisms. Due to the characteristics of the soil-forming rocks as well as the accumulation of plant residues, there is a distinctive pattern of organic soil proile with a high percentage of humus and a homogenous composition of organic matter throughout the soil proile. Despite a high percentage of crushed stone and high water permeability of soils on shungite rocks, humic acids are ixed in the soil proile. This is due to the distinctive chemical composition of the soils, containing low silica and high iron and calcium oxide concentrations. These form strong polymeric complexes with humic acids. The low mobility of organic-mineral complexes in soils formed on shungite-bearing rocks has led to the formation of a texturally undifferentiated proile where organic matter and mineral mass are transformed in situ without the migration of substances beyond the soil boundary. Thus, the main processes that form the above soils are humus formation under neutral or slightly acid environmental conditions and the in situ metamorphism of mineral mass with the release of iron, calcium and other oxides. These soil-forming processes are not characteristic of Karelian soils but their occurrence in Zaonezhye is due to unique natural conditions. Primitive soils, combined with Leptosols, are common where crystalline rocks are either exposed or occur near the earth’s surface. Primitive soils are subdivided into crustal, organic (sodden, humus, peaty) or detrital soils depending on the degree of soil-forming process. In primitive soils, the layer of unconsolidated material is no more than 10 cm thick and consists of crystalline rock eluvium. Diabase eluvium, which is common in Zaonezhye, contains a large amount of iron (up to 20%) and calcium. Because the unconsolidated sedimentary cover is thin, these soils are poorly fertile. Open pine forests with suppressed growth occupy these soils. In parts of their distribution, they also grow juniper brushwood (alvars). Leptosols are formed on lat ridge tops or terraced slopes that provide favourable conditions for the accumulation of crystalline rock eluvium and eluvium-deluvium. 54 Reports of the Finnish Environment Institute 40 | 2014 These soils often grow moderately dense pine stands with grass in the undergrowth. Also juniper brushwood is occasionally encountered. The soil proile consists of A0-AhBfm-BC-M horizons. The AhBfm horizon displays features characteristic of humus-illuvial and metamorphic horizons. It is hard to divide these soils into genetic horizons because they contain large amount of rocks and crushed stone (particle content varies between 50 and 90%). The entire proile of these soils is saturated with humus. Podzols are typical of Karelia but scarce in Zaonezhye, which is due to the polymictic composition of unconsolidated sediments that contain considerable quantities of boulders, crushed stone as well as coarse basic and intermediate rocks. Also the abundance of mixed and deciduous open woodland, with a well-developed grass cover, contributes to the accumulation of humus. The podzolic soils of Zaonezhye are characterized by the poor eluvial-illuvial distribution of silicon, the presence of aluminium and iron oxides along the proile as well as the accumulation of organic elements (phosphorus, calcium, manganese, potassium, magnesium and sulfur) in the forest litter. However, the mineralogical composition of soil-forming rocks has affected the chemical composition of the soils. As a result, almost all of the soils contain much less silica than average in Karelia. These soils are also enriched with iron and often calcium, which has decreased soil acidity. Therefore, podzolic soils with a humus-accumulating horizon (A1) and a low level of podzolization are more common in Zaonezhye than podzols. Histic Podzols are formed on poorly drained plains and in wide depressions, composed of silicate sand and loamy sand, where ground water is near. Normally there is peat-saturated forest litter for at least 10 cm or a 10–30 cm thick peaty horizon. These soils are highly acidic, particularly in the upper part of the proile, and they have a low base saturation. Therefore, the soils are poorly fertile. Peaty soils are formed in deep depressions and lows between ridges under moisture-loving vegetation. In these conditions there is excess moisture and, therefore, the mineralization of plant residues is delayed. Fibric Histosols occupy only a small area in Zaonezhye. They are more common in watershed areas composed of silicate moraine, aqueo-glacial sand and loamy sand. Terric Histosols occur in areas where basic crystalline rocks are widespread. There, they occupy mires in old lake basins without outlow, ravines and at the foot of the slopes. Conclusions Zaonezhye consists of diverse areas. The soil contours are clearly aligned from southeast to northwest throughout the area. The distinctive feature of soil cover in Zaonezhye is its unique dark soils formed on carbonaceous rocks (shungite) or glacial deposits that are not encountered in other parts of the world. Although soils formed on shungite-bearing rocks have attracted the attention of many researchers who have described physical, chemical and biological soil properties in their publications, many issues remain poorly understood. Also, their place in soil classiication is unclear. Considering that shungite-bearing rocks are highly diverse in their chemical composition and abundance in Quaternary deposits, the genesis of these soils is still largely unknown. LITERATURE LОЯТЧsШЧ-LОssТЧР, F.ВЮ. 1889. . . sШТХЖ. − IЧ: OХШЧОЭsФТвО GЮЛОrЧsФвО VОНШЦШsЭТ 33:357–358. PОЭrШгКЯШНsФ. АШrХН rОПОrОЧМО ЛКsО ПШr sШТХ rОsШЮrМОs. 2006. ДOЧ ЭСО OХШЧОЭs ЛХКМФ Reports of the Finnish Environment Institute 40 | 2014 55 Mesic grassland in Zaonezhye Peninsula: Gymnadenia conopsea among Melampyrum nemorosum (Photo Tapio Lindholm). 56 Reports of the Finnish Environment Institute 40 | 2014 1.5 Paleogeography of Zaonezhye Peninsula Lyudmila Filimonova* and Nadezhda Lavrova** *Institute of Biology of Karelian Research Center of Russian Academy of Sciences, Petrozavodsk. 11 Pushkinskaya St, 185910 Petrozavodsk, Karelia, Russia Corresponding author Lyudmila Filimonova E-mail: ilimonovaluda@mail.ru Tel: +79535444890 ** Institute of Geology of Karelian Research Center of Russian Academy of Sciences, 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia E-mail: lavrova@krc.karelia.ru Tel.: +79214545451 Introduction Zaonezhye Peninsula juts out into Lake Onega, occupying central parts of its northern coast. It is a unique area of diverse Quaternary sediments. Diverse in composition and distribution of the complexes of Quaternary deposits are a result of the complex structure of the crystalline basement, the composition of bedrocks as well as the Late Pleistocene and Holocene evolution. The distribution of Quaternary sediments forms the basis of modern landscapes and biodiversity on the peninsula. Major relief-forming factors include glacial activity and denudation of surface horizons in Precambrian crystalline rocks. A combination of these factors has resulted in two genetically different landforms: 1) forms composed of crystalline rocks and 2) forms consisting of Quaternary rocks of different genesis (e.g. glacial and glacioluvial accumulative relief). The topography of Zaonezhye Peninsula can be divided into two parts: eastern and western. The eastern part is a moraine plain with gently sloping hills. It is a relatively lat area 30–60 m above lake level with paludiied depressions separated by gently sloping ridges. The western part of Zaonezhye Peninsula displays a typical selkä relief with a system of NW-trending ridges at an altitude of up to 120 m above lake level. Ridges have steep, stepped slopes and steep scarps. Narrow lake basins and the Lake Onega bays occupy depressions between the ridges. Elevated sites are either covered with thin moraine, or completely devoid of Quaternary sediments. All glacial and aqueoglacial deposits on Zaonezhye Peninsula relect the composition of the bedrock, eroded by glaciers (Lukashov & Ilyin 1993). Local moraines are widespread on shungite schis and rich in carbon, potassium, nitrogen and trace elements such as Cu, V, Ni, Zn and B. These elements are easily assimilated by plants, thus providing substrate for shungitic “black earth (chernozem)”, one of the best soil types for agriculture in Karelia Reports of the Finnish Environment Institute 40 | 2014 57 (Demidov 1993). The topographic characteristics and the composition of Quaternary deposits determine the plant biodiversity of Zaonezhye Peninsula. Vegetation dynamics have been reconstructed from the Allerød period (~11800 BP) to the present based on palynological, macrofossil and radiocarbon data for the lacustrine deposits of the Lake Putkozero cross-section from central Zaonezhye Peninsula (Lavrova 1999, Demidov & Lavrova 2000) as well as from lake-mire deposits of the Zamoshye and Boyarshchina cross-sections from eastern parts of the peninsula (Elina & Filimonova 1999, Elina et al. 1999, 2000, Elina et al. 2010; Fig. 1). Also, data from coeval deposits in central parts of Lake Onega as well as present-day ponds and mires in its basin have been analysed (Elina 1981, Filimonova 1995, 2010, Elina Filimonova 1996, Lavrova 2004, 2005). Vegetation dynamics are shown against variations in geomorphology (Lukashov & Ilyin 1993, Demidov & Lavrova 2000), climate (Klimanov & Elina 1984, Filimonova & Klimanov 2005) as well as the transgressions and regressions of Lake Onega (Devyatova 1986, Demidov 2005, 2006). In addition, surface pollen and spore spectra from the study area and other regions as well as correction coeficients for tree pollen have been examined (Elina & Filimonova 1999, Filimonova 2007 et al.). Ecological and geographic analyses of identiied taxa (after Grichuk et al. 1969) and estimations of pollen concentration in the deposits (after Stokmarr 1972) have been performed to reveal redeposited and remote pollen, which is essential for the study of Late Glacial vegetation. 58 Reports of the Finnish Environment Institute 40 | 2014 Fig. 1. Pollen diagram for the lake-mire deposits of the Zamoshye cross-section. (КЧКХвsОН Лв E. DОЯвКЭШЯК КЧН L. FТХТЦШЧШЯК) ДТЧ: EХТЧК КЧН FТХТЦШЧШЯК 1999Ж LОПЭ – sЭrКЭТРrКЩСТМ МШХЮЦЧ: 1–8 = ПОЧ ЩОКЭ: 1 – ЛТrМС, 2 – аШШНв, 3 – аШШНв-rООН, 4 – аШШНв-РrКss, 5 – rООН, 6 – РrКss, 7 – sОНРО-Sphagnum, 8 – Sphagnum (Sphagnum teres), 9 – ЭrКЧsТЭТШЧКХ Sphagnum (S. centrale); 10 – sКЩrШЩОХ-ХТФО ЩОКЭ; 11 – sКЩrШЩОХ; 12–14 – МХКвs: 12 – ЦКssТЯО, 13 – iЧО sКЧН ХОЧsОs, 14 – ЯКrЯОН. IЧ ЭСО НТКРrКЦ, iХХОН ЩКЭЭОrЧs sСШа ЭСО ЩШХХОЧ КЧН sЩШrО МШЧЭОЧЭ (%) ШП ЭСО ЭКбК ТЧНТМКЭОН; ЮЧiХХОН ЩКЭЭОrЧs sСШа ЭСО МШЧЭОЧЭ (%) ЦКРЧТiОН Лв 10; МШЧМОЧЭrКЭТШЧs ШП ХОss ЭСКЧ 1% КrО sСШаЧ аТЭС НШЭs Reports of the Finnish Environment Institute 40 | 2014 59 Geological Periods Late Glacial period (AL, DR3: 11 800–10 300 BP). Approximately 12 000 years ago, the territory of present-day Lake Onega and its surroundings were occupied by the last glacial ice sheet. During the retreat of the Valdai glaciation, a large periglacial meltwater body formed in the Lake Onega basin and on the adjacent lowlands. Its area and water level varied constantly depending on the position of the ice margin, the glacial isostatic adjustment of the earth’s crust and the erosional activity around the lake’s margins. After reaching the southern shores of Zaonezhye Peninsula, the glacier retreated relatively rapidly. Large, deep periglacial water bodies such as Lake Onega (which was over 100 m deep), Lake Ladoga and the White Sea contributed to the rapid retreat of the glacier. The periglacial Lake Onega basin, over 100 m deep, was dominated by a type of deglaciation which caused the ascent and destruction of the ice lobe periphery. In this case, the ice margin retreated at a speed of no less than 1–1.5 km/year, while upon deglaciation of frontal type it retreated at a speed of no more than 200–250 m/year. However, on reaching the south shore of the Zaonezhye Peninsula, the glacier retreated fairly rapidly Active glacier tongues, moving across deep bays and the rugged relief of the peninsula, contributed to the rapid disintegration of the ice lobes. The deglaciation of the Lake Onega basin began around 12 400 BP. By about 11 600 BP the ice had receded completely from the northern parts of Zaonezhye Peninsula (Demidov 2005, 2006, Filatov 2010) (Fig. 2). Fig. 2. Deglaciation of Zaonezhye Peninsula [After Demidov 2005, Filatov 2010]. 1 – Active ice sheet 2 – Passive ice sheet 3 – Cracks and tunnels in glacier 4 – Old water bodies and icebergs 5 – Large dead ice massifs 6 – Runoff directions 7 – Modern hydrographic network 8 – Absolute altitudes of modern surfaces 9 – Large old deltas 60 Reports of the Finnish Environment Institute 40 | 2014 During deglaciation, the water level of the periglacial Lake Onega changed constantly. The periglacial lake started to developed in the lower River Vytegra, on the southern shores of present-day Lake Onega. It is likely to have formed a part of the Upper Volga lake system where the water level was 120–130 m (Kvasov 1976). As a result of the glacial runoff, cutting through the river valley of Oshta, Tuksha and Oyat into the Baltic Sea about 12 500–12 400 BP, the lake’s water level dropped to 106 m (Demidov 2006). About 12 300 BP the ice margin retreated from the Svir river valley, and the lake was provided with a new, lower, threshold into the Baltic Sea (Saarnisto & Saarinen 2001). Consequently the water level in its southern parts dropped to 75–85 m (Demidov 2006). As a result of glacier retreat, deglaciation of new areas and glacial meltwaters, the periglacial Lake Onega reached its maximum size by the end of the Allerød (about 11 400 BP) when its water level rose to 115–130 m in the northern part. About 11 300 BP the water level dropped by 20–25 m down to 95–100 m due to isostatic uplift of the earth’s crust and the opening of a new threshold into the White Sea. Also another threshold was opened into Lake Ladoga in the northern parts of the Onega-Ladoga watershed and River Vidlitsa before the water level stabilized for a long time. The next large-scale regression of Lake Onega took place at the end of the Late Pleistocene about 10 300 BP due to the renewed runoff into Lake Ladoga though River Svir. At the same time Lake Onega lost its connection with the ice margin, which had retreated to Western Karelia. As a result, its level dropped by about 20 m and large areas were drained (Demidov 2005, 2006). Varved clay accumulated in the periglacial Lake Onega until 10 700 BP. After the ice margin retreated beyond the lake basin, mass deposition of homogeneous clay and silt in Lake Onega began. As deglaciation proceeded, water-and ice-free areas were colonized by vegetation whose distribution and evolution were determined by climatic, geological and geomorphological factors. At the inal stages of the Valdai glaciation, climatic changes were considerable. Quantitive climatic indices have been estimated for the Late Dryas: mean July temperatures were 3–6° lower, mean January temperatures 8–14° lower, annual temperatures 5–9° lower and precipitation 175–250 mm/year lower than at present (Filimonova & Klimanov 2005; Fig. 3). During the earlier Allerød interstadial warm period, negative temperature and precipitation deviations would have been more substantial on Zaonezhye Peninsula without the huge periglacial water body that made the climate slightly less continental. Reports of the Finnish Environment Institute 40 | 2014 61 Fig. 3. Dynamics of the climate, of Lake Onega level and vegetation in the Late Glacial and Holocene periods. Palaeoclimatic characteristics are shown as deviations from present values: toVI = 16o, toI = - 11o, toyear = 2o, total annual precipitation = 550 m. Acronyms: T – tundra, FT – forest-tundra, NT – northern taiga, MT – middle taiga, ST – southern taiga, Qm – broad-leaved species and hazel 62 Reports of the Finnish Environment Institute 40 | 2014 The evolution of the vegetation in Zaonezhye began after the ice receded and plants started to invade suitable areas, free from the melting ice. First almost the entire Zaonezhye was covered by the periglacial Lake Onega, leaving only some islands, elongated in a near-N-S direction, above the water level (Fig. 4). Plant growth was boosted by the presence of small quantities of mineral nutrients in the substrate, supplied by glacial meltwaters. Lower plants, dominated by algae and lichens, were most probably the irst to colonize the study area. These were followed by higher plants (Botrychium boreale, Dryas octopetala, Eurotia ceratoides, Lycopodium alpinum, Thalictrum alpinum, Saxifraga oppositifolia, Cryptogramma crispa, Ephedra and Saxifraga species) growing on crushed stones and rocky ground as well as on substrates with an unstructured, disturbed soil cover (Artemisia species,Chenopodium album, Ch. polyspermum, Ch. rubrum, Kochia lanilora and K. scoparia). These species are not sensitive to environmental change. However, they are resistant to temperature variations and water availability. These species grew on the soil-free islands that later turned into mainland of Zaonezhye Peninsula. First, seeds brought by various agents such as wind and water evolved into seedlings that provided the area with more seeds and formed a pioneer community. Later the pioneer species were joined by new species. As the ice retreated, water level in the periglacial lake dropped. While soils began to form on the islands and in adjacent areas, also the plant cover became more complex. It consisted of forest, tundra and steppe communities, comprised of species conined to different environments. Due to the proximity of the retreating ice cover, the weather was dry and the ground was saturated, which created favourable conditions for the growth of xerophytes, mesoxerophytes, mesophytes and hygrophytes. Late Glacial deposits on Zaonezhye Peninsula contain pollen of geographically diverse arctalpine (Dryas octopetala, Diphasiastrum alpinum, Saxifraga oppositifolia, Thalictrum alpinum, Oxyria digyna, etc.), hypoarctic (Betula czerepanovii, Botrychium boreale, Huperzia appressa, Lycopodium pungens, Rubus chamaemorus, Selaginella selaginoides, etc.), boreal (Alnus incana, Diphasiastrum complanatum, Lycopodium clavatum, etc.) and steppe species (Ephedra, Helianthemum, Eurotia ceratoides, Kochia scoparia, Kochia lanilora, etc.). During the Late Glacial period the plant cover was open, as shown by low pollen concentrations and the occurrence of heliophyte pollen (Hippophae rhamnoides, Helianthemum and Ephedra) in the deposits. Pioneer plant groups and bare ground succeeded each other. One of the critical factors limiting the spread of vegetation was long-term permafrost, which prevented the downward growth of roots. Its existence in the study area is supported by the presence of halophytes (Salsola kali, Salicornia herbacea and Atriplex nudicaulis) that found favourable habitats in saline depressions. Chenopodium album, Ch. rubrum, Eurotia ceratoides and Ephedra are also resistant to moderate salinity. In the dry continental climatic conditions, salts accumulated in the surface soil layer, while permafrost prevented their transfer into the deeper horizons. Permafrost contributed to the saturation of soils, too, by preventing moisture from penetrating into deeper layers, which in turn led to soliluction. Cold winters with little snow and strong winds were typical of periglacial zones and resulted in soil erosion. Thus, soliluction and erosion created suitable habitats for plants growing in disturbed and unstructured soils (taxa are shown above). Relief and the composition of Quaternary sediments were essential for the formation and distribution of plant communities. The succession of plains, ridges and hills created diverse conditions for plant growth on clay, loam and inequigranular sand. Some of the hills were completely devoid of Quaternary cover. Elevated areas and slopes were composed of rock debris, occupied by xerophylous communities (i.e. species of the Chenopodiaceae family and the Artemisia Ephedra and Helianthemum genera, Dryas octopetala, Cryptogramma crispa, Huperzia appressa, etc.). Depressions with accumulated snow protected plants against cold winter winds and provided Reports of the Finnish Environment Institute 40 | 2014 63 favourable habitats for tundra-like dwarf birch-green moss communities, consisting of Selaginella selaginoides, Rubus chamaemorus and Salix, Pedicularis, Cyperaceae and Poaceae species, in addition to Betula nana and Bryales. One of the factors responsible for the distinctive pattern of the Late Glacial vegetation was the permanent exposure of the earth’s surface after the glacier retreat and the lowering of the periglacial lake level. As a result, paleocommunities of unstructured soils existed for a long time. The presence of algae of the genus Pediastrum (Pediastrum boryanym var. boryanum, P. integrum var. integrum, P. kawraiskyi, P. privum) indicates that the periglacial Lake Onega was cold, deep and oligotrophic. Such conditions halted the spread of aquatic and littoral aquatic plants. The growth of woody species in the late glacial period poses a complex and ambiguous question. On one hand the pollen content of the deposits from the late glacial period is high (Fig. 1). On the other, most pollen seems to have been transported by wind and redeposited, as indicated by the low pollen concentration of woody plants. At the same time, favourable habitats provided good conditions for some woody plants, e.g. Betula pubescens, B. czerepanovii, Alnaster fruticosus and Alnus incana. These species differ considerably in their adaptability to low temperatures, cold soils and permafrost. It is likely that there were favourable habitats for open communities of woody plants or individual trees at least at the end of the Allerød. Another signiicant cooling event triggered the advance of the glacier in the Late Dryas (Fig. 3). Due to cold winters and thin snow cover, soliluction, erosion and weathering of the unstable ground increased. As a result, areas covered by crushed stone, rocky ground and plant communities on disturbed soils (Artemisia, Chenopodiaceae species, etc.) expanded. While the contribution of woody communities in the plant cover decreased, the tundra dwarf birch-green moss communities were survived in favorable habitats (Fig. 3, Fig. 4). In general the loristic composition of the Late Glacial vegetation remained practically unchanged. 64 Reports of the Finnish Environment Institute 40 | 2014 Fig. 4. Palaeovegetation maps of Zaonezhye Peninsula (10 500, 8500, 7500, 5500, 3000 and 1000 BP) [After Elina et al. 2010]. 1, 2 – Periglacial palaeocommunities (pc): 1 – Artemisia-Chenopodiaceae, 2 – Artemisia-Chenopodiaceae with herbs; 3 – Tundra pc: Betula nana-Bryales pc; 4 – Forest tundra pc: open Betula woodland; 5–9 – Middle taiga pc: 5 – Betula-herbs, 6 – Betula-Alnus-herbs, 7 – Pinus-Betula with Alnus, 8 – Pinus-Ericales-Bryales-Lichenes, 9 – Picea-Ericales-Bryales; 10–12 – Southern taiga pc: 10 – Pinus-herbs and Pinus-herbs-Bryales, 11 – Alnus glutinosa-Picea-herbs, 12 – Picea-Ulmus-herbs; 13 – Past shoreline; 14 – Shoreline at present; 15 – Shore scarps Reports of the Finnish Environment Institute 40 | 2014 65 The Holocene (10 300 BP – Present) During the Holocene, the greater availability of heat and moisture triggered an irreversible change in plant cover dynamics. As a result, the treeless ecosystems of Late Dryas were succeeded by open birch woodland and, more recently, taiga forests. The Preboreal period (PB: 10 300–9 300 BP) began with a substantial warming of the climate to a temperature maximum ca. 10000 BP when July temperatures were 2°C lower, January temperatures 6°C lower and annual temperatures 4°C lower than at present. Also precipitation was lower by 150 mm/year. Then, in PB-2 (10 000–9 300 BP), the climate became more unstable and colder, especially in the winter months. The deviation of the above parameters was 4–4.5°, 6–9°, 5–7° and 150–200 mm/year, respectively (Filimonova & Klimanov 2005; Fig. 3). The water level of Lake Onega continued to decrease, while transgressions and regressions succeeded one another (Fig. 3). Cross-sections have been studied from the massive clay deposits of Zamoshye and Boyarshchina on Zaonezhye Peninsula (Elina, Filimonova et al. 1999, Elina et al. 1999, 2000, Elina et al. 2010). Consequently, varves of ine sand found in the clay clearly correlate with the regressions: irst varve at the DR3/PB contact, second varve in the middle of PB and third varve at the end of PB (Fig. 1, Fig. 3). As the water level of Lake Onega declined, islands jutted out of the water and merged to form larger islands. Water-free areas were colonized by Artemisia, Chenopodiaceae (including Chenopodium album, Ch. hybridum, Ch. foliosum, Ch. glaucum, Ch. polyspermum, Ch. rubrum, Eurotia ceratoides, Salicornia herbacea, Salsola kali) and other pioneer plants. It looks as if these plant groups followed the retreating lake water and remained widespread until the end of the Preboreal period. At the beginning of the period, a large part of the area was occupied by dwarf birch-green moss tundra with Sphagnum, dwarf birch and willow thickets, occurring along the creeks. Birch continued to spread, although its contribution in the plant cover decreased. The tundra communities conined to fragmented stones and rocks on the tops and slopes of ridges, hight above sea level, persisted longer than other communities. The considerable contribution of wormwood-goosefoot-motley grass (Artemisia-Chenopodiaceae-Varia) paleocommunities during the Preboreal period was due to the cold and dry climate (Fig. 3), the cooling effect of Lake Onega and the formation of new land areas after the lowering of the lake’s water level. In the parts of Karelia, farther from large water bodies these communities were more typical during DR3, whereas in the PB-period their contribution in the plant cover decreased (Elina 1981, Filimonova 1995, 2014, Lavrova 2005, 2006). In the early Preboreal period open birch woodland (Betula czerepanovii, B. pubescens) spread on plains, ridge tops and ridge slopes. The ground cover was composed of Betula nana, Salix, Ericales, Poaceae, Bryales and Lycopodiaceae, presumably with a small percentage of Pinus sylvestris (Fig. 3, Fig. 4). Moist habitats were dominated by tallgrass open birch forests with Alnus incana, while depressions with good water low and ground cover of clay and loam were colonized by birch-alder and alder grassfern communities with Filipendula ulmaria, Geum rivale and Angelica sylvestris. In the late PB-2 (approximately 9 700 BP onwards), birch forests (Betula pubescens) and open pine-birch forests, similar to northern taiga forests, became more abundant (Fig. 3). Alder grew in tall-grass birch forests and formed alder groves. During the Preboreal period the number of xerophytes, halophytes and species typical of unstructured and disturbed grounds decreased, together with arctic, arctalpine, hypoarctic and steppe lora. At the same time boreal species, especially mesophytes and hydrophytes became more abundant. Grasses were represented by Apiaceae, Asteraceae (Aster, Tanacetum type), Brassicaceae, Caryophyllaceae, Ephedra, Fabaceae, Galium, 66 Reports of the Finnish Environment Institute 40 | 2014 Lamiaceae (including Mentha), Myosotis, Polygonaceae (including Bistorta oficinalis, Rumex,), Ranunculaceae (including Thalictrum alpinum), Rosaceae (including Dryas octopetala, Filipendula ulmaria), Scrophulariaceae, Urtica, Cyperaceae, Poaceae and Polypodiaceae (including Polypodium vulgare). Lycopodiaceae included Diphasiastrum alpinum, D. complanatum, Huperzia apressa and Lycopodium pungens. The formation of shallow bays made possible the growth of wetland plants (Myriophyllum spicatum, Sparganium, Parnassia palustris, Phragmites australis, Typha angustifolia, T. latifolia, Cyperaceae, Isoëtes, Equisetum, Bryales and Sphagnum). During the Preboreal period, nature and climate were generally unfavourable for human livelihood, although temporary settlements may have been established on the shores of shallow bays during warmer periods. The Boreal Period (BO: 9300–8000 BP) is characterized by the some climate warming. It began with cold conditions but reached maximum temperatures around 8500 BP when air temperatures were either close to, or above present values in the Lake Onega basin (Elina et al. 1984, Devyatova 1986, Filimonova & Klimanov 2005). In BO-3 (8300–8000 BP) the climate cooled and around 8200 BP July temperatures decreased by 1.5°C, January temperatures by 3.5°C and annual temperatures by 2.5°C. The amount of precipitation were by 25 and 75 mm/year lower than at present, respectively (Fig. 3). Thus, the climate was drier during the Boreal period than at present. In the BO-period, the water level in Lake Onega varied as transgressions were succeeded by regressions (Fig. 3). During the last regression, the water level dropped to 43 m above sea level. As a result, island area increased signiicantly. The vegetation responded to the changes in nature and climate, changing from northern taiga in the irst third of the Boreal period to middle taiga thereafter. Pine, birch-pine-green moss and grass-motley grass forests became predominant in the central parts of the islands (Fig. 4). Birch and alder tall-grass forests with Poaceae, Polypodiaceae (including Dryopteris linnaeana, D. phegopteris and D thelypteris) and motley grasses, e.g. Apiaceae, Fabaceae, Liliaceae, Polygonaceae (including Bistorta oficinalis), Ranunculaceae (including Thalictrum), Rosaceae (including Filipendula ulmaria), Rumex, Urtica grew at lower altitudes in shallow, well-lowing topographic depressions The presence of Artemisia and Chenopodiaceae pollen in the deposits (Fig. 1) indicates that more extensive areas became water-free during the Boreal period. Furthermore, habitats responded to the new environmental conditions. Late Glacial deposits contain pollen of Hippophae rhamnoides and Ephedra as well as Dyphasiastrum alpinum spores. Also the abundance of the Lycopodiaceae spores (Dyphasiastrum complanatum, D. tristachium, D. alpinum, Huperzia selago, Lycopodium pungens, L. annotinum and L. clavatum) is characteristic of the Boreal period. Club mosses are characteristic of open woodlands and open, treeless areas, including exposed, rocky grounds. The increased abundance of pollen and spores of aquatic (Myriophyllum spicatum, Nymphaea, Potamogeton, Sparganium and Iso tes) and coastal-aquatic plants (Alisma, Parnassia palustris, Phragmites australis, Typha angustifolia, T. latifolia and Cyperaceae) indicate an abundance of shallow bays. During the Boreal period Lake Onega retreated, more areas became water-free and the climate became milder. As a result, conditions for human livelihood became more favorable. Around the lake, people picked mushrooms and berries as well as ished and hunted for elk, reindeer, bear, hare and other animals, including waterfowl (geese, ducks, etc.) The Atlantic period (AT: 8000–4700 BP) was a period of a climatic optimum as well as considerable changes in hydrology and vegetation. Air temperature were higher than at present throughout the entire period: 1–2.5°C warmer in July and 1–4°C warmer in Reports of the Finnish Environment Institute 40 | 2014 67 January. In general, mean annual precipitation was higher by 50–75 mm/year. But it decreased in the late AT-3 (especially around 5200 BP) when air temperatures were relatively high (Fig. 3). As the results, the climate became drier in this time. During AT-1 (8000–7000 BP), the natural complexes of the Lake Onega basin were affected by the warm, humid climate as well as the considerable (over 3 m) transgression of Lake Onega (Fig. 3). Also, the water levels in small and medium-sized water bodies rose, as well as the groundwater in mires (Filimonova, 2010 et al.). In the middle of AT-2 (7000–6000 BP), the climate became less humid and the crystalline Baltic Shield continued to ascend. As a consequence, the Lake Onega water level dropped by 5 m. Its subsequent variations were smaller, in accordance with humid and dry periods (Fig. 3). Peat accumulation began here about 6700–6600 BP, during the Mid-Atlantic regression of Lake Onega. The mire has never been looded by lake water since (Elina & Filimonova, 1999). As a result of regression that preceded the AT-period, the depression, occupied now by Zamoshye Mire, separated from Lake Onega, and a shallow, overgrowing water body was formed there. This is supported by the greater occurrence of the pollen and spores of aquatic and mire plants and the formation of 10 cm thick sapropel and sapropel-like peat layers in the central portion of the mire in the late AT-1. Peat accumulation began there about 6700–6600 BP, when the Mid-Atlantic regression of Lake Onega took place. A warmer and more humid climate supported the spread of broad-leaved species (Ulmus laevis, U. glabra, Quercus robur, Tilia cordata, Acer platanoides), Corylus avellana and Alnus glutinosa. These species became most abundant in Zaonezhye during AT-2, as shown by the radiocarbon date 6580±80 BP. During the AT-period, the vegetation acquired southern taiga features. At the beginning of the period, pine and birch-pine forests continued to dominate. However, also grass-green moss spruce forests were spreading (Fig. 3, Fig. 4). These communities became more prevalent since AT-2 (~7000 BP). Depressions with fertile soils, saturated by lowing water, grew birch-black alder and spruce-black alder forests with elm and hazelnut, as well as lush grasses (Angelica sylvestris, Fillipendula ulmaria, Bistorta oficinalis, Fabaceae, Geum rivale, Humulus lupulus, Liliaceae, Urtica, Polypodiaceae, etc.). Also Alnus incana, Sorbus aucuparia, Viburnum opulus, Frangula alnus, Lonicera, Ribes and Salix have been encountered in these forest communities. The birch took part in coniferous forests and formed post-pyrogenic birch forests as well as birch-grass-moss communities, growing on eutrophic mires. Fires affected pine forests especially in dry habitats, as indicated by the Zamoshye pollen diagram (Fig. 1): The percentage of Pinus sylvestris pollen decreased, whereas the percentage of Betula sect. Albae pollen increased. Also pollen of Chamaenerion angustifolium and coal particles is occasionally encountered. Shallow-water zones continued to overgrown by aquatic and mire plants (Hydrocharis Nuphar, Triglochin and Menyanthes trifoliata were added to the taxa identiied earlier). At irst shallow reed and reed-sedge mires were common close to the shoreline; later they were succeeded by grass-Sphagnum fens. Atlantic period was the most favorable time for people’s lives. This contributed to the presence of many kilometers of shoreline with high, dry ridges, as well as an abundance of plant resources, game animals, birds and ish. The Subboreal period (SB: 4900–2500 BP) began with an abrupt cooling event, with a drop in humidity to a minimum around 4500 BP. It determined the course of subsequent environmental change. According to climatic reconstructions from seven pollen diagrams for the Lake Onega basin, July temperatures were 0.5–1° lower, January temperatures 1–2° lower and precipitation 50 mm/year lower than at present (Elina et al., 1984, Filimonova & Klimanov 2005). Since SB-2 (4200 BP) temperatures 68 Reports of the Finnish Environment Institute 40 | 2014 began to rise again, within the same range as during SB-1. However, mean annual precipitation was smaller. Climate was the driest during SB-1 (4700–4200 BP) and after 3900 BP (Fig. 3). The regression of Lake Onega as well as smaller water bodies is consistent with the cooling and decreased precipitation during the early SB-period. At the same time, there was a drop in groundwater levels, including in the mires, where woody communities became common. During the middle-Subboreal transgression, moisture-loving plants reappeared, as indicated by the peat stratigraphy of Zamoshye Mire (Elina & Filimonova 1999, Elina et al. 1999). The overall reduction of water level in the Lake Onega has led to an increase in land area. A signiicant cooling and reducing the humidity of the climate caused the gradual replacement of southern taiga forests on middle-taiga forests. During the Subboreal period, spruce and pine-spruce green moss forests were common (Fig. 3, Fig.4). They occupied lacustrine glacial plains and selkä slopes Broadleaved species were present, although they were more common in moist birch-black alder and spruce-black alder forests. By the end of the period, their contribution to the forest composition had decreased. Corylus avellana, Populus tremula, Sambucus racemosa, Sorbus aucuparia, Viburnum opulus and Ribes occurred in the undergrowth. Pine forests with dwarf shrub, green moss and lichen grew on rocky ridges. Birch took part in coniferous forests, although it formed post-pyrogenic birch forests and played a leading role in the afforestation of mires. Distinguished in the grass cover are several loristic groups characteristic of forests and forest edges with moist and fertile soils (Urtica, Thalictrum and Polypodiaceae), moist communities growing at the periphery of mires (Filipendula ulmaria, Bistorta oficinalis and Geum rivale) and meadow-like moist (Parnassia palustris and Cyperaceae) and dry communities (Chamaenerion angustifolium, Galium, Potentilla, Ranuculaceae, Fabaceae and Liliaceae). Eutrophic grass mires, one of which is 2770±60 years old, succeed coastal aquatic and wetland plant thickets. Mires became common towards the end of the period. The development of meadows and meadow-like communities is indicated by the considerable amount of grass pollen and the pollen content in the pollen diagrams (see Fig. 1). Climate, the formation of new territories and the abundance of various food resources and forests with a variety of useful plants were favorable for living and the establishment of permanent settlements. During the Subatlantic period (SP: 2500 BP – Present) the shoreline of the Zaonezhye Peninsula acquired its modern shape and landscapes. These landscapes have been affected by both natural and anthropogenic factors. During the SA-period the climate became colder than in the two previous periods. In the beginning, July temperatures were 1°C lower, January temperatures 2°C lower and precipitation 50 mm/year lower than at present. Both the temperature and the precipitation luctuated simultaneously (Fig. 3). The most considerable warming event took place during the SA-2 (1800–800 BP) in the Viking epoch, especially around 1800 BP and during the Little Climatic Optimum in the Middle Ages (1100–1000 BP) when July temperatures were 1.5°C higher, January temperatures 2°C higher and precipitation 75 and 50 mm/year higher, respectively. The SA-3 (the past 800 years) began with a global cooling. In their coolest, around 700 BP, July temperatures were 1–1.5° lower, January temperatures 1–2°C lower than at present. Precipitation was as it is today or smaller by 50 mm/ year. Other cooling events occurred around 500 BP, 200 BP and a little more than 100 BP, while warming events took place around 600 BP, 300 BP and 170–150 BP. The lat- Reports of the Finnish Environment Institute 40 | 2014 69 est warming event began towards the middle of the 20th century (Klimanov & Elina, 1984, Filimonova & Klimanov 2005). A rise in atmospheric humidity caused increased of groundwater level, including in the mires. At that time the moisture-loving mire communities became more common, peat accumulation rate increased and the degree of peat decomposition decreased (Elina & Filimonova 1999, Kuznetsov et al. 1999). During the irst part of SA-period, middle taiga spruce forests dominated (Fig. 3), especially those were widespread on the gently sloping moraine plains of selkä Zaonezhye Peninsula (Fig. 4). Pine forests were more common in the western esker area. Black alder and black alder-spruce forests with a lush grass cover grew between selkäs and in topographic depressions with good stream moistening. Birch took part in the above forests. It also formed tall-grass and pyrogenic birch forests as well as played a part in the afforestation of mires. Broad-leaved species (Acer, Ulmus and Tilia) grew on more fertile soils. In the second part of SA-period, especially during the past 1000 years, the amount of coniferous forests has decreased and the amount of small-leaved forests has increased. Especially spruce forests have declined (Fig. 3). This has been largely due to agricultural development. Spruce forests growing on fertile soil were cut and burned for use as farmland. Pine has been used as building material and irewood as well as for charcoal. As a result of intensive human activities, most primeval forests have disappeared and been replaced by settlements, meadows, pastures, arable land and secondary forests. Abandoned agricultural land is now overgrown with birch, aspen and grey alder (Alnus incana). The effects of human activities are relected in the spore and pollen diagrams. There is a decrease in the proportion of pollen from coniferous plants, especially Picea, as well as an increase in the amount and diversity of grass pollen. Also coal particles are present. Pollen of species adapted to secondary habitats (Chenopodium album, Ch. rubrum, Ch. polyspermum, Chamaenerion angustifolium, Potentilla, Ranunculus, Artemisia and Poaceae) has become more common. Pollen of ruderal plants (Rumex, Urtica, Potentilla, Galium, Plantago, Apiaceae, Geraniaceae and Chenopodiaceae), segetal weeds (Asteraceae, Centaurea, Cichoriaceae, Fabaceae, Caryophyllaceae and Lamiaceae) and cereals (Cerealia) also occurs. These changes in the spore and pollen spectra suggest that agricultural activities on Zaonezhye Peninsula began about 1100-900 BP. This conclusion is also supported by the radiocarbon dates 1140±50 BP and 950±110 BP obtained from the Moshguba and Shlyamino Mire deposits (Lavrova et al., 2007). Obtained data are in good agreement with the date 1060±60 BP for the beginning of agriculture in the vicinities of Essoila village, Syamozero Lake, on the Onega-Ladoga isthmus (Ekman & Zhuravlev 1986). According to reconstructions from Alleröd to the present, the dominant vegetation on Zaonezhe Peninsula follows the sequence: periglacial steppe-like (Artemisia, Chenopodiaceae, Poaceae, etc.) and tundra (Betula nana, Salix, Ericales, Dryas, Saxifraga, Carex, Bryales) palaeocommunities (PC) [AL, DR3: 11800–10300 BP] → forest-tundra: open birch woodlands (with some pine and alder) combined with dwarf shrub moss tundra and Artemisia-Chenopodiaceae-Varia PC [ -1,2: 10300–9700 BP] → northern taiga: light birch and pine-birch forests [P -2: 9700–9300 BP] → light birch-pine and pine forests [ -1: 9300–8900 BP] → mid taiga: pine and birch-pine forests ДB -2,3: 8900–8000 BP] → southern taiga: pine, pine-birch and birch-black alder forests with broad-leaved species and hazel (Qm), spruce [ -1: 8000–7000 BP] → spruce, pinespruce, birch- and spruce-black alder forests with Qm [ -2,3: 7000–4700 BP] → spruce, pine-spruce, birch-black alder forests with Qm and spruce forests with black alder and elm [SB: 4700–2500 BP] → mid taiga (with elements of the south taiga): spruce, pine-spruce-pine and spruce-black alder forests with present of Qm [SA-1,2: 70 Reports of the Finnish Environment Institute 40 | 2014 2500–1300 BP] → pine, spruce-pine and spruce-black alder forests with present of elm and lime, as well as secondary forests dominated with birch and grey alder [SA-2,3: 1300 BP – 0 yrs]. The diversity natural patterns of Zaonezhye are a result of its geological evolution and climate history. Its carbonate and shungite rocks, diverse landforms and Quaternary deposits of various grain sizes have provided diverse habitats for species and communities in different light, moisture, heat and mineral conditions. These and other natural features of Zaonezhye contributed preserving individual species and communities (spruce and lime forests, black alder fens, and fens with black alder and spruce) that existed during the period of climatic optimum. Tilia cordata, Ulmus laevis and U. scabra are encountered on mainland Zaonezhye and on the islands of Zaonezhye. Nemoral, herbaceous plant species grow in areas with fertile soils (e.g. Kuznetsov 1993, Kravchenko et al. 1993). Relicts of the cold Late Glacial period include Helianthemum nummularium, which is found on Bolshoi Lelikovsky Island (Kuznetsov 1997). In Karelia, pollen of Helianthemum nummularium occurs in Late Glacial deposits of some sections (Demidov & Lavrova 2001, Lavrova 2011). Nowadays the northern limit of the species’ distribution extends from the Åland Islands to the southwestern coast of Finland. Only ive Helianthemum nummularium habitats are known to the north or east: two in Finland, two in Russian Karelia (northern shore of Janisjärvi Lake and Zaonezhye) and one in Cape Tury, Kola Peninsula (Vasari & Vasari 1999, Kravchenko 2007). REFERENCES DОЦТНШЯ, I.N. 1993. . . ДVКrЯОН МХКв sЭrЮМЭЮrО КЧН НОРХКМТКЭТШЧ ЩКЭЭОrЧ ШП CОЧЭrКХ KКrОХТКЖ. − IЧ: PrШЛХОЦs ТЧ ЭСО PrОМКЦЛrТКЧ РОШХШРв ШП KКrОХТК. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 127–151. (IЧ Russian). DОЦТНШЯ, I.N. 2005. . . ДDОРrКНКЭТШЧ ШП ЭСО ХКsЭ РХКМТКЭТШЧ ТЧ LКФО OЧОРК ЛКsТЧЖ. − IЧ: GОШХШРв КЧН МШЦЦОrМТКХ ЦТЧОrКХs ШП KКrОХТК. IssЮО 8. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 134–142. (IЧ RЮssТКЧ). 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Reports of the Finnish Environment Institute 40 | 2014 73 Black alder swamp in Klimenetsky Island (Photo Tapio Lindholm). 74 Reports of the Finnish Environment Institute 40 | 2014 1.6 Nature protected areas in Zaonezhye Denis Maksimov*, Philip Uchuvatkin*, Ivan Kiprukhin**, and Anna Volkova*** * Directorate for regional protected areas of the Republic of Karelia 66 Rigachin St., 185005, Petrozavodsk, Karelia, Russia E-mail: oopt@karelia.ru ** Ministry of Nature Management and Environment of the Republic of Karelia 2/24 Andropov St., 185035, Petrozavodsk, Karelia, Russia E-mail: ecopetr@karelia.ru ***Petrozavodsk State University 33 Lenin prospect, 185035, Petrozavodsk, Karelia, Russia Introduction At present there are three regional nature reserves and 19 regional nature monuments on Zaonezhye Peninsula with a total area of 2500 ha (Table 1). In addition, the federal Kizhi zoological reserve (zakaznik) covers 50 000 ha in the southeastern part of the peninsula. Within its boundaries lie the Kizhi open-air museum and its buffer zone as well as the regional nature monuments “Yuzhniy Oleniy Island”, “Wetland by the village of Boyarschina”, “Wetland by Petrikov’s Bay” and “Wetland Zamoshye”. Overview of protected areas in Karelia On the whole there are 137 regional protected areas in the Republic of Karelia (as of 1st November 2014). These protected areas cover 391 600 ha, or 2.17% of the republic, and include the Valaam nature park (24 700 ha) as well as 31 nature reserves (zakazniks) and 105 nature monuments. The nature reserves consist of 15 landscape reserves (242 800 ha), one marine reserve (72 900 ha), 11 botanical reserves (2 100 ha) and four hydrological reserves (6 700 ha), while the nature monuments comprise 64 protected mires (31 600 ha), nine hydrological monuments (over 6 000 ha), 10 geological monuments (2 400 ha), three landscape monuments (2 300 ha) and 19 botanical monuments (over 100 ha). Overall nature reserves (75% of which are landscape reserves) constitute 82.86% of the total area of regional protected areas in the Republic of Karelia, whereas nature monuments make up 10.83% and nature parks 6.31%. Buffer zones have been designated around the protected areas. By imposing restrictions to land use, these zones shield protected areas from negative human impact. In the Republic of Karelia, 33 regional protected areas (with a total area of 78 000 ha) are Reports of the Finnish Environment Institute 40 | 2014 75 accompanied by 5 600 ha of buffer zones on land. For 15 protected areas, the extent of the buffer zones has not been speciied. In the Republic of Karelia, regional protected areas are established in accordance with the Regional land-use plan of the Republic of Karelia, approved by the government of the republic (Scheme 2012, Regulation 2014). In justiication materials to this document, there are two lists of new protected areas to be established by 2030: A list of planned protected areas, for which the necessary documents have been prepared (Annex 1), and a list of perspective protected areas (Annex 2). The irst list consists of protected areas to be established in the irst stage. For these protected areas, the necessary ecological and economical impact assessments have been prepared and presented to the regional authorities. These assessments include detailed descriptions of ecological, social and economic impacts of the protected areas as well as their borders, areas and proposed protection regimes. At present there are eight planned protected areas with a combined area of 264 890 ha, or 1.5% of the total area of the Republic of Karelia. These include the nature reserves Chukozero, Gridino (in Loukhi municipality), Maslozero, Varozero, Yangozero, Yupauzhsuo and Zaonezhsky as well as the Vargachnoe-Korbozerskoe nature monument. Two regional protected areas were established in 2013: Gridino landscape reserve (8 400 ha; Kemi municipality) and Kumi-Porog nature monument (3 400 ha; Kalevala municipality). In addition, the Institute of Biology of the Karelian Research Centre of the Russian Academy of Sciences has conducted ield studies on the mire systems of Yupauzhsuo and Kepasuo (Kalevala municipality) and prepared the necessary documents for the establishment of the Yupauzhsuo nature reserve. The second list consists of perspective protected areas. These areas have high conservation value, for example habitats of regionally or nationally red-listed species. However, more detailed information is needed for the establishment of these protected areas. In the Regional land use plan there are altogether 49 perspective protected areas that cover a total area of 1 192 900 ha. With the aim of developing the network of protected areas in Karelia and the Barents Euro-Arctic Region, in 2012 the Karelian Research Centre of the Russian Academy of Sciences conducted ield studies and an ecological impact assessment of the landscapes, lora and fauna on Zaonezhye Peninsula, with funding from the Ministry of Natural Resources and Environment of the Republic of Karelia. Based on these studies as well as existing information, the Karelian Research Centre has prepared the ecological impact assessment of the Zaonezhskiy landscape reserve (zakaznik). Protected areas on Zaonezhye Peninsula and its adjacent islands The Klim-Gora nature monument is the largest existing regional protected area on the peninsula. It is one of the most picturesque parts of Zaonezhye Peninsula where Mount Klim rises 90 m above Lake Onega. The nature monument was established for the preservation of glacioluvial landforms in their natural state, as well as for tourism and recreation. Another geological monument worth mentioning is the Shunga outcrop, which is the only large outcrop of shungite rocks in the world. It is part of the Kizhi Skerries group of geological monuments, 12 km east of the Kizhi Islands, which also includes Yuzhniy Oleniy Island in northwestern Lake Onega. Hydrological nature monuments include two water seeps: Tri Ivana and Solyanaya Yama. The Tri Ivana water seep is irst mentioned in literature in 1861. It is located two kilometres north of the abandoned village of Karasozero, 22 km from the village of Velikaya Guba. The water seep resembles a funnel, 1-1.5 m in diameter and 0.5-0.7 m in depth, from where approximately one litre of water lows out every second. 76 Reports of the Finnish Environment Institute 40 | 2014 It is near a small chapel, fenced with a stone dyke, and it has been covered with a wooden construction. The Solyanaya Yama water seep is unique for Karelia. It is located in the backswamp depression of the river Sudma, two kilometres north of the village of Velikaya Guba. In the past, local people collected water from the seep to make salt. A wooden construction has been built inside the well. However, nowadays the wooden construction is dilapidated and the 6-m-deep well is half full of silt. The water’s salt concentration is 4 g/l at the surface and it increases deeper in the well. Due to the large quantities of hydrogen sulide (32 mg/l), sodium chloride water is used as medicinal mineral water. Nature reserves have been created to preserve unique plantations of broadleaf trees, including the state nature reserve “Highly productive stands of larch and common alder” as well as the nature monuments “Natural stands of small-leaved lime and Scotch elm (Ulmus glabra)”, “Natural stands of Scotch elm (Ulmus scabra)”, “Plantation of Siberian pine – 64” and “Plantation of Siberian pine – 65”. Scotch elm, small-leaved lime and Acer platanoides reach their northern limits in Zaonezhye. Protected areas on the peninsula also include the Anisimovschina botanical reserve, created in 1984. This reserve is a unique natural refugium for the curly (Karelian) birch, which is a calling card of both the peninsula and Karelia as a whole. Wetlands cover only 5% of the total area of forest land on Zaonezhye Peninsula (See Chapter 2.3). However, nearly half of the protected areas in Zaonezhye are wetlands. These nature monuments represent wetlands of different type and genesis. In addition, wetland ecosystems are home to berries as well as rare and red-listed plant species. Planned protected areas on Zaonezhye Peninsula Several regional protected areas are planned to be established on Zaonezhye Peninsula. In 2009 the Karelian Research Centre of the Russian Academy of Sciences carried out a scientiic feasibility study for the development of the protected area network in the Republic of Karelia (Feasibility study 2009). However, its irst priority was the establishment of another planned protected area, the Zaonezhskiy nature reserve, which covers nearly 110 000 ha of unique esker landscapes in the northern part of the peninsula. In 2011 the Karelian Research Centre proposed a preliminary area and borders for the Zaonezhskiy nature reserve, which were included in the inal version of the Land-use plan of the Republic of Karelia (Scheme 2012). The nature conservation NGO “SPOK” is proposing the largest protected area in Zaonezhye, the Zaonezhsky nature park. It covers the entire southeastern part of the Zaonezhye Peninsula as well as parts of the peninsulas Sjar and Lizh – altogether 115 000 ha. An alternative way to protect rare, red-listed and indicator species in the southeastern part of the peninsula is to establish six nature monuments, covering 14 500 ha (Fig. 1). These areas were identiied during a multidisciplinary expedition, arranged by the Barents Protected Area Network (BPAN) project (Lindholm et al. 2014) REFERENCES FОКsТЛТХТЭв sЭЮНв 2009. . . ДFОКsТЛТХТЭв sЭЮНв ШП ЭСО ЩrШЭОМЭОН КrОК ЧОЭаШrФ ТЧ ЭСО RОЩЮЛХТМ ШП KКrОХТК. KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 112Щ.Ж (ТЧ Russian). LТЧНСШХЦ, T., JКФШЯХОЯ, J. & KrКЯМСОЧФШ, A. (ОНs.) 2014. BТШРОШРrКЩСв, ХКЧНsМКЩОs, ОМШsвsЭОЦs КЧН sЩОМТОs ШП ГКШЧОгСвО PОЧТЧsЮХК, ТЧ LКФО OЧОРК, RЮssТКЧ KКrОХТК. RОЩШrЭs ШП ЭСО FТЧЧТsС EЧЯТrШЧЦОЧЭ IЧsЭТЭЮЭО 2014/40:1-360. Reports of the Finnish Environment Institute 40 | 2014 77 RОРЮХКЭТШЧ 2014. . 7 2014 № 88- . 6 2007 № 102- . . . ДRОРЮХКЭТШЧ ШП ЭСО GШЯОrЧЦОЧЭ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК 07.04.2014, №88-P. OЧ ЭСО МСКЧРОs ЭШ ЭСО RОРЮХКЭТШЧ ШП GШЯОrЧЦОЧЭ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК 06 .07.2007 № 102- . PОЭrШгКЯШНsФЖ. (IЧ RЮssТКЧ). СЭЭЩ://РШЯ.ФКrОХТК.rЮ/LОРТsХКЭТШЧ/ХКаЛКsО.СЭЦХ?ХТН=11393 SМСОЦО (2012). К , 06.07.2007 № 102- . . . ДSМСОЦО ШП SЩКЭТКХ ЩХКЧЧТЧР ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК. 06.07.2007 № 102- . PОЭrШгКЯШНsФЖ. (IЧ RЮssТКЧ). СЭЭЩ://ааа.РШЯ.ФКrОХТК.rЮ/PШаОr/CШЦЦТЭЭОО/BЮТХН/PХКЧ/ SPOK 2013. , « » NGO “SPOK”. ДDШМЮЦОЧЭКЭТШЧ ШП ЭСО МШЦЩХОб ОМШХШРТМКХ ТЧЯОЧЭШrв УЮsЭТПвТЧР ОsЭКЛХТsСЦОЧЭ ШП ЭСО ГКШЧОгСsФв SЭКЭО NКЭЮrО PКrФЖ. 2013. PОЭrШгКЯШНsФ.108 Щ. (IЧ Russian). Table 1. Regional protected areas on Zaonezhye Peninsula Category: NR – Nature reserve, NM - Nature monument 78 Date of № Name of protected area Category Proile Area, ha establishment 1 Highly productive larch and common alder stands NR Botanical 110.4 15/06/1976 2 3 4 5 Lake Kovshozero Yuzhniy Oleniy Island NR NR NM Shunga outcrop NM 60 5.4 75 10 20/07/1984 20/07/1984 29/07/1981 29/07/1981 6 Plantation of Siberian pine – 64 NM Botanical Botanical Geological Geological Botanical 2.4 29/07/1981 7 Plantation of Siberian pine – 65 NM Botanical 1.9 29/07/1981 8 Natural stands of smallleaved lime and Scotch elm (Ulmus scabra) NM Botanical 5 29/07/1981 9 Natural stands of Scotch elm (Ulmus scabra) NM Botanical 23 29/07/1981 10 Solyanaya Yama water seep NM Hydrological 11 Tri Ivana water seep NM Hydrological 125 21/10/1993 12 Wetland Konye №402 NM 86.2 24/05/1989 13 Wetland Razlomnoe NM Wetland Wetland 39 24/05/1989 14 15 Wetland Pigma №390 24/05/1989 24/05/1989 Wetland Kalegubskoe №3061 Wetland Wetland Wetland 525 204 16 NM NM NM 168 29/12/1997 17 Wetland by Lake Lelikozero №3063 NM Wetland 200 29/12/1997 18 Wetland by River Lelrechka NM Wetland 95 29/12/1997 19 20 Wetland Zamoshye №483 NM NM Wetland Wetland 178 43 29/12/1997 29/12/1997 21 Wetland by the village of Boyarschina NM Wetland 24 29/12/1997 22 Klim-Gora NM Landscape 617 21/10/1993 Anisimovschina Wetland Pala №400 Wetland by Petrikov’s Bay Reports of the Finnish Environment Institute 40 | 2014 20/07/1984 Fig 1. Location of the existing and planned protected areas of Zaonezhye Peninsula. Reports of the Finnish Environment Institute 40 | 2014 79 80 Reports of the Finnish Environment Institute 40 | 2014 2 Biomes and biogeography of Zaonezhye Peninsula area 2.1 Modern landscapes of Zaonezhye Peninsula Maria S. Bogdanova Institute of Water Problems in the North of the Karelian Research Center of Russian Academy of Sciences. 50 Alexandra Nevskogo St., 185003 Petrozavodsk, Karelia, Russia E-mail: mari-mb@mail.ru Zaonezhye is located on the northern shore of Lake Onega. It includes Zaonezhye Peninsula and the adjacent Kizhi Archipelago. According to the biogeographical classiication of Northwest Russia, Zaonezhye belongs to the Karelian middle taiga region of the Eastern European taiga zone (A. Isachenko 2008). Selkä terrain, plains and drained and cultivated peatland dominate the landscape. The selkäs are elongated ridges of consolidated crystalline rocks, whereas the plains consist of boulder, sandy loam and loam or boulder-free sand and loam. In the course of the history, a succession of human communities with different economic activities, agricultural practices and socioeconomic conditions exerted a considerable inluence on the modern landscapes of the region. I have divided the landscape history of Zaonezhye into eight stages from the Mesolithic period to the present, based on the analysis of available data (Bogdanova 2011). To assess the present landscapes of Zaonezhye, basic features of the landscape are divided based on landscape dynamics into site features (relatively stable properties of relief and underlying rocks) and long-term states (more dynamic characteristics of vegetation and soils). Landscape areas are described using three basic indices: 1) landform or morphological features of the relief, 2) composition of underlying (soil-forming) rocks in the uppermost (1 m) layer and 3) moisture regime (drainage conditions). Natural processes as well as human activities have inluenced the landscape dynamics, which consists of different states of different lengths (G. Isachenko 1998, 2007). The landscapes of Zaonezhye were studied between 2005 and 2013. Basic landscapes were described during ield studies. The resulting 1050 landscape descriptions formed the basis for the database “Landscape structure of the Zaonezhye hydrographic province, Republic of Karelia” (Bogdanova 2014). Large-scale maps show key areas of the most representative landscapes. I have developed a classiication of basic landscapes in Zaonezhye and prepared a 1:200 000 scale landscape map. The map shows 775 contours and 32 different types of landscapes, including 16 landscape combinations. Contrasting landscapes are combined if the map scale is too large to show small-scale differences when landscapes succeeded one another at determined intervals. In addition to natural landscapes Reports of the Finnish Environment Institute 40 | 2014 81 (unaffected by human activities), the map shows 14 types of landscapes modiied by long-term agricultural use and/or drainage as well as three artiicial landscapes. The total area studied is 1964 km2, including the inland water bodies and islands of Zaonezhye Peninsula (but excluding Bolshoi Klimenetsky, Yernitsky and Bolshoi and Maly Lelikovsky Islands). The landscape map provides a reliable tool for describing the spatial distribution of natural complexes in Zaonezhye and assessing their present condition. The spatial distribution of the landscapes and their long-term vegetation and soil types are shown in Table 1. When vegetation and soil cover are fragmented and diverse, only dominant vegetation and soil types are described. Table 1. Landscape classiication in Zaonezhye. Landscape sites Long-term states Dominant vegetation Area Dominant soil types km2 % Combinations of selkä ridges and depressions (The elongated selkä ridges consist of Proterozoic crystalline rocks, such as gabbro-dolerite, shungite shale, tuff schist and tufite, covered by moraine and diluvium. The depressions between the ridges are covered by boulder, sandy loam and loam, or a thin layer of peat.) 1. High selkä ridges (relative height 40–90 m) with lat tops and stepped slopes, covered by a layer of eluvium-deluvium and moraine (up to 1.0–1.5 m) and peat (up to 1 m). Rocky scarps are up to 30 m high and their lower parts are covered by coarse clastic material. Pine- and spruce-dominated Vaccinium myrtillus-Calamagrostis arundinacea forests on the ridge tops and slopes; Spruce-dominated forests with a large proportion of pine, birch and aspen; Aspen-dominated forests with spruce, birch, Vaccinium myrtillus and green moss; Bogs in depressions and on the slopes Primitive 75.0 soils, Leptosols, Cambisols, Peat bog, Soil absent 3.8 2. High, rugged selkä ridges (relative height 30–80 m) with numerous rock exposures and cliffs (relative height 30 m). The ridge tops and slopes are covered by a layer of discontinuous eluvium-deluvium and moraine (up to 0.5 m). Sparse pine forests with Vaccinium vitis-idaea and lichen, as well as rocky wasteland on the ridge tops; Birch- or pine-dominated forests with green moss, Vaccinium myrtillus, V. vitis-idaea and lichen on the slopes; Bogs in depressions Primitive 85.5 soils, Leptosols, Peat bog, Soil absent 4.4 3. Poorly structured selkä ridges (relative height up to 20 m) with few rock exposures and a layer of discontinuous eluvium-deluvium and moraine (up to 0.5 m) Sparse pine forests with green moss, Vaccinium vitis-idaea, dwarf shrubs and lichen, as well as rocky wasteland on the ridge tops; Primitive, 37.5 Leptosols, Soil absent 1.9 Combinations of contrasting landscape sites, dominated by drained slopes with mineral soils, where differences in elevation are more than 10 m 4. Hills and ridges consisting of sandy loam and boulder (relative height up to 20 m), combined with plains formed of sand, clay and boulder and sandy loam, as well as thin peatlands 82 Reports of the Finnish Environment Institute 40 | 2014 Pine-, spruce- or birch-dominated forests with green moss, Vaccinium myrtillus, dwarf shrubs and Calamagrostis arundinacea; Former clearcut areas covered by Calamagrostis arundinacea and secondary mixed forests, developed through natural succession; Different types of mires from bogs to fens in depressions Leptosols, 86.3 Cambisols, Peat bog 4.4 5. Hills and ridges consisting of sandy loam and boulder, often with crystalline rock exposures, combined with undulating plains formed of consolidated boulder, sand and sandy loam, as well as thin peatlands Sparse pine forests with dwarf Leptosols, 46.5 shrubs, green mosses and lichen on Cambisols, tops of eskers; Peat bog Spruce-, aspen- or birch-dominated forests with pine, green mosses, Vaccinium myrtillus, dwarf shrubs and Calamagrostis arundinacea; Clearcut areas covered with Calamagrostis arundinacea, Rubus idaeus and Chamaenerion angustifolium; Secondary mixed forests, developed through natural succession of former clearcut areas on the slopes and in depressions; Transitional and raised bogs in depressions 2.4 6. Elongated hills and ridges consisting of sand and pebble or sand and boulder, combined with peatlands in depressions. Often there are also plains consisting of boulder, pebble and sand. Birch- or pine-dominated forests with dwarf shrubs and green moss; Clearcut areas in different stages, covered with Calamagrostis arundinacea and Chamaenerion angustifolium; Fens and transitional bogs in depressions 0.9 Podzol, Surface podzol, Peat bog 16,9 Combinations of contrasting landscape sites, dominated by drained slopes with cultivated mineral soils, where differences in elevation are more than 10 m 7. Cultivated hills and ridges consisting of sandy loam and boulder (relative height up to 20 m), commonly combined with plains formed of sand and clay or boulder, sand and loam, as well as thin peatlands Grassland (Poaceae and herbaceous meadows), arable land and abandoned meadows, which have become overgrown with trees; Young birch, aspen and pine forests with herbaceous plants and spruce; Fens and transitional bogs in depressions Cambisols- 21.1 old arable soils, Peat bog 1.1 8. Cultivated hills and ridges (eskers) consisting of shungitic and shungite-bearing pebble, boulder and sand, combined with cultivated plains formed of boulder, pebble and sand, as well peatlands in depressions Grass and herbaceous meadows, arable land, overgrown meadows; Young birch, aspen and pine forests with herbaceous plants; Fens and transitional bogs in depressions Shungite cambisolsold arable soils, Peat bog 45.5 2.4 Surface podzol 6.5 0.3 Podzols, Surface podzol, Peat bog 103.43 5.3 Drained plains, dominated by mineral soils 9. Plains formed of boulder-free sand and sandy loam Pine-dominated forests with dwarf shrubs and green moss; Birch-dominated forests with spruce, Vaccinium myrtillus and Calamagrostis arundinacea 10. Plains formed of small boulder, Birch- or pine-dominated forests pebble and sand, often combined with with spruce, Calamagrostis arundinathin peatlands cea, dwarf shrubs and green moss; Fens and transitional bogs 11. Undulating plains and gently sloping ridges on consolidated boulder, sand and sandy loam, often combined with thin peatlands Birch- or aspen-dominated forests Leptosols, 357.2 with pine, spruce, dwarf shrubs, Cambisols, Calamagrostis arundinacea and green Peat bog moss; Young mixed forests with herbaceous plants; Clearcut areas covered with Calamagrostis arundinacea and Chamaenerion angustifolium fens and transitional bogs 18.2 Cultivated drained plains, dominated by mineral soils 12. Cultivated, undulating plains and terraces formed of boulder-free sand and sandy loam (lacustrine-glacial and glacial) Grass and herbaceous meadows, Soddy old 37.7 arable land, overgrown meadows; arable soils Young mixed forests, dominated by birch or aspen, with herbaceous plants and pine 1.9 Reports of the Finnish Environment Institute 40 | 2014 83 13. Cultivated, undulating plains formed of small boulder, pebble and sand (luvioglacial deposits) Grass and herbaceous meadows, Cambisols- 22.4 arable land, overgrown meadows; old arable Mature mixed forests, dominated soils by birch or aspen, with herbaceous plants and pine; Young mixed forests, dominated by spruce, birch or aspen with herbaceous plants and Calamagrostis arundinacea 1.1 14. Cultivated, undulating plains and gently sloping ridges on consolidated boulder, sand and sandy loam (moraine) Grass and herbaceous meadows, arable land, overgrown meadows; Young forests dominated by birch, common alder (Alnus glutinosa) and bird cherry (Padus avium) with herbaceous plants Mature spruce or aspen dominated forests with pine, herbaceous plants and Calamagrostis arundinacea Cambisols- 120.9 old arable soils 6.2 Combinations of plains with different soil moisture contents 15. Permanently saturated plains, covered with boulder-free sand, quite often with a thin layer of peat, with a mildly undulating and gently sloping relief. These landscapes also include small peatlands. Forests dominated by pine, birch and common alder with herbaceous plants, sedges, horsetail and Sphagnum; Fens and transitional bogs Humic gley, Peaty gley, Peat bog 9.9 0.5 16. Permanently saturated plains, covered with boulder-free clay and sandy loam, quite often with a thin layer of peat, with a mildly undulating relief. These landscapes also include small peatlands. Birch-, aspen- or pine-dominated forests with common alder, herbaceous plants and Vaccinium myrtillus; Birch-, pine- or common alder-dominated forests with herbaceous plants, sedges and Sphagnum; Birch forests with meadowsweet (Filipendula) and sedges; Lowland fens and transitional bogs Humic gley , Peaty gley, Peat bog 88.6 4.5 17. Saturated plains, covered with boulder and sandy loam, quite often with a thin layer of peat. These landscapes also include small peatlands and hills, consisting of sand and boulder. Birch, pine and spruce forests with herbaceous plants, Vaccinium myrtillus and Sphagnum; Birch, pine and dwarf shrub forests on the hills; Fens and transitional bogs in depressions Cambisols, 69.6 Gley cambisols, Peaty gley, Peat bog 3.5 18. Drained peatland and artiicially drained plains with a thin layer of peat (up to 0.5 m); often combined with drained plains Birch and pine forests or birch, pine and spruce forests with dwarf shrubs, Sphagnum and herbaceous plants of moist soils Peaty gley, Humic gley, Cambisols 10.3 0.5 Combinations of cultivated sites with different soil moisture contents (plains and low hills) 84 19. Predominantly cultivated, saturated plains, covered with boulder-free clay and sandy loam, quite often with a thin layer of peat. These landscapes include small peatlands and cultivated hills of sand and boulder. Meadowsweet (Filipendula) and sedge-meadowsweet meadows, including those overgrown with willow and birch; Meadows with herbaceous plants, sedges and Sphagnum; Young deciduous forests with herbaceous plants and pine; Grass and herbaceous meadows and deciduous forests with pine growing on the hills; Fens and transitional bogs in depressions Humic 14.2 gley, Peaty gley, Peat bog, Cambisolsold arable soils 0.7 20. Cultivated plains and gently sloping ridges, covered with boulder, shungite-bearing and shungitic sandy loam, often combined with shallow peatlands Arable land, grass and herbaceous meadows, overgrown meadows; Young grey alder and birch forests; Birch-or aspen-dominated forests with pine or spruce, herbaceous plants, Vaccinium myrtillus and green moss; Fens and transitional bogs Shungite cambisolsold arable soils, Peat bog 11.6 Reports of the Finnish Environment Institute 40 | 2014 227.4 21. Cultivated, drained plains and gently sloping ridges covered with boulder and shungitic sandy loam, with crystalline rock exposures. These are often combined with plains formed of boulder-free, sandy loam. Grass and herbaceous meadows, arable land, overgrown meadows; Young small-leaved forests with herbaceous plants; Birch and aspen forests with herbaceous plants, pine and spruce; Meadows of herbaceous plants and sedges, mixed with birch forests with herbaceous plants and sedges of moist soils Cambisols- 34.3 old arable soils, Humic gley 1.7 22. Cultivated, artiicially drained plains, covered with boulder-free clay and sandy loam, as well as paludiied plains with a thin layer of peat. Occasionally there are also cultivated hills of sand and boulder. Grass, tall grass and herbaceous meadows, including overgrown meadows; Meadows with sedges and Sphagnum; Small-leaved forests with herbaceous plants and pine; Fens and transitional bogs Soddy hu- 30.8 mic gley, Peaty gley, Peat bog, Cambisolsold arable soils 1.6 Peatland with a peat layer of more than 0.5 m 23. Oligotrophic raised bogs (peat over 1.5 m thick) Pine-covered Sphagnum-cottongrass-dwarf shrub bogs Raised bog 24.8 soils 1.3 24. Drained oligotrophic raised bogs Pine-covered Sphagnum-cottongrass-dwarf shrub bogs Drained raised bog soils 3.3 0.2 25. Meso-oligotrophic and mesHerb-sedge-Sphagnum bogs, often otrophic peatland (varying thicknesses covered with birch and pine; of peat) Moist birch- or pine-dominated forests with herbaceous plants, sedges and Sphagnum Mesotrophic bog soils 40.3 2.0 26. Drained meso-oligotrophic and mesotrophic peatland Herb-sedge-Sphagnum bogs, often covered with birch and pine; Moist birch- or pine-dominated forests with herbaceous plants, sedges and Sphagnum Drained mesotrophic bog soils 5.00 0.3 27. Drained, cultivated meso-oligotrophic and mesotrophic peatland Grass and herbaceous meadows; Moist meadows with herbaceous plants and sedges following the cessation of agriculture; Moist meadows with herbaceous plants and sedges, including those with birch undergrowth; Birch forests with moist herbaceous plants Drained mesotrophic bog soils and cultivated bog soils 16.0 0.8 28. Mesoeutrophic and eutrophic peatland in lotic depressions; varying thicknesses of highly mineralized peat Sedge and herb-sedge bogs with willow, birch and black alder; Black alder and birch forests with moist herbaceous plants; Reed thicket Boggy fen peat and bog-gley soils 5.5 0.3 Drained and cultivated boggy fen peat and bog-gley soils 122.1 6.2 29. Drained, cultivated mesoeutrophic Grass and herbaceous meadows; and eutrophic peatland Meadows with moist herbaceous plants and sedges following the cessation of agriculture; Birch scrub forests; Birch forests with moist herbaceous plants Sites with relief and grounds transformed by human activities 30. Former peat production areas Peat wasteland in areas affected by ires; Burned moorland with heather Young birch forests Soil absent 3.6 0.2 31. Sand- and gravel-pits Only sparse vegetation during Soil quarrying; absent Young pine and small-leaved forests after the cessation of quarrying 0.5 <0.1 Reports of the Finnish Environment Institute 40 | 2014 85 32. Shungite rock quarries Only sparse vegetation during quarrying; Young small-leaved forests after the cessation of quarrying Soil absent Inland water bodies on the peninsula, excluding Lake Onega bays Total 0.3 <0.1 194.3 10.3 1964 100 Fig.1. Landscape areas of Zaonezhye Peninsula. Numbers indicate l andscape areas: 1. Kosmozero-Putkozero; 2. Dianogorsko-Mizhostrov; 3. Pigmozero; 4. Myagrozero-Lelikovo; 5. Shunga-Kuzaranda; 6. Limozero-Gankovo; 7. Velikaya Guba-Tambitsy; 8. Kizhi Due to the characteristics of the geological structure, the landscape pattern of Zaonezhye is fragmented, including a mosaic of small-scale landscapes. Its landscape contours are typically elongated from northwest to southeast. In Zaonezhye, a total of eight landscape areas are identiied based on recurrent combinations of landscapes (Fig. 1): 1. Kosmozero-Putkozero area, dominated by selkä ridges, cultivated plains and hills 2. Dianogorsko-Mizhostrov area, dominated by selkä ridges 3. Pigmozero area, dominated by luvioglacial sand plains and peatland 4. Myagrozero-Lelikovo area, dominated by moraine plains and peatland 5. Shunga-Kuzaranda area, dominated by cultivated land on shungite and shungite-bearing rocks, as well as drained and cultivated plains and peatland 6. Limozero-Gankovo area, dominated by moraine plains, covered with a thin layer of peat, as well as peatland and drained peatland 7. Velikaya Guba-Tambitsa area, dominated by cultivated plains on moraine, and peatland 8. Kizhi area, dominated by cultivated land on shungite and shungite-bearing rocks. 86 Reports of the Finnish Environment Institute 40 | 2014 Cultivated land makes up a large proportion of the landscapes in Zaonezhye. In the past, it has been one of the most agriculturally developed areas in Karelia. Agricultural development in Zaonezhye began in the 9th and 10th centuries, although natural complexes were most signiicantly transformed in the 19th century. By the end of the 19th century, agricultural development had reached its peak with about 30% of the peninsula cultivated for arable crops or hay. Old arable land is characterized by a well-deined soil horizon, even if the land is no longer cultivated. Normally the horizon is over 15 cm thick. On old arable land, speckled alder, birdcherry and mountain ash dominate the forest cover, whereas the ground cover is characterised by meadow species. The agricultural development of Zaonezhye is characterized by the cultivation of bouldery (moraine and luvioglacial) plains, ridges and hills as well as gently sloping selkäs and relatively steep slopes of (up to 50–70%) crushed stone. Boulders were removed and stored for future use. Local people called these piles rovnitsas. Rovnitsas are a part of the cultural landscape of Zaonezhye, reminding of its agricultural history. It was not until the late 20th century that people began draining bogs here. Until then only small parts of paludiied plains and lowland bogs had been used for cultivating hay. During the past centuries unique cultural landscapes have formed in Zaonezhye where plains, selkä ridges, coniferous and small-leaved forests, dry valley forests, arable land and lakes coexits. Wooden architecture is an inseparable part of the region’s landscape. There are several well-preserved old wooden buildings in Zaonezhye, including 96 architectural monuments (including the famous churches of Kizhi Island), of which 65 are listed buildings. The best example of wooden architecture in Zaonezhye is the Kizhi Pogost with the Church of the Intercession and the Church of the Transiguration. Kizhi Pogost is included in the UNESCO list of World Heritage Sites. Zaonezhye landscapes are transforming: Coniferous and small-leaved forests are maturing. Agricultural land has become overgrown. Cutting areas and abandoned quarries grow scrub forests. Over 20 different dynamic processes have been identiied in different types of landscapes. The following trends are most typical for the region: • The composition and growing stock of pine and spruce forests on selkä ridges have stabilized. • The phytomass and growing stock of young and middle-aged small-leaved coniferous forests in cutting areas have increased. • The phytomass and growing stock of young and middle-aged small-leaved forests and small-leaved coniferous forests on former agricultural land have increased. • Secondary paludiication of reclaimed land is accompanied by the appearance of mesohygrophytes and hygrophytes in the vegetation cover. Vegetation cover is actively overgrow by scrub forests. • Meadows are declining and secondary small-leaved forests are increasing as former agricultural land becomes overgrown with speckled alder, birch, aspen and pine. • Grass and herb-grass communities are succeeded by tall grass-chervil (Anthriscus sylvestris) and tall grass-raspberry (Rubus idaeus) communities. If Zaonezhye landscapes are left without human intervention, the area of both young and mature mixed small-leaved forests as well as small-leaved coniferous for- Reports of the Finnish Environment Institute 40 | 2014 87 ests will increase in the next 50 years. Also the portion of young small-leaved forests on overgrown meadows is expected to increase. A wide range of landscapes on Zaonezhye Peninsula needs protection, including the rapidly disappearing cultural landscapes. Protected areas with different protection regimes should be established to promote nature conservation and environmental tourism in the area. REFERENCES BШРНКЧШЯК, . S. 2011. . . : . ДTСО НОЯОХШЩЦОЧЭ СТsЭШrв КЧН ЭСО ЩrОsОЧЭ МШЧНТЭТШЧ ШП ГКШЧОгСвО’s ХКЧНsМКЩОs: ХКЧНsМКЩО-НвЧКЦТМ sЭЮНвЖ.− IгЯОsЭТвК ШП RЮssТКЧ GОШРrКЩСв SШМТОЭв 143 (2): 23–31. (IЧ Russian). BШРНКЧШЯК, . S. 2014. . . ( ). – ДLКЧНsМКЩО sЭrЮМЭЮrО ШП ЭСО ГКШЧОгСвО СвНrШРrКЩСТМ ЩrШЯТЧМО, RОЩЮЛХТМ ШП KКrОХТКЖ CОrЭТiМКЭО ШП ЭСО ШПiМТКХ rОРТsЭrКЭТШЧ ШП ЭСО НКЭКЛКsО ЧШ. 2014620226 ШП 5.02.2014. (IЧ RЮssТКЧ). IsКМСОЧФШ, . G. 2008. . . , , . ДTСО EКrЭС’s ХКЧНsМКЩО sЭrЮМЭЮrО, sОЭЭХТЧР КЧН ЭСО ЮsО ШП ЧКЭЮrКХ rОsШЮrМОsЖ. – SЭ. PОЭОrsЛЮrР. 320 Щ. (IЧ RЮssТКЧ). IsКМСОЧФШ, G. . 1998. . . ДMОЭСШНs ПШr iОХН ХКЧНsМКЩО sЭЮНв КЧН ХКЧНsМКЩО-ОЧЯТrШЧЦОЧЭКХ ЦКЩЩТЧРЖ. – SЭ. PОЭОrsЛЮrР. 112 Щ. (IЧ RЮssТКЧ). IsКМСОЧФШ, G. A. 2007. LШЧР-ЭОrЦ МШЧНТЭТШЧs ШП ЭКТРК ХКЧНsМКЩОs ШП EЮrШЩОКЧ RЮssТК. – IЧ: LКЧНsМКЩО AЧКХвsТs ПШr SЮsЭКТЧКЛХО DОЯОХШЩЦОЧЭ. TСОШrв КЧН AЩЩХТМКЭТШЧs ШП LКЧНsМКЩО SМТОЧМО ТЧ RЮssТК. MШsМШа, AХОб PЮЛХТsСОr Щ. 144–155. Fig. 2. Flat top of the selkä ridge (Landscape sites 1, Table 1) (Photo Maria Bogdanova). 88 Reports of the Finnish Environment Institute 40 | 2014 Fig. 3. Stepped slope of the selkä ridge (Landscape sites 1, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 89 Fig. 4. Rugged top of the selkä ridge (Landscape sites 2, Table 1) (Photo Maria Bogdanova). 90 Reports of the Finnish Environment Institute 40 | 2014 Fig. 5. Slope of the selkä ridge (Landscape sites 2, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 91 Fig. 6. Cliff of the selkä ridge (Landscape sites 1 and 2, Table 1) (Photo Maria Bogdanova). 92 Reports of the Finnish Environment Institute 40 | 2014 Fig. 7. Poorly structured low selkä ridge (Landscape sites 3, Table 1) (Photo Maria Bogdanova). Fig. 8. Cultivated ridge (esker) consisting of pebble, boulder and sand (Landscape sites 8, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 93 Fig. 9. Arable land on esker, consisting of shungitic pebble and sand (Landscape sites 8, Table 1) (Photo Maria Bogdanova). Fig. 10. Plain formed of boulder-free sand (Landscape sites 9, Table 1) (Photo Maria Bogdanova). 94 Reports of the Finnish Environment Institute 40 | 2014 Fig. 11. Plain on consolidated boulder, sand and sandy loam (moraine) (Landscape sites 11, Table 1) (Photo Maria Bogdanova). Fig. 12. Cultivated plain formed of boulder-free sand (Landscape sites 12, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 95 Fig. 13. Plain formed of small boulder, pebble and sand (luvioglacial deposits) (Landscape sites 13, Table 1) (Photo Maria Bogdanova). Fig. 14. Cultivated plain on consolidated boulder, sand and sandy loam (moraine) (Landscape sites 14, Table 1) (Photo Maria Bogdanova). 96 Reports of the Finnish Environment Institute 40 | 2014 Fig. 15. Overgrown arable land on consolidated boulder, sand and sandy loam (moraine) (Landscape sites 14, Table 1) (Photo Maria Bogdanova). Fig. 16. Plain covered with boulder-free clay and sandy loam (Landscape sites 16, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 97 Fig. 17. Cultivated, artiicially drained plain, covered with boulder-free clay and sandy loam (Landscape sites 22, Table 1) (Photo Maria Bogdanova). Fig. 18. Oligotrophic raised bog (Landscape sites 23, Table 1) (Photo Maria Bogdanova). 98 Reports of the Finnish Environment Institute 40 | 2014 Fig. 19. Mesotrophic peatland (Landscape sites 25, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 99 Fig. 20. Eutrophic peatland (Landscape sites 28, Table 1) (Photo Maria Bogdanova). Fig. 21. Former peat excavations (Landscape sites 30, Table 1) (Photo Maria Bogdanova). 100 Reports of the Finnish Environment Institute 40 | 2014 Fig. 22. Sand- and gravel-pit (Landscape sites 31, Table 1) (Photo Maria Bogdanova). Reports of the Finnish Environment Institute 40 | 2014 101 Fig. 23. Shungite rock quarry (Landscape sites 32, Table 1) (Photo Maria Bogdanova). 102 Reports of the Finnish Environment Institute 40 | 2014 2.2 Landscape structure of Zaonezhye Peninsula Vladimir Karpin Forest Research Institute of the Karelian Research Center of Russian Academy of Sciences 11 Pushkinskaya St., 185610 Petrozavodsk, Karelia, Russia E-mail: landscapeexplorer@gmail.com Introduction Zaonezhye Peninsula is characterised by a complex landscape structure as well as a diverse forest cover. According toVolkov et al. (1990), Gromtsev (2008) and Gromtsev (2013), there are two contrasting types of geographical landscapes on Zaonezhye Peninsula (Fig.1): (1) Paludiied lacustrine and lacustrine-glacial plains occur in the east, where forests are dominated by spruce (II in Fig 1), while (2) paludiiedtectonic-denudation ridge (selkä) landscapes occur in the west,where forets are dominated by pine (I in Fig.1). The landscape structure of Zaonezhye consists of large geomorphological areas, or geographical terrains. These geomorphologically uniform areas cover approximately 10 000 hectares (or over 90 % of the area). The geographical terrains have a homogeneous composition of Quaternary sediments as well as uniform hydrographic and soil conditions. As a consewuenve, they show a constant succession of forest and mire complexes on the mesoscale, covering areas of 10–100 ha (Gromtsev 2000, 2008). Fig. 1. Geographical terrains of Zaonezhye Peninsula.Image and fax viewing software. Reports of the Finnish Environment Institute 40 | 2014 103 Results The tectonic-denudation landscape of Zaonezhyevaries at the sub-landscape level (Selkä landscapes2013). Three types of geographical terrains have been identiied: Moderately paludiiedtectonic-denudation ridge terrain, dominated by pine habitats (No. 1 in Fig. 1) This dominant terrain type covers 40 % of the area (Fig. 2). Its relief is a result of multiple tectonic movements that have created a system of northwest-trending subparallel folds, comprising ridges (selkäs), steep slopes and steplike scarps. The long and rocky ridges correspond to synclines, whereas the straight, narrow and shallow basins and bays of Lake Onega are consistent with the anticlines. Thefold structure is broken by a system of stepped strike-slip faults.Quaternary sediments are represented by a thin moraine cover. On the ridge tops, moraine is either dozens of centimeters thick or completely absent, while on the slopes and in the depressions between the ridges moraine can be up to 2 m thick. Altitudes range from 33 m to 202 m, while altitudes of adjacent landforms vary between 20 m and 50 m above sea level. Overall, mires cover less than 20% of the terrain. Open mires account for 5%. Mires are predominantly mesotrophic or oligotrophic. Hydrographically, the percentage of lakes is relatively high (28%). The network of rivers and lakes shows a pattern of small streams and small lakes, which contributes to the fragmentation of the forest cover. The soil cover is dominated by two soil types: Primitive, poorly developed soils cover bedrock exposures on ridgetops and rocky shores. These soils are infertile and susceptible to erosion. More fertile, humus-rich soils known as Leptosol are common on ridge slopes. The dissected topography, disrupted with tectonic dislocations, is responsible for a distinctive microclimate. Conditions are favourable for more southern lora and fauna on south-facing slopes, which receive more sunlight and are protected against cold, northerly winds. More northern higher vascular plant and moss species occur on north-facing slopes and in narrow crevasses. Considerable variations in altitude (up to 200 m) at this latitude (62–63°N) have resulted in altitudinal zoning. As a consequence, frosts occur 10–30 days earlier in the elevated areas. Also the numerous lakes have a substantial effect on the microclimate. The forest cover has been considerably transformed by selective and clear cutting. However, most of the forest communities have survived or recovered due to the relatively small number of trees removed as well as the natural dynamics of the forests.In contrast with the rest of Zaonezhye, there is practically no agricultural development in this terrain. In this geographical terrain (No. 1 in Fig. 1), the forest cover consists mainly of pine forests, growing on rocky ground, and pine-dominated forests of Myrtillus type, growing on tectonic blocks that are covered by a thin layer of unconsolidated sediments. Other predominant forest types include mesic, pine- or spruce-dominated stands of Myrtillus type on the slopes and in the depressions between the ridges. These forests are characterized by diverse ground vegetation and complex plant communities. Birch-dominated stands make up less than 5% of the area covered by forests of Myrtillus type. However, their ground vegetation is diverse, including combinations of herbaceous species, motley grass and Myrtillus patches. On average, these plant communities are restricted to relatively small areas. Paludiied glacial terrain of hills and ridges, dominated by pine habitats (No. 2 in Fig. 1) This terrain type covers 30% of the tectonic-denudation landscapes (Fig.3). Its glacial relief comprises of plains, intersected by gently sloping, lat-topped ridges 104 Reports of the Finnish Environment Institute 40 | 2014 without a well-deined foot of the hill. Altitudes vary between 60 and 120 m above sea level and vertical ruggedness is 30–40 m. Quaternary sediments consist mainly of moraine that forms a 4–7 m layer, covering 70–80% of the crystalline basement and evening out the rugged bedrock. In parts of the terrain, also moraine drumlins contribute to the ridge pattern.Overall, mires cover approximately 20% of the terrain and open mires 8%. These eutrophic and mesotrophic mires contain a diverse lora and a variety of plant communities. The hydrographic network is well developedand uniform. The largest rivers are between 10 km and 30 km long. Lakes account for approximately 7% of the terrain. The soil cover is dominated by acidic, sandy loam and loamy burozems (Cambisols). These highly fertile soils areazonal and provide good conditionsfor a relatively high biological diversity for Karelia. With the exception of the western parts of the terrain, the gently sloping landscape and the minor vatiations in altitude have created a uniform microclimate. In the western parts, Lake Onega evens out considerable variations in temperature. Vegetation has been markedly transformed by long-term slash-and-burn farming of fertile land as well as continuous selective and clear cutting. However, forest regeneration has been successful over most of the area and plant communities have largely been restored to their original state. Nowadays, the forest cover is characterised by a mosaic of fresh pine and spruce forests of Myrtillus type with nemoral elements in the ground vegetation.Other common vegetation types include birch forests of Myrtillus type as well as herbaceous birch forests, growing on abandoned agricultural land. Also these forests have nemoral elements in the ground vegetation. Grey alder (Alnus incana) forests with a large proportion of mountain ash (Sorbusaucuparia) and European birdcherry (Padus racemosa) often grow on the most fertile sites. Spruce is absent in these stands. Some Sphagnum habitats are occupied by low-productive secondary spruce and birch stands. The average contour of the plant communities is 120 m long. Paludiied lacustrine-glacial hill terrain, dominated by pine stands (No.3 in Fig. 1) The relief of this terrain has been affected by the regression of Lake Onega (Fig.4). It makes up 30% of the tectonic-denudation landscapes. Its gently sloping, undulating plain is formed through accumulation and abrasion (of former lake bottom). Active movement along crystalline faults has produced small ridges, although they are not characteristic of this terrain. Absolute altitudes of watersheds are no more than 60 m above sea level and vertical ruggedness is 5–20 m. Overall, mires make up 20% of the terrain. Open mires account for 6% of the terrain. Due to their lacustrine origin, mires are predominantly mesotrophic or eutrophic. Usually peat is underlain by sapropel, lake clay and silt. These features have resulted in diverse plant communities and a rich lora. Long and narrow lakes, conined to faul zones, determine the hydrographic conditions of the terrain. Lakes cover no more than 10 % of the area (excludingUnitsa Bay and a small portion of Lizhma Bay). Small streams that are less than 5 km long are distributed evenly throughout the area. The diverse soil cover consists of dark, acidic sandy loam and loam burozemson shungite, marshland humus gley and lowland peat soils. These fertile soils provide good conditions for a variety of species and plant communities. In addition, the microclimate is uniform across the terrain. However, the area has been heavily affacted by human activities, including forest cutting and agriculture. There is an increasing amount of highly fertile soils (on land formerly used for agriculture), covered by secondary forests or secondary forest and meadow communitites. The forest cover is a mosaic of fresh pine and birch forests with a diverse ground cover (motley grass, motley grass-bilberry, grass-bilberry, etc.). Also pine forestswith Sphagnum are widespread. Spruce forests make up only a Reports of the Finnish Environment Institute 40 | 2014 105 small percentage of the area, but their ground cover is diverse. Birch communities are mostly conined to abandoned agricultural land.All these forest types host a variety of woody and shrub species, including nemoral species such as lime, elm and currant. The average contour of the plant communities is 120 m long. Normally paludiied lacustrine and lacustrine-glacial plains, dominated by spruce, have indistinct boundaries, although their core areas are well deined. This landscape type comprises the following geographical terrains: Paludiied terrain of moraine plains, dominated by spruce habitats (No. 4 in Fig. 1) This is the dominant terrain type, covering 50% of the paludiied landscapes of lacustrine and lacustrine-glacial plains (Fig. 5). Its glacial relief consists of a plain with gently sloping hills and lat-topped ridges that lack a well-deined foot of the hill. Altitudes vary between 50 and 90 m above sea level and vertical ruggedness is 10–30 m. Quaternary deposits consist of a 4–7 m thick layer of moraine, which covers 90–100% of the crystalline basement and smoothes the ruggedness of the bedrock. In parts of the terrain, a ridge relief is formed by moraine drumlins. Mires make up about 50% and open mires 15% of the terrain. These eutrophic and mesotrophic mires contain a diverse lora and a variety of plant communities. The hydrographic network is well developedand uniform. Rivers are between 10 km and 30 km long and there are practically no lakes. The soil cover is dominated by acidic, sandy loam and loamy burozems. The gently sloping landscape and the minor vatiations in altitude have created a uniform microclimate. However, Lake Onega evens out considerable variations in temperature in its vicinity. Vegetation has been considerably transformed by long-term slash-and-burn cultivation of fertile land as well as continuous selective and clear cutting. However, forest regeneration has been successful over most of the area and plant communities have largely been restored to their original state. Nowadays, the forest cover is characterised by a mosaic of fresh bilberry spruce forests that grow on the enriched ground. Other common vegetation types include bilberry, bilberry-grass and wide-grass aspen and birch forests. The most fertile soils host plant communities, consisting of speckled alder as well as extensive mountain ash and European birdcherry stands. In these communities, spruce is absent in the undegrowth. Some Sphagnum habitats are occupied by low-productive secondary spruce and birch stands. The average contour of the plant communities is 120 m long. Moderately paludiied, topographically complex aqueo-glacial terrain, dominated by pine stands (No.5 in Fig 1) This terrain type makes up approximately 20 % of the landscape area (Fig. 6). Fluvioglacial landforms include radial ridges (eskers), associated with luvioglacial deltas. The terrain extends for over 30 km from northwest to southeast. Altitudes vary between 5 m and 15 m. Absolute altitudes of watersheds are no more than 80 m above sea level. Overall, mires cover up to 20% of the terrain, while open mires account for 5% of the terrain. Raised bogs with low mineral consentrations are common. There are no lakes in the terrain, and streams are less than 5 km long creeks. Microclimatic conditions remain more or less the same throughout the terrain. The soil cover consists of podzols and leptosols. More fertile sites include clasts of local basic and shungite-bearing rocks. Ridges and wide delta-like areas are used for agriculture. The forest cover is considerably transformed. It shows a mosaic pattern (Fig.) of pine, aspen and birch stands, growing in fresh bilberry habitats with diverse ground 106 Reports of the Finnish Environment Institute 40 | 2014 vegetation (motley grass, motley grass-bilberry, grass-bilberry, etc.). Often speckled alder grows on abandoned agricultural land. Wet habitats are occupied by Sphagnum. Spruce stands are few. The undergrowth consists of currant, lime, buckthorn and birdcherry. The average contour of the plant communities is 70 m. Highly paludiied lacustrine-glacial terrain of plains, dominated by spruce habitats (No. 6 in Fig. 1) This terrain type makes up 30% of the landscapes (Fig. 7). Its relief consists of a plain with gently sloping hills. Absolute altitudes are estimated at no more than 80 m above sea level and vertical ruggedness is 5–20 m. Structural denudation landforms are completely covered by unconsolidated sediments, which are dominated by a 6–7 m thick layer of varved clay. Overall, mires make up 70% of the area, while open mires account for 30% of the area. Mires are predominantly eutrophic and mesoeutrophic and their lora consist of both marshland and forest species. Streams are less than 5 km long and lakes cover no more than 5 % of the terrain.The microclimate is uniform across the terrain. Well-drained eluvial, surface and gley loam soils support highly productive forests. However, the forest cover has been totally transformed by selective and clear cutting as well as agriculture. Nowadays, secondary forests dominate most of the area, including abandoned agricultural land. The most common forests are aspen, birch and speckled alder stands of bilberry and horsetail types. These forests have succeeded spruce stands,which are characteristic of the terrain. Black alder communities are encountered on stream-irrigated sites. Paludiied sites are dominated by pine stands with sedge and Sphagnum. The average contour of the plant communities is 150 m. REFERENCES GrШЦЭsОЯ, .N. 2000. . . : ДLКЧНsМКЩО ОМШХШРв ШП ЭКТРК ПШrОsЭs: ЭСОШrОЭТМКХ КЧН КЩЩХТОН КsЩОМЭsЖ. – PОЭrШгКЯШНsФ. KКrОХТКЧ RОsearch Center of Russian Academy of Sciences. 144 p. (in Russian). GrШЦЭsОЯ, .N. 2008. . . ДBКsТМ ХКЧНsМКЩО ОМШХШРв ШП RЮssТК’s EЮrШЩОКЧ ЭКТРК ПШrОsЭsЖ. PОЭrШгКЯШНsФ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП Russian Academy of Sciences. 226 p. (in Russian). GrШЦЭsОЯ, A.N. (ОН.) 2013. . . ( .). : , , ДSОХФК ХКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ МСКrКМЭОrТsЭТМs, LКЧН UsО, CШЧsОrЯКЭТШЧЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 179 Щ. (IЧ RЮssТКЧ). VШХФШЯ, .D., GrШЦЭsОЯ, .N., ErЮФШЯ, G.V., KКrКЯКОЯ, V.N., KШХШЦвЭsОЯ, V. ., KЮrСТЧОЧ, В.P., LКФ, G.T., PвгСТЧ,. .F., SКгШЧШЯ, S.V. &SСОХОФСШЯ, . . 1990. . ., . ., . ., . ., . ., . ., . ., . . ., . ., . . ( ) ДLКЧНsМКЩО ОМШsвsЭОЦs ШП аОsЭОrЧ ЦТН-ЭКТРК: sЭrЮМЭЮrО КЧН НвЧКЦТМs. PОЭrШгКЯШНsФЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. 284 Щ. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 107 Fig .2 Forest structure in a mildly paludiied denudation-tectonic ridge terrain dominated by pine habitats (fragment). Fig. 3 Forest structure in glacial hilly-ridge mid-paludiied terrain dominated by pine habitats (fragment). 108 Reports of the Finnish Environment Institute 40 | 2014 Fig. 4 Forest structure in lacustrine-glacial hilly mid-paludiied terrain dominated by pine stands (fragment). Fig. 5 Forest structure in mid-paludiied morainic plain terrain dominated by spruce habitats (fragment). Reports of the Finnish Environment Institute 40 | 2014 109 Fig. 6. Forest structure in aqueo-glacial topographically complex mildly paludiied terrain dominated by pine stands (fragment). Fig. 7 Forest structure in highly paludiied lacustrine-glacial plain terrain dominated by spruce habitats (fragment). 110 Reports of the Finnish Environment Institute 40 | 2014 2.3 The structure of forest land and forest stands in Zaonezhye Peninsula Boris Raevsky* and Nikolay Puteshov** * Directorate for Regional protected areas of the Republic of Karelia, 66 Rigachin St. 185005, Petrozavodsk, Karelia, Russia. Corresponding author Boris Raevsky. E-mail: oopt@karelia.ru ** Ministry of Nature Management and Environment of the Republic of Karelia, 2/24 Andropov St. 185035, Petrozavodsk, Karelia, Russia. E-mail: ecopetr@karelia.ru Introduction Zaonezhye Peninsula (Zaonezhye) is known both inside and outside of Russia as an exceptionally valuable natural and cultural territory. Currently there is a clear trend towards the intensiication of the exploitation of forest and mineral resources as well as increased recreational pressure in Karelia, particularly in Zaonezhye. Therefore, the creation of a protected area network, aiming at preserving the most valuable objects under different threats, becomes of paramount importance. At present there are 22 regional protected areas in the peninsula, covering 2500 ha. The largest among them is the Klim-gora landscape nature monument (approximately 600 ha). Kizhi federal zoological reserve (zakaznik), which covers 50 000 ha, is located southeast of the peninsula. The main objectives of this reserve are to preserve natural values of the Kizhi skerries and to protect nesting places of waterfowl (Figure 1). The Kizhi open-air museum and its buffer zone are within the boundaries of the reserve and they cover a large proportion of it. The open-air museum is characterized by landscapes that have been under a heavy human inluence. Results Forest ecosystems are the most dynamic components of natural landscapes due to their biological and ecological characteristics as well as their economic value. Therefore, forests require special protection. The establishment of a large-scale protected area on Zaonezhye is crucial for the conservation of forest communities; primarily pine forests, which are most valuable from ecological, biological and recreational point of view. In 2013, Karelian Research Center published a monograph which summarized research data concerning esker landscapes situated in the middle part of Zaonezhye Peninsula (Gromtsev 2013). The authors have used the results of the publication as scientiic arguments for the establishment of the Zaonezhye landscape reserve. In 2013 the NGO “SPOK” also developed arguments for the establishment of the Zaonezhye nature park (Documentations... 2013; see Figure 1). Reports of the Finnish Environment Institute 40 | 2014 111 According to modern knowledge, Zaonezhye is located within the Fennoscandian middle taiga subzone. Its area is divided into western and eastern parts that differ clearly in their landscape features. The transition zone between them divides two contrasting types of geographical landscapes in line with the villages of Velikaya Guba, Velikaya Niva and Shunga. Areas to the west of these villages are dominated by moderately paludiied denudation-tectonic esker landscapes; whereas areas to the east are dominated by moderately waterlogged lacustrine and lacustrine-glacial lowland landscapes. Pine habitats prevail in the west, while spruce habitats dominate in the east (Gromtsev 2013). The landscape reserve (LR), proposed by the Karelian Research Centre, covers a total area of 106 373 ha. It is located in its entirety within the boundaries of the former landscape type. On the contrary, the nature park (NP) proposed by the NGO “SPOK”, which covers 107 862 ha, lies mostly within the boundaries of the latter landscape type. Together these planned protected areas cover roughly two thirds of Zaonezhye Peninsula. According to the Ministry of nature management and environment of the Republic of Karelia (1/1/2012), forests cover 81,9% and 87,5% of the protected areas respectively. The planned landscape reserve and nature park share 25% of their territories and 22% of their forest areas. Comparative analysis of the structure of forest land (lesnoi fond in Russian) shows the level of anthropogenic transformation in the two protected areas. It also suggests that characteristics of intact forest communities are preserved mainly in pine stands. Analysis of the land categories of forest land in LR and NP (Table 1) shows that the proportion of forest areas is relatively high: 79,4% and 86,9% respectively. In the Karelian context, this suggests, irst and foremost, moderate or low paludiication of the territory. Wetlands cover no more than 5% of the area. Practically all of the forest areas are covered by forests (99,0% in LR and 96,4% in NP). At the same time, the proportion of forest plantations is higher in LR (19,7%) than in NP (13,4%). This suggests that artiicial reforestation has been widely used on the peninsula at least since the middle of the 20th century. Fig. 1. Protected areas of Zaonezhye peninsula. 112 Reports of the Finnish Environment Institute 40 | 2014 Table. 1. Distribution of different land categories of forest land (lesnoi fond) in the planned protected areas*. Land category Landscape reserve Nature park Area, ha Structure, % Area, ha Structure, % Total area of forest land (lesnoi fond) 87138 100 94422 100 Total forest area, including: 69227 79.4 (100) 82025 86.9 (100) Forest-covered areas 68520 78.6 (99.0) 79067 83.7 (96.4) Forest plantations 13518 15.5 (19.7) 10998 11.6 (13.4) Total of bare forest land, including: 705 0.8 (100) 2956 3.1 (100) Open plantations 147 0.2 (20.9) 964 1.0 (32.6) Forest nurseries and seed orchards 99 0.1 (14.0) – – Open stands – – – – Fire sites 3 – 7 – Dead plantations 9 – 30 0.03 (1.0) Felling areas 447 0.5(63.4) 1955 2.1 (66.1) Forest clearings and waste- – land – – – Total of non-forest areas, including: 17912 20.6 (100) 12397 13.1 (100) Arable land – – – – Hay meadows 88 0.1 (0.5) 270 0.3 (2.2) Pastures – – – – Water area 12873 14.8 (71.9) 8246 8.7 (66.5) Gardens and berry ields – – – – Roads and clearings 243 0.3 (1.4) 281 0.3 (2.3) Buildings – – 43 – Wetlands 4355 5.0 (24.3) 3295 3.5 (26.6) Sand – – – – Other non-forest areas 353 0.4 (2.0) 264 0.3 (2.1) * The proportion of sub-categories within the land categories of forest land is shown in parentheses. Felling areas predominate the structure of bare forest land in both territories (63,4 and 66,1%) but their area is four times larger in NP than in LR. Felling areas also occupy a considerable proportion of bare forest land within the total forest land. The proportion of non-forest areas is less than 21% of the total forest land in the examined protected areas. Water areas and wetlands dominate their structure. The proportion of water objects in the total structure of the forest land roughly corresponds to the average igure in Karelia (approximately 10%), whereas the proportion of mires is considerably lower than average for the paludiied forest land of Karelia (23,7%). In general, structural analysis of the forest area indicates relatively extensive exploitation and anthropogenic transformation of the nature park in comparison with the landscape reserve. Reports of the Finnish Environment Institute 40 | 2014 113 Forests dominated by coniferous species cover 68,4% and 59,3% of forest-covered areas in LR and NP respectively (Table 2). Table 2. Distribution of forest-covered areas, based on the dominant species. Landscape reserve Nature park Dominant species Area, ha % Area, ha % Pine (Pinus sylvestris) 28693 41.9 21188 26.8 Spruce (Picea x fennica) 18105 26.4 25678 32.5 Larch (Larix sibirica) 33 0.05 41 0.1 Birch (Betula spp.) 18308 26.7 23962 30.3 Speckled alder (Alnus incana) 1264 1.8 3427 4.3 Black alder (Alnus glutinosa) – – 66 0.1 Aspen (Populus tremula) 2117 3.1 4705 6.0 Total 68520 100.0 79067 100.0 A high proportion (90% or more) of forests, dominated by coniferous species, is typical for intact taiga forests. A higher proportion of deciduous stands, dominated by birch, alder and aspen, indicate both moderate human inluence and relatively high soil fertility in the area. Pine dominates in the landscape reserve while spruce dominates in the nature park, which relects the characteristics of the aforementioned landscapes. Siberian larch is present in forest plantations. Next, we will use a set of parameters to examine the distribution of forest stands in the main coniferous structures. Coniferous stands show a particular age class distribution (Table 3). For coniferous species, each age class equals 20 years. Approximately 68% of coniferous stands in LR and 51% of pine and spruce stands in NP fall into age classes I-V. For intact taiga forests, the opposite is true. In these forests, more than 70% of forest stands belong to age classes VIII-XII. In the planned protected areas, the proportion of stands in these age classes is no more than 17%. Thus, the distribution of age classes is a certain sign of considerable anthropogenic transformation of Zaonezhye forests. Table 3. Age class distribution of coniferous forests. 114 Age class Landscape reserve Nature park Pine, ha % Spruce, ha % Pine, ha % Spruce, ha % 1 925.7 3.2 1240.9 6.8 411.6 2.1 4389.8 18.6 2 3950.2 13.9 5493.6 30.0 842.7 4.3 4334.9 18.3 3 4903.5 17.2 1220.5 6.7 2065.2 10.6 184.2 0.8 4 4749.3 16.7 2311.5 12.6 2442.8 12.5 628.7 2.7 5 4740.8 16.6 2203.4 12.0 3828 19.6 2868.6 12.1 6 2671.7 9.4 1887.9 10.3 3731.5 19.1 3839.1 16.2 7 2349.6 8.2 1637.8 8.9 2965.8 15.2 3944.9 16.7 8 2104.3 7.4 1293.2 7.1 1807.7 9.2 2138.8 9.0 9 1678.9 5.9 952 5.2 1035.7 5.3 1276.8 5.4 10 313.8 1.1 96.9 0.5 387.5 2.0 44.6 0.2 11 76.1 0.3 – – 34.6 0.2 – – Reports of the Finnish Environment Institute 40 | 2014 12 41.6 0.1 – – – – – – TOTAL 28505.5 100.0 18337.7 100 19553.1 100.0 23650.4 100.0 According to species or group of species dominating either within the ground cover layer or in the undergrowth, different forest types are being distinguished (Table 4). Forest type is a site in the forest which is characterized by uniform forest-growing conditions, similar species composition and ground cover and which demands the same silvicultural methods (Sukachev & Zonn 1961). Table 4. Forest types that are common in pine dominated forests of Zaonezhye peninsula. Forest type Indicatory species Cladonia lichens of genus Cladonia spp. Rocky Cladoniaceae spp. and mosses on outcrops of cliffs Vaccinium Vaccinium vitis-idaea Myrtillus Vaccinium myrtillus Oxalis Oxalis acetosella Long mosses Polytrichum spp. Herbal on bogs Various herbs in waterlogged forests Meadowsweet Filipendula ulmaria Sedge-Sphagnum Cyperaceae spp. and Sphagnum spp. Sphagnum Sphagnum spp. Ledum Ledum palustre The ecological spectrum of coniferous forests in Zaonezhye seems relatively normal. Here, coniferous forests are represented by seven main forest types, as well as a separate type of drained stands (Table 5.) Table 5. Distribution of coniferous forests by forest type. Forest type Landscape reserve Nature park Pine, ha % Spruce, ha Cladonia 676 2.4 – – 379 1.8 – – Vaccinium 3576 12.5 4 0.02 2608 12.3 46 0.2 Myrtillus 16700 58.2 12036 66.5 7147 33.7 16420 63.9 Oxalis 2888 10.1 4598 25.4 3376 15.9 5820 22.7 Long mosseses 1142 4.0 1324 7.3 746 3.5 2002 7.8 Herbal on bogs 35 0.1 47 0.3 80 0.4 178 0.7 Sphagnum 3507 12.2 81 0.4 6220 29.4 1212 4.7 Drained stands 170 0.6 14 0.1 633 3.0 2 0.01 TOTAL 28694 100 18104 100 21189 100 25680 100 % Pine, ha % Spruce, ha % Normally spruce forests are dominated by the Myrtillus type. In forest inventories, these types are referred to as mixed-herb Myrtillus, Myrtillus and moist Myrtillus forests. It is commonly known that during natural reforestation spruce is a more demanding species. Therefore, it occupies relatively homogenous habitats with the most favourable conditions. Meanwhile, pine is ecologically more lexible and dominates less favourable habitats with more diverse habitat conditions. The characteristics of Reports of the Finnish Environment Institute 40 | 2014 115 Zaonezhye forests include the relatively unvaried typological spectrum of pine and spruce. Also, the proportion of Myrtillus pine forests in denudation-tectonic landscapes is high – nearly as high as the proportion of spruce forests - indicating that there are relatively highly fertile mineral soils in the landscape reserve. The proportion of waterlogged forests (49.4%) within the nature park is twice as large as within the landscape reserve (25.0%), which is typical for lacustrine-glacial lowland landscapes. The forests of the peninsula show a distinctive distribution pattern of site quality classes (Table 5). The productivity of coniferous stands varies from classes I to Va and Vb, which is relatively common in Karelia. Characteristically, a particularly high proportion of pine stands belong to class III. These stands constitute nearly half of all pine forests in the landscape reserve. Pine stands cover 1.7 times larger area than spruce stands. Table 6. Distribution of coniferous forests by site quality class (bonitet). Site class Landscape reserve Nature park Pine, ha % Spruce, ha I 58 0.2 – – 114 0.5 3 0.01 II 3422 11.9 491 2.7 1579 7.5 763 3.0 III 13229 46.1 7902 43.7 8637 40.8 12085 47.1 IV 6167 21.5 7432 41.1 3244 15.3 8081 31.5 V 4425 15.4 2280 12.6 4006 18.9 4507 17.6 Va 1392 4.9 – – 3520 16.6 231 0.9 Vb – – – – 89 0.4 8 0.03 TOTAL 28693 100 18105 100 21189 100 25678 100 Average index III.5 – III.6 – IV.0 – III.7 – % Pine, ha % Spruce, ha % Uneven-aged forest stands are a typical feature of primeval forests in the taiga zone of the European part of Russia. Normally these forest stands dominate coniferous stand structures of intact forests. In general, uneven-aged forest stands provide a dynamic balance between growth and dieback processes. Forest inventory data is crucial for detecting primeval forests in existing and planned protected areas as well as calculating certain parameters of their natural age structure. We have used the classiication of S. Zyabchenko (1984) as the methodical basis for analyzing the pine forests of Zaonezhye. We have only analyzed pine-dominated stands in age classes VII and higher. A forest stand is considered absolutely uneven-aged when the following conditions are met: a) there is a minimum of two generations of pine; b) the growing volume of the structure is no more than 40%; c) the oldest generation is at least 180 years old; d) there should be a difference of more than three age classes between generations. In younger age classes, as well as when the proportion of growing volume in one generation is at least 50%, forests are considered relatively uneven-aged. If there has been only one generation of pine, the stand is considered potentially even-aged. The results of the classiication of pine stands in the landscape reserve and the nature park are presented in Tables 6, 7 and 8. We have used the following abbreviations: P – pine; S – spruce; L – larch; B – birch; As – aspen; Ali – speckled alder (Alnus incana); Alg – black alder (Alnus glutinosa). The ages of the elements are described in subscript. 116 Reports of the Finnish Environment Institute 40 | 2014 Table 7. Distribution of pine stands in the Zaonezhye landscape reserve by age structure, forest type and site quality class. № Forest type Site class Composition and structure (in tenth parts of growing volume) Growing volume, m3/ha Total area, ha % Absolutely uneven-aged 1 Myrtillus III 3P190 2P 90 3S170 1B901As90 270 53.0 80.5 2 Sedge-Sphagnum V 3,7P190 2,7P100 1,3S140 2,3B70 84 5.7 8.7 11 Long mosses V 4СP190 2P 90 2S170 2B 80 120 3.2 4.9 12 Ledum V 4P190 3P 90 1S170 2B70 111 3.9 5.9 65.8 100.0 TOTAL Relatively uneven-aged 1 Myrtillus II 4P130 3P110 2B 80 1As80 330 2.1 0.1 2 Myrtillus III 5,3P170 2,2P 90 1S130 1,5B90/As90 253 332.8 18.4 3 Myrtillus IV 5,7P170 2P70 2S70 2B701As70 183 234.8 13.0 4 Myrtillus V 3P130 2,9P100 0,5S90 0,9B90/As90 155 35.0 1.9 3 Vaccinium IV 5,7P150 3,1P 90 0,8S120 0,4B 80/As80 194 142.5 7.9 4 Vaccinium V 5,8P160 3,7P100 0,5B90/As90/S90 133 154.5 8.6 5 Rocky V 6,5P170 2,8P 90 0,7S90/B 80/As80 72,4 126 7.0 6 Rocky Va 6,4P160 2,9P 90 0,7S150/B90 67 27.5 1.5 7 Sedge-Sphagnum V 6,5P170 3P100 0,3S130 0,2B70 113 227.6 12.6 8 Sedge-Sphagnum Vа 4,3P170 5,3P110 0,4B 80/S70 83 179.1 9.9 9 Long mosses IV 5P150 4P 90 1B 40 111 10.1 0.6 10 Ledum V 6,3P170 3,2P110 0,4S170 0,1B 80 121 66.6 3.7 11 Ledum Vа 5P150 5P70 42 3.7 0.2 12 Sphagnum V 6,8P170 2,6P 90 0,6S110/B70 77 87.5 4.8 13 Sphagnum Vа 6,9P160 3P110 0,1S110/B 80 76 143 7.9 1805.8 100.0 TOTAL Potentially even-aged 1 Herbal on bogs II 4P130 1,5S110 4,5B90/As90 345 17.1 0.4 2 Herbal on bogs III 5,4P1301,5S120 3,1B90/As90 320 210.5 5.2 3 Oxalis II 5P130 3S130 1,5B90/As90 0,5S60 331 5.5 0.1 4 Oxalis III 5,1P130 2,5S110 2,3B90/As90 0,8S90 318 63 1.6 5 Oxalis IV 5,7P130 2P110 2,3B90/As90 264 70.6 1.7 6 Myrtillus II 3P130 3S110 2As902B90 362 4.7 0.1 7 Myrtillus III 5,9P140 2,3S130 1,8B90/As90 278 951.4 23.5 8 Myrtillus IV 6,2P140 2,1S110 1,7B90/As90 190 370 9.2 9 Vaccinium III 7P130 1S90 2B90/As90 185 13.9 0.3 10 Vaccinium IV 8,1P130 1S90 1B70/As70 178 397 9.8 11 Vaccinium V 8,6P140 1S90 0,4B 80/As80 141 319 7.9 12 Rocky V 9,5P140 0,5S140/B 80 99 81.9 2.0 13 Rocky Va 9P140 1S150/B60 71 23.5 0.6 14 Meadowsweet IV 5P140 2S130 3B90 186 8.7 0.2 15 Meadowsweet V 5,5P1401,5S140 2,5B70 128 7 0.2 Reports of the Finnish Environment Institute 40 | 2014 117 16 Sedge-Sphagnum V 6,7P160 2S150 1,3B 80 131 482 11.9 17 Sedge-Sphagnum Va 8,3P150 1S130 0,7B90 65 34.7 0.9 18 Long mosses IV 5,8P140 2,6S140 1,6B 80 142 123 3.0 19 Long mosses V 5P150 2,7S140 2,3B90 121 148 3.7 20 Ledum V 9,5P150 0,4S150 0,1B90 143 124 3.1 21 Ledum Va 9P1401S110 +B90 95 31 0.8 22 Sphagnum V 9,2P140 0,5S150 0,3B90 94 167 4.1 23 Sphagnum Va 7,5P140 1,5S140 1B90 65 390 9.6 4043.5 100.0 TOTAL Table 8. Distribution of pine stands in the Zaonezhye nature reserve by age structure, forest type and site quality class. № Forest type Site class Composition and structure (in tenth parts of growing volume) Growing volume m3/ ha Total area, ha % Absolutely uneven-aged 1 Myrtillus III 3P190 2P 90 3S170 1B901As90 270 53.0 73.8 4 Vaccinium V 4P 200 2P130 2S190 2As110 129 6.8 9.5 8 Sedge-Sphagnum Va 4P190 4P 90 2B60+S150 71 12 16.7 71.8 100 TOTAL Relatively uneven-aged 1 Myrtillus III 5,7P180 2,3P100 2B90/As90 237 100.9 6.9 2 Myrtillus IV 5,8P170 2,8P120 1,4B90 226 135.5 9.3 3 Vaccinium IV 5,9P160 2,3P120 1S90 0,8B90/As90 204 259.1 17.7 4 Vaccinium V 6,5P190 2,5P120 1B100 156 84.7 5.8 5 Rocky V 8P150 1,3S140 0,7B90 133 61.3 4.2 6 Rocky Va 9P130 1S130+B 80 133 12 0.8 Oxalis III 3P170 2P120 2,5S1302,5B90 215 31.0 2.1 7 Oxalis IV 5,8P180 2,6P100 1,6S100/B90 218 34.1 14.1 8 Herbal on bogs III 6P130 2P180 1B90 1As90 244 14 1.0 9 Meadowsweet V 5P150 2P 210 3B100 168 6.2 0.4 10 Sedge-Sphagnum V 5,7P160 3P 90 1,3B 80 +S130 99 166.1 11.3 11 Sedge-Sphagnum Va 5,7P1503,5P 90 0,7B 80 0,1S150 71 269.4 18.4 12 Long mosses IV 3P170 2 P120 2,5S1302B90 0,5Ali100 169 12.7 0.9 13 Ledum V 7P190 3P105 94 6.8 0.5 13 Sphagnum V 5,7P160 2,7P130 1,6S130/B 80 85 31.7 2.2 14 Sphagnum Va 6P140 4P 90 +S130 53 66.4 4.5 1464.3 100 TOTAL Potentially even-aged 1 Herbal on bogs III 6P130 2,1S120 1,9B90/As90 268 165.6 3.2 2 Oxalis II 3P130 3S130 3As90 1B90 336 2.6 0.1 3 Oxalis III 5,5P150 2S140 2,5B90/As90 257 144.9 2.8 4 Oxalis IV 6,5P160 2,2S100 1,3B90 236 277.9 5.4 5 Myrtillus II 3P130 3S110 2As90 2B90 362 4.7 0.1 118 Reports of the Finnish Environment Institute 40 | 2014 6 Myrtillus III 5,4P140 2,3S130 2,3B90/As90 266 1088.3 21.0 7 Myrtillus IV 6,7P150 2,1S140 1,2B90/As90 213 97.7 1.9 8 Vaccinium III 7,3P160 1,5S130 1,2B90 264 23.6 0.5 9 Vaccinium IV 8,3P130 1,1S120 0,6S 80/B 80 201 297 5.7 10 Vaccinium V 9,1P140 0,7S110 0,3B 80/As80 176 608.4 11.7 11 Rocky V 8P150 1,3S140 0,7B90 133 61.3 1.2 12 Rocky Va 9P130 1S130+B 80 133 12 0.2 13 Meadowsweet IV 4,7P140 1,7S130 3B90 0,6As90/Ali90 183 16.3 0.3 14 Sedge-Sphagnum V 6,1P140 2,2S130 1,6B 80 0,1Alg80 122 522.4 10.1 15 Sedge-Sphagnum Va 6,4P140 2,1S130 1,5B 80 79,4 1306.6 25.2 16 Long mosses IV 6P140 2,5S140 1,1B 80 0,4As90/Ali90 183 43.9 0.8 17 Long mosses V 6,4P150 2,2S140 1,3B90 0,1As75/Alg60 150 151.5 2.9 18 Ledum V 8,9P150 1,1S150/B90 113 41.8 0.8 19 Ledum Va 10P130 95 14 0.3 20 Sphagnum V 7,9P150 0,9S140 1,2B 80 93 79.5 1.5 21 Sphagnum Va 7,6P140 1,4S140 0,9B90 0,1Alg100 72 229.6 4.4 5189.6 100 TOTAL Table 9. The composition and structure of Zaonezhye pine stands, based on the type of age structure. Composition and structure (in tenth parts of growing volume) Average age class Growing volume, m3/ha Total area, ha % Potentially even-aged 6,7P140 1,8S110 1,5B 80/As80 7.5 184 4043.5 68.4 Absolutely uneven-aged 3,2P190 2,1P 90 2,7S170 2B90 10 237 65.8 1.1 Relatively uneven-aged 6P160 3,3P100 0,7S110/B90/As90 8 145 1805.8 30.5 5915.1 100 Type of age structure Landscape reserve TOTAL Nature park Potentially even-aged 6,4P140 2S110 1,6B90/As90/Ali90/ Alg90 7.7 168 5189.6 77.2 Absolutely uneven-aged 3,3P190 2,3P 90 2,7S150 1,7Ali110 10 223 71.8 1.1 Relatively uneven-aged 5,8P160 3P110 0,5S130 0,7B 80 8.5 158 1464.3 21.7 6725.7 100 TOTAL After analysing Tables 7, 8 and 9, we have come to the following conclusion: Absolutely uneven-aged stands represent the smallest share, amounting to only 1,1% of all types of age structures in both the landscape reserve and the nature park. Consequently, these forest-covered areas are least preserved from anthropogenic transformation. The absolutely uneven-aged Myrtillus pine stands of III site quality class indicated in Tables 6 and 7 are located in the forest compartment (kvartal) 117 of the Velikaya Guba forest district (lesnichestvo). The proportion of relatively uneven-aged stands is Reports of the Finnish Environment Institute 40 | 2014 119 30,5% in the landscape reserve and 21.7% in the nature park. Potentially even-aged pine stands dominate both planned protected areas, totaling 68.4% of the landscape reserve and 77.2% of the nature park. The formation of potentially even-aged pine stands depends on a set of natural and anthropogenic factors. Natural factors include large ires and vast windfalls. The natural reforestation of potentially even-aged pine stands is expected within 20–40 years after these catastrophic events. The main anthropogenic factor is intensive felling, namely clear cutting, followed by natural or artiicial reforestation. In the two planned protected areas, anthropogenic factors play a bigger part due to the long history of agriculture and high population density in Zaonezhye. According to Zyabchenko (1984), relatively uneven-aged pine stands appear after 60–80 years of natural afforestation of pine stands in open areas, namely ire sites. Alternatively, they can be formed under the inluence of intensive selective logging. The latter is true for Zaonezhye. On the whole, anthropogenic transformation is more pronounced in the planned nature park than in the landscape reserve. After analyzing Tables 6 and 7, we have come to the conclusion that the proportion of pine in the stand structure increases when the site quality class decreases. The biggest proportions of spruce are typical for highly productive, potentially even-aged pine stands of the Oxalis and Myrtillus types. Even though the two planned protected areas are located in different geographical landscapes their pine stands are characterized by similar structures (Table 9). According to our analyses, the pine-dominated boreal forests of Zaonezhye Peninsula have been highly productive in the past. These forests have supplied quality construction material for the outstanding monuments of wooden architecture, for which Zaonezhye is famous. Despite the extent of anthropogenic transformation of ecosystems, there are still small areas of old-growth pine stands of high conservation and recreational value. As shown in Figures 2 and 3, nearly all of these areas are already located within protective forests. Average indicators for the planned landscape reserve and nature park are shown in Table 10. At present, a signiicant proportion of coniferous forests in the planned protected areas (LR – 50.5% and NP – 39.7%) are located in protective forests where clear cutting is prohibited. In general, the average indicators for these forests are higher than for commercial forests. There is a special interest in the forest compartments (kvartal) of the Tolvuya and Velikaya Niva forest districts (lesnichestvo), which are included in both the landscape reserve and the nature park. Table 10. Average indicators for coniferous forests in the planned landscape reserve and nature park, based on inventories. Area, ha Average Relative Growing Average composition age, Site class stand volume, and structure years density m3/ha Pine 15443.2 96 III.5 0.67 181 6P2B1S1As+L,Ali,Alg Spruce 8184.8 93 III.7 0.70 173 5P2P2B1As+Ali,Alg Larch 16.1 36 III.9 0.81 109 5B3L1S1P TOTAL 23644.1 95 III.6 0.68 178 5P2S2B1As+L,Ali,Alg 13249.8 72 III.5 0.66 131 5P3B1S1As+Ali,Alg Dominant species Landscape reserve Protective forests Commercial forests Pine 120 Reports of the Finnish Environment Institute 40 | 2014 Spruce 9919.8 63 III.6 0.70 135 5S2B1P1As1Ali+Alg Larch 16.4 47 III.0 0.74 144 4L3P2B1S TOTAL 23186.0 68 III.6 0.68 133 4P3S2B1As+L, Ali,Alg Pine 10860.0 106 III.5 0.69 198 6P2B1S1As+Ali,Alg Spruce 7772.2 110 III.4 0.72 217 6S2B1P1As+Ali,Alg Larch 1.0 46 II.0 0.70 170 5B3L1P1S TOTAL 18633.2 108 III.5 0.70 206 4P3S2B1As+L,Ali,Alg Pine 10328.3 96 IV.4 0.61 128 6P2B1S1As+Ali,Alg Spruce 17906.0 76 III.8 0.67 147 6S2B1P1As+Ali,Alg Larch 40.0 42 II.5 0.80 141 4B3L1S1P1As TOTAL 28274.3 83 IV.0 0.65 140 4S3P2B1As+L,Ali,Alg Nature park Protective forests Commercial forests On the whole, when it comes to protecting forest ecosystems, the two proposed protected areas complement each other to some extent. However, the denudation-tectonic landscape of the landscape reserve seems more promising in terms of structure. Following the creation of a strict protected area (where cutting of dead and damaged stands is allowed only under exceptional circumstances), we would expect over 120-year-old pine stands to acquire features of intact pine forests within the next 50 years. REFERENCES ДDШМЮЦОЧЭКЭТШЧ ШП ЭСО МШЦЩХОб ОМШХШРТМКХ ТЧЯОЧЭШrв УЮsЭТПвТЧР ОsЭКЛХТsСЦОЧЭ ШП ЭСО ГКШЧОгСsФв sЭКЭО ЧКЭЮrО ЩКrФЖ 2013. , « » NGO “SPOK”. – PОЭrШгКЯШНsФ.108 Щ. (IЧ RЮssТКЧ). GrШЦЭsОЯ, A.N. (ОН.) 2013. . . (Щ .). : , .ДSОХФК ХКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ МСКrКМЭОrТsЭТМs, LКЧН UsО, CШЧsОrЯКЭТШЧЖ. – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 179 Щ. (IЧ RЮssТКЧ). SЮФКМСОЯ, V.N., ГШЧЧ, S.V. 1961. . ., . . . ДMОЭСШНТМКХ ТЧsЭrЮМЭТШЧs ПШr sЭЮНвТЧР ШП ПШrОsЭ ЭвЩОsЖ. – USSR AМКНОЦв ШП SМТОЧМОs PЮЛХТМКЭТШЧs. MШsМШа. 144 Щ. ГвКЛМСОЧФШ, S. S. 1984. . . . PТЧО ПШrОsЭs ШП ЭСО EЮrШЩОКЧ NШrЭС. – LОЧТЧРrКН, “NКЮФК” LОЧТЧРrКН ЛrКЧМС 248 Щ. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 121 Fig. 2. Spatial distribution of old-growth (older than 120 years) pine-dominated forests in planned Zaonezhye Nature (landscape) Reserve, northern part of Zaonezhye Peninsula. 122 Reports of the Finnish Environment Institute 40 | 2014 Fig. 3. Spatial distribution of old-growth (older than 120 years) pine-dominated forests in planned Zaonezhye Nature Park, southeastern part of Zaonezhye Peninsula. Reports of the Finnish Environment Institute 40 | 2014 123 Old growth spruce-dominated forest in Zaonezhye (Photo Boris Rayevsky). 124 Reports of the Finnish Environment Institute 40 | 2014 2.4 Forest structures and human impact on Zaonezhye Peninsula: a classiication and case studies Timo Kuuluvainen* and Olli-Pekka Tikkanen** * Department of Forest Sciences, University of Helsinki, PO Box 27, 00014 Helsingin yliopisto, Finland. ** School of Forest Sciences, University of Eastern Finland, PO Box 111, 80101 Joensuu, Finland Corresponding authors Timo Kuuluvainen & Olli-Pekka Tikkanen E-mail: Timo.Kuuluvainen@helsinki.i Tel: + 358504486146 E-mail: Olli-Pekka.Tikkanen@uef.i Tel: +358469210746 Introduction Human population history and past land use has a profound and diverse effect on current forest landscapes and forest structures within them (Brumelis et al. 2011). In eastern Fennoscandia, transformation of forests to agricultural land and use of wood for construction and heating has created open cultural landscapes in surroundings of villages (Huttunen 1980, Tikkanen et al. 2014). In Karelia, the landscapes around the old villages are now, after their abandonment, recovering towards more natural stage (Tikkanen et al. 2014, Tikkanen & Chernyakova 2014). Further away from the villages, slash and burn agriculture and other human activities have increased ire frequency, which has favored presence of pine and deciduous trees in forest landscapes and suppressed spruce (Huttunen 1980, Tikkanen & Chernyakova 2014). As a result, we can ind a gradient of human impact with increasing naturalness as a function of increasing distance from villages (Tikkanen et al. 2014). Zaonezhye peninsula has a long population history and it is has historically been more densely populated than many other areas in the Karelian Republic. In addition, industrial forestry has changed forest structure in many parts of the peninsula (see 2.3. in this volume). High intensity in forest use is known to lead to declining naturalness of forest structures including the amount and diversity of dead wood (Rouvinen et al. 2002). This is detrimental to many rare forest species, which are found in pristine forests and require abundance, diversity and long continuum of dead wood (Martikainen et al. 2000, Similä et al. 2003, Penttilä et al. 2004, Junninen et al. 2006). From the point of view of conservation of biodiversity and planning of conservation area networks it is critically important to ask 1) what effect has past human impact on modern day forest Reports of the Finnish Environment Institute 40 | 2014 125 structures and, especially, 2) can we still found primeval forests, which are potential habitats of rare species in Zaonezhye peninsula. Methods For this study, ield inventories and forest structure measurements were carried out in August 2013 using the circular plot method. Each inventory plot had a radius of 15 m (0.07 ha). Plots were chosen subjectively to be representative of the studied forests area (see map, Fig. 1). All living and dead trees with a diameter of more than 10 cm were measured. A vertex device was used to examine trees along the plot borders to accurately deine the plot size. Results and discussion According to the ield observations and inventories, forests of Zaonezhye Peninsula can be roughly divided into three classes: (A) high-quality primeval forests with negligible human impact, (B) forests with high conservation potential, which are no longer utilized and which are rapidly developing natural values and (C) successional, mostly deciduous, forests growing on abandoned ields or forests pastures. These forests retain important natural values as well due to a large amount of living and dead deciduous trees, as well as the natural succession that has occurred here for dozens of years. Examples of structure, tree volume and species composition in the three classes of forests are given in Tables 1–3 and in Figures 2–5. However, we would like to emphasize that although we made an effort to select representative examples, there is considerable variation in forest structures and composition within these broad classes, which is not fully relected in these examples. Map 1 Fig. 1. Locations of the sample plots in Table 1. A1 A2 C3 Lipovitsa B1 B2 Map 2 A3 C1 B3 C2 Tambitsa 126 Reports of the Finnish Environment Institute 40 | 2014 The irst group (class A) is high-quality primeval forests. These forests exhibit all the qualities of old, intact natural forests, including diverse tree species composition, big trees and complex stand structure as well as a large amount, diversity and continuity of dead wood. There are very few signs of human inluence, if any. Examples of structural features of these forests of the highest conservation priority are given in Table 1 and in Figures 2 and 3. At these sites the amount of dead wood ranged from 94 to 248 m3/ha and living tree volumes from 113 to 539 m3/ha. Not surprisingly, these forests were found from the most remote sites, which were visited; several kilometers from the closest larger settlements. Table 1. Examples of tree volumes (m3/ha) in three plots of the class A primeval forests. Tree volumes are presented for different tree species as well as living and dead trees separately. Coordinates for the plots are given in parenthesis (latitude/longitude). See Figure 1 for plot locations. Plot Pinus Picea Betula Populus Sorbus Alnus Total 110.5 - 54.2 - 59.8 225.9 A1(62°10’33.11”,35°3’39.88”) - Living 1.4 - Dead 24.7 66.4 7.4 13.1 - 15.7 127.3 - Total 26.1 176.9 7.4 67.4 - 75.6 353.2 A2 (62°10’15.85”, 35° 3’32.15”) - Living 8.7 103.8 - - - - 112.6 - Dead - 222.8 24.7 - - - 247.5 - Total 8.7 327.6 24.7 - - - 360.1 150.5 52.6 335.5 - - 538.5 A3 (62°17’17.93”, 35°33’53.45”) - Living - - Dead - 79.7 - 14.0 - - 93.7 -Total - 230.2 52.6 349.5 - - 632.3 Fig. 2. Primeval forest with a signiicant amount of large aspens in plot A1 (see Table 1) (Photo Timo Kuuluvainen). Reports of the Finnish Environment Institute 40 | 2014 127 Fig. 3. Primeval forests in plot A2 (see Table 1). In this plot we found the rare fungi species Pycnoporellus alboluteus (Photo Timo Kuuluvainen). The second group (class B) is forests that have been utilized in the past for selective cutting, slash-and-burn cultivation or forest pastures. However, after the cessation of human activities, these forests have developed for dozens of years under natural processes. Therefore, they are rapidly regaining natural structures and they already contain important features of natural forests, such as large trees, layered canopies and a rapidly increasing amount of coarse dead wood. These forests, although still showing signs of past human utilization, can still be considered as forests of high conservation potential. This is the case especially when they are located close to class A forests of the highest conservation priority. Together class A and B forests can form more representative and functional conservation areas. Examples of the composition of forests with high conservation potential are given in Table 2 and in Figure 4. In the study plots, the amount of dead wood ranged from 71 to 193 m3/ha and living tree volumes from 180 to 395 m3/ha. In Finland, these quantities of coarse woody debris has been found suficient to support very high number of species depended on dead wood (Martikainen et al. 2000, Similä et al. 2003, Penttilä et al. 2004, Junninen et al. 2006). Table 2. Examples of tree volumes (m3/ha) in three plots of the class B forests with high conservation potential. Tree volumes are presented for different tree species as well as living and dead trees separately. Coordinates for the plots are given in parenthesis (latitude/longitude). See Figure 1 for plot locations. Plot Pinus Picea Betula Populus Sorbus Alnus Total 109.3 13.6 - - - 180.9 B1 (62° 6'20.58", 35° 3'19.98") - Living 57.9 - Dead 25.8 167.7 - - - - 193.4 - Total 83.7 277.0 13.6 - - - 374.3 B2 (62° 6'15.45", 35° 2'11.61") - Living 10.6 152.9 20.9 - - - 184.4 - Dead - 80.0 - - - - 80.0 - Total 10.6 232.8 20.9 - - - 264.4 259.6 7.5 127.6 - - 394.7 B2 (62°15'15.91", 35°35'48.08") - Living 128 - - Dead - 47.1 20.2 2.9 0.8 - 71.0 - Total - 306.7 27.7 130.5 0.8 - 465.7 Reports of the Finnish Environment Institute 40 | 2014 Fig. 4. An example of forest with high conservation potential that has clear signs of past human use but also rapidly developing natural values, such as coarse woody debris (Photo Timo Kuuluvainen). The forests of the third group (class C) are typically located near old, abandoned villages. These forests have been under intensive human inluence but are now, after the cessation of human activities, in the early or middle stages of natural forest succession. These are former ields, slash-and-burn sites or pastures near abandoned villages. These forests vary greatly in structure and composition, relecting different histories of land use as well as the length of time since the area has last been affected by human activities. These successional forests include dense self-thinning alder stands and mixed deciduous stands with alder, birch and (often large) aspen, sometimes spruce in the undergrowth. There are also spruce-dominated stands among the successional forests. These forests provide important habitats for species thriving on living and dead deciduous trees. Examples of the structure and composition of forests with high conservation potential are given in Table 3 and in Figure 5. Even in these secondary forests, the amount of dead wood was relatively high compared to that of intensively managed forests of western Fennoscandia (Fridman & Walheim 2000, Ihalainen & Mäkelä 2009). Table 3. Examples of tree volumes (m3/ha) in three plots of the class C forests, characterized by intensive human inluence in the past. Tree volumes are presented for different tree species as well as living and dead trees separately. Coordinates for the plots are given in parenthesis (latitude/longitude). See Figure 1 for plot locations. Plot Pinus Picea Betula Populus Sorbus Alnus Total 175.0 82.8 - - 1.0 258.8 C1 (62°14'59.28", 35°27'22.18") - Living 12.1 - Dead - 42.0 23.3 - - - 65.3 - Total 12.1 217.0 106.1 - - 1.0 324.1 C2 (62°14'38.37", 35°29'35.54") - Living - 132.4 95.9 78.4 0.3 - 306.9 - Dead - 35.6 3.6 94.2 1.2 - 134.7 - Total - 168.0 99.5 172.5 1.6 - 441.6 137.4 99.8 20.4 0.3 - 359.6 C3 (62° 8'24.90", 34°56'29.94") - Living 101.5 - Dead - 2.6 10.0 - - - 12.6 - Total 101.5 140.0 109.8 20.4 0–3 - 372.2 Reports of the Finnish Environment Institute 40 | 2014 129 Fig. 5. An example of a successional, deciduous (class C) forest, developing on an abandoned ield (Photo Timo Kuuluvainen). Overall, we conclude that the past human impact on the current forest structures on the Zaonezhye peninsula can be clearly seen, but also primeval forests of negligible human impact can be found in more remote locations. The cessation of major human inluence some dozens of years ago have led to large scale recovery and restoration of natural forest features in many areas. This together with the occurrence of primeval forests of highest conservation priority and culturally modiied habitats, opens up promising prospects for designing eficient forest conservation area networks for protection of biodiversity on the Zaonezhye peninsula. REFERENCES BrЮЦОХТs, G., JШЧssШЧ, B.G., KШЮФТ, J., KЮЮХЮЯКТЧОЧ, T. & SСШrШСШЯК, E. 2011. FШrОsЭ ЧКЭЮrКХЧОss ТЧ ЧШrЭСОrЧ EЮrШЩО: ЩОrsЩОМЭТЯОs ШЧ ЩrШМОssОs, sЭrЮМЭЮrОs КЧН sЩОМТОs НТЯОrsТЭв. – SТХЯК FОЧЧТМК 45(5): 807–821. FrТНЦКЧ, J. & АКХСОТЦ, M. 2000. AЦШЮЧЭ, sЭrЮМЭЮrО, КЧН НвЧКЦТМs ШП НОКН аШШН ШЧ ЦКЧКРОН ПШrОsЭХКЧН ТЧ SаОНОЧ. FШrОsЭ EМШХШРв КЧН MКЧКРОЦОЧЭ, 131: 23–36. HЮЭЭЮЧОЧ, P. 1980. EКrХв ХКЧН ЮsО, ОsЩОМТКХХв ЭСО sХКsС-КЧН-ЛЮrЧ МЮХЭТЯКЭТШЧ ТЧ ЭСО МШЦЦЮЧО ШП LКЦЦТ, sШЮЭСОrЧ FТЧХКЧН, ТЧЭОrЩrОЭОН ЦКТЧХв ЮsТЧР ЩШХХОЧ КЧН МСКrМШКХ КЧКХвsОs. – AМЭК BШЭКЧТМК FОЧЧТМК 113: 1–45. IСКХКТЧОЧ, A. & MтФОХт, H. 2009. KЮШХХООЧ ЩЮЮsЭШЧ Цттrт EЭОХт- УК PШСУШТs-SЮШЦОssК 2004–2007. – MОЭsтЭТОЭООЧ КТФКФКЮsФТrУК 1:35–56. (IЧ FТЧЧТsС). JЮЧЧТЧОЧ, K., SТЦТХт, M., KШЮФТ, J. & KШЭТrКЧЭК, H. 2006. AssОЦЛХКРОs ШП аШШН ТЧСКЛТЭТЧР ПЮЧРТ КХШЧР ЭСО РrКНТОЧЭs ШП sЮММОssТШЧ КЧН ЧКЭЮrКХЧОss ТЧ ЛШrОКХ ЩТЧО НШЦТЧКЭОН ПШrОsЭs ТЧ FОЧЧШsМКЧНТК. – EМШРrКЩСв 29: 75–83. MКrЭТФКТЧОЧ, P., SТТЭШЧОЧ, J., PЮЧЭЭТХК, P., KКТХК, L. & RКЮС, J. 2000. SЩОМТОs rТМСЧОss ШП CШХОШЩЭОrК ТЧ ЦКЭЮrО ЦКЧКРОН КЧН ШХН РrШаЭС ЛШrОКХ ПШrОsЭs ТЧ sШЮЭСОrЧ FТЧХКЧН. – BТШХШРТМКХ CШЧsОrЯКЭТШЧ 94: 199–209. PОЧЭЭТХт, R., SТТЭШЧОЧ, J. & KЮЮsТЧОЧ, M., 2004. PШХвЩШrО НТЯОrsТЭв ТЧ ЦКЧКРОН КЧН ШХН-РrШаЭС ЛШrОКХ PТМОК КЛТОs ПШrОsЭs ТЧ sШЮЭСОrЧ FТЧХКЧН. – BТШХШРТМКХ CШЧsОrЯКЭТШЧ 117: 271–283. RШЮЯТЧОЧ, S., KЮЮХЮЯКТЧОЧ, T. & KКrУКХКТЧОЧ, L. 2002. CШКrsО аШШНв НОЛrТs ТЧ ШХН PТЧЮs sвХЯОsЭrТs НШЦТЧКЭОН ПШrОsЭs КХШЧР К РОШРrКЩСТМ КЧН СЮЦКЧ ТЦЩКМЭ РrКНТОЧЭ ТЧ ЛШrОКХ FОЧЧШsМКЧНТК. – CКЧКНТКЧ JШЮrЧКХ ШП FШrОsЭ RОsОКrМС 32: 2184–2200. SТЦТХт, M., KШЮФТ, J. & MКrЭТФКТЧОЧ, P. 2003. SКЩrШбвХТМ ЛООЭХОs ТЧ ЦКЧКРОН КЧН sОЦТЧКЭЮrКХ SМШЭs ЩТЧО ПШrОsЭs: qЮКХТЭв ШП НОКН аШШН ЦКЭЭОrs. – FШrОsЭ EМШХШРв КЧН MКЧКРОЦОЧЭ 174: 365–381. TТФФКЧОЧ, O.-P. & CСОrЧвКФШЯК, I.A. 2014. PКsЭ СЮЦКЧ ЩШЩЮХКЭТШЧ СТsЭШrв КППОМЭs МЮrrОЧЭ ПШrОsЭ ХКЧНsМКЩО sЭrЮМЭЮrО ШП VШНХШгОrШ NКЭТШЧКХ PКrФ, NШrЭСаОsЭ RЮssТК. – SТХЯК FОЧЧТМК. TТФФКЧОЧ, O.-P., RЮШФШХКТЧОЧ, A. & HОТФФТХт, R. 2014. RОМШЯОrв ШП ЛШrОКХ ПШrОsЭ ЧОКr КЛКЧНШЧОН ЯТХХКРОs ТЧ аОsЭОrЧ АСТЭО SОК KКrОХТК, RЮssТК. – SМКЧНТЧКЯТКЧ JШЮrЧКХ ШП FШrОsЭ RОsОКrМС 29: 152–161. 130 Reports of the Finnish Environment Institute 40 | 2014 2.5 Mires of the Zaonezhye Peninsula Oleg Kuznetsov*, Pavel Tokarev*, Stanislav Kutenkov*, Vladimir Antipin* and Tapio Lindholm** * Institute of Biology of the Karelian Research Centre of Russian Academy of Sciences, Petrozavodsk. 11 Pushkinskaya St., 185003 Petrozavodsk, Karelia, Russia ** The Finnish Environment Institute (SYKE), P.O.Box 140, 00251 Helsinki, Finland. Corresponding author: Tapio Lindholm E-mail: tapio.lindholm@ymparisto.i Introduction Mire ecosystems play an essential role in the boreal zone, both in landscape functioning and in biodiversity conservation. Since the mid-20th century, mires in the southern parts of the Republic of Karelia have been extensively drained for forestry and agriculture. Due to these practices, there has been a need for special research and decision making to protect the diversity of wetland ecosystems in the republic (Antipin & Kuznetsov 1998). Since 1950, the Mire Ecosystems Laboratory of the Institute of Biology of the Karelian Research Centre Russian Academy of Sciences has carried out multidisciplinary studies on wetland vegetation, stratigraphy, dynamics and natural resources, as well as their management and protection in the European North of Russia and adjacent regions (Kuznetsov 2003, Elina & Kuznetsov 2006, Elina et al. 2010). For nearly 30 years, the Mire Ecosystems Laboratory has been studying wetland diversity in eastern Fennoscandia as well as mire conservation issues in collaboration with colleagues from Finland (Heikkilä et al. 1997, 2001, Kuznetsov et al. 2012). Zaonezhye Peninsula lies between two long bays in the northern part of Lake Onega. Its nature is quite different from other parts of eastern Fennoscandia. First, the vegetation is highly diverse owing to the mineral-rich bedrock and soils. Secondly, the dissected terrain and the small size of mires have spared them from large-scale draining. Even though Zaonezhye has been inluenced by human activities already for a millennium, there are still substantial areas of undisturbed nature, which are of high conservation value for the entire Northern Europe. Different types of mires are the best-preserved ecosystems in Zaonezhye. Therefore, special research on mire ecosystems has been carried out within the project “Barents Protected Area Network, BPAN”, resulting in proposals for biodiversity conservation in Zaonezhye. Reports of the Finnish Environment Institute 40 | 2014 131 Study area Zaonezhye Peninsula features two contrasting landscapes: highly dissected tectonic-denudation ridge landscape in the northwestern and central parts, and glacial lacustrine plain landscape in the eastern and southeastern parts of Zaonezhye. The contrasting landscapes have shaped the patterns of paludiication as well as the distribution of mire types in the peninsula. The Mire Ecosystems Laboratory of the Institute of Biology of the Karelian Research Centre RAS has carried out botanical and stratigraphic surveys on some of the mires since 1951. A part of the results have been published (Kozlova 1971, Antipin et al. 1993, 1994, Dyachkova et al. 1993, Kuznetsov & Khokhlova 1994, Elina et al. 1999, Kuznetsov et al. 1999, 2000, 2013, Maksimov 2005). These results have also been used in preparing this paper. Material and methods Satellite imagery and in situ surveys revealed 642 undrained mires, covering an area of 15 000 ha. In Zaonezhye, small mires (0.5–10 ha) are widespread, whereas large mires (more than 200 ha) are few. In general, large mires represent mire systems that consist of several massifs, sometimes including different types of mires (Tab. 1, Fig. 1). In the Russian tradition of mire research, a mire massif has been the main object of research. According to this research tradition, individual mires develop in individual depressions. As depressions are illed with peat and expand, individual massifs become connected in mire systems. Mire massifs are classiied based on the composition and structure of plant cover in the central part, as well as the distribution of plant communities along the centre-to-margin gradient of the mire massif (Tsinzerling 1938, Elina et al. 1984, Yurkovskaya 1992). According to Yu.D. Tsinzerling (Tsinzerling 1938), aapa mire massifs also include minerotrophic fens where the central part consists of string-lark or hummock-lack systems. There is a sparse cover of herbs or herbs and mosses on the wet larks, and peat accumulation has either slowed down or ceased (Kuznetsov 1986, 2003). In this study, peat types were determined according to Russian classiication (Tyuremnov 1976), which includes distinctive features for Karelia (Elina et al. 1984). Vegetation dynamics of mires were reconstructed by analysing the botanical composition of peat. Samples were analysed microscopically (with 5% precision) and plant macrofossils were identiied (Korotkina 1939). Based on these data, diagrams were plotted to determine paleacommunities, determined by the dominant plant species in each stratum. Computer programme “Korpi” was used to draw these diagrams (Kutenkov 2013 a). Mire types with similar ecological properties, as well as those dificult to identify in satellite images, were grouped together. Thus, type V (Fig. 1) comprises herbaceous mires on lakeshores as well as herbaceous and herb-moss mires in depressions, which have a pronounced herbaceous cover despite not being associated with lakes. Results and discussion Mapped mires cover 7.6% of the peninsula. Nearly a half of the mires are minerotrophic, forested mires. The tree stands consist of different species and their canopy closure is 40% or higher. There are also areas of paludiied forests (with less than 30-cm-thick peat deposits) that raise the degree of paludiication on the peninsula to around 10%. A large amount of mires in the eastern and southeastern parts of the peninsula have been drained and converted into farmland. Altogether 38 drained mire massifs with a combined area of 3207 ha were identiied from cartographic materials (Peatland … 132 Reports of the Finnish Environment Institute 40 | 2014 1979) and satellite images (Fig. 2). There has been hardly any drainage for forestry, which has affected no more than 300 ha in the northern part of the peninsula. In Zaonezhye, mires occupy tectonic and glacial depressions, as well as overgrow bays of Lake Onega and other inland waterbodies. As a result, mires have a NW-SE orientation, which can be clearly seen in Figure 1. The mires of Zaonezhye were formed at different times. In higher parts of the peninsula, where the waters of Lake Onega retreated earlier, mires began forming 8000–9000 BP; whereas in the Lake Onega bays, mire formation occurred 3000–5000 BP (Elina et al. 1999, Kuznetsov et al. 1999). These mires are of both terrestrial and lacustrine origin. In tectonic depression, lacustrine-paludal deposits are often ive to seven (or nine) metres, and sapropel deposits one to several meters thick. In one herbaceous mire on the southern shore of Lake Karasozero, there is over eight metres of sapropel, with a metre of quagmire peat on top. There are also mires in depressions, resembling gullies, with four to six metres of peat deposits of terrestrial origin. Examples of peat stratigraphy and formation of massifs are given below. In moraine and lacustrine sediments, as well as in the Lake Onega bays, peat deposits are thinner (between one and three metres). Table 1. Types of mire massifs on Zaonezhye Peninsula. Type of mire massif Number Number Area, ha (%) Min. and max. area of massif, ha Min. and max. area of massif, ha Ombrotrophic ridge-hollow bogs (raised bogs) (I) Average area of massif, ha 238 61 – 358 Ombrotrophic pine-dwarf shrub-cottongrass-Sphagnum bogs (pine bogs) (II) Min. and max. area of massif, ha 12 0.5 – 200 Mesotrophic tree-grass-Sphagnum mires (III) 1730 (12) 14 0.5 – 184 Mesoeutrophic string-lark aapa mires (IV) 7 326 (2) 82 1 – 168 Mesoeutrophic and eutrophic herb-moss and herb mires (V) 118 2003 (13) 15 0.5 – 330 Minerotrophic forested mires (VI) 105 7378 (49) 77 2– 586 Undetermined mire type (VII)* 82 367 (3) 4 0.5– 19 Total 642 15064 (100) 24 0.5-586 *These include small mires whose plant cover could not be determined. Zaonezhye Peninsula is characterized by basic and ultrabasic bedrock, whose clasts are found also in Quaternary sediments. As a consequence, groundwater discharge to mires is highly mineralized and minerotrophic mires are widespread (Tab. 1). It has made little sense to drain mires in the ridge landscape due to the topography and the small size of mires. Therefore, nearly all mires on the peninsula remain intact. As a result, the mires of Zaonezhye feature a high diversity at several levels of ecosystem organization. The mires of Zaonezhye contain around 240 vascular plant species, which is over 70% of the entire mire lora in Karelia (Kuznetsov 2012). There are several regionally red-listed species (Ivanter & Kuznetsov 2007), including Epipactis palustris, Malaxis monophyllos and Dactylorhiza traunsteineri, as well as a number of Siberian species at the western limit of their distribution that are relatively rare in Fennoscandia, including Ligularia sibirica and Rubus humulifolius. The moss lora of the Zaonezhye mires is also relatively comprehensive. There are around 90 species, which account for more than 60% of the moss lora of Karelian mires. Also rare species occur, some of which are at the limit of their range, including Sphagnum pulchrum, S. lindbergii, S. Reports of the Finnish Environment Institute 40 | 2014 133 aongstroemii, Hamatocaulis vernicosus and Loeskypnum badium (Boychuk & Kuznetsov 2000, Maksimov & Syrjanen 2014). Also, the plant communities of Zaonezhye mires are highly diverse. They represent more than a half of known syntaxa of mire vegetation in Karelia (Kuznetsov, 2003, 2012). Especially noteworthy is the wide range of eutrophic communities of herbaceous and herb-moss mires as well as tree-herb-moss mires. These mires are of high conservation value for the whole of Northern Europe. Below we give a short description of plant cover and formation patterns of the main types of mire massifs in Zaonezhye. Ombrotrophic ridge-hollow Sphagnum bogs occupy 956 ha (6%) and comprise several relatively large mire systems (Yuno, Pivgozerskoe, and Koybozerskoe) in Zaonezhye. Their central parts are characterized by a ridge-hollow or hummock-hollow microtopography (Fig. 3). Dwarf shrub-Sphagnum communities with Sphagnum fuscum (sometimes S. magellanicum) and the occasional pine grow on the ridges, whereas the hollows are dominated by Sphagnum balticum and Eriophorum vaginatum, sometimes Scheuchzeria palustris. These mires may also have narrow water tracks, occupied by mesotrophic sedge-Sphagnum communities (Carex rostrata – Sphagnum fallax). The mire margins are covered by pine-cottongrass-dwarf shrub-Sphagnum communities, which are also habitats of cranberry and cloudberry. Among these mires, of particular conservation value is the Koybozerskoe mire, where moss species rare for Zaonezhye have been found, including Sphagnum pulchrum, S. lindbergii and S. aongstroemii (Kuznetsov et al. 2000). Ombrotrophic pine-dwarf shrub-cottongrass-Sphagnum bogs occupy ca. 2300 ha (15%) in Zaonezhye. These mires are represented by a large number of small mire massifs, ranging from 0.5 to 10 ha, and only a few mires larger than 100 ha. Their tree stands are sparse (with a canopy closure of 0.2–0.4%) and their tree layers are 4–10 m (sometimes 12–14 m) tall. The ground cover is dominated by Rubus chamaemorus, which is a common dwarf shrub on wetlands. Also Eriophorum vaginatum is often present. There is a continuous moss cover, comprising Sphagnum angustifolium, S. magellanicum, S. russowii, S. fuscum, S. capillifolium and Pleurozium schreberi in different proportions. There is little variation in microtopography, although dwarf shrubs are more abundant in elevated areas around tree trunks. These mires are usually relatively shallow (2–3 m thick). In most cases their formation began with minerotrophic stages. A proile of this type of mire is shown in Figure 4. Its formation began with a eutrophic horsetail-Sphagnum community (Borehole 2), which was soon replaced by a cottongrass-Sphagnum mesotrophic community, followed by an ombrotrophic stage. Peat bog deposits in the mire are two metres thick. At the margins (Boreholes 1 and 3) the mire has not gone though a minerotrophic stage. Aapa mires occupy 326 ha (2%) of the peninsula. These mires are conined to narrow depressions and abundantly fed by groundwater from the mineral banks. They form a part of a number of mire systems, together with other types of mire massifs. Central parts of aapa mires are characterized by string-lark and hummock-lark complexes, with herbaceous or herb-Hypnum larks. The formation of these complexes in the aapa mires of Zaonezhye began relatively recently. Therefore, the strings are low (10–20 cm) and the herbaceous cover of the larks is relatively dense. These complexes occupy 20–30% of the area of the massifs. Owing to highly mineralized groundwater and a high low rate, the vegetation of the complexes is eutrophic or mesoeutrophic. Microtopographic elevations are covered by herb-Sphagnum (Sphagnum centrale, S. warnstorii, S. subfulvum, S. teres) communities. The ield layer is dominated by Carex lasiocarpa and Molinia caerulea, with frequent Potentilla erecta and Trientalis europaea, as well as Juniperus communis and short pines. The larks host herbaceous and herb-Hypnum (Warnstoria exannulata, Scorpidium scorpioides) communities, sometimes with 134 Reports of the Finnish Environment Institute 40 | 2014 Sphagnum subsecundum and S. teres. The ield layer consists of sedges (Carex lasiocarpa, C. limosa, C. livida, C. chordorrhiza), Menyanthes trifoliata, Equisetum luviatile and Utricularia intermedia. Most of the area in aapa mires is occupied by herb-moss eutrophic and mesoeutrophic communities, and there is little variation in microtopography. The rims of aapa mires are covered by mesotrophic tree-herb-Sphagnum communities. Due to this feature, aapa mires in Zaonezhye are similar to herb-moss mires, which makes identifying these two types in satellite images and in-situ surveys problematic. Kalegubskoe mire massif (№ 15, Fig. 1) illustrates the formation of aapa mires. It covers 168 ha in a deep and narrow tectonic depression, which is over 5 km long, and its waters discharge to Lake Onega. The peat deposits of Kalegubskoe mire are 5.5 metres thick (Fig. 5, 6). Its formation began with eutrophic birch-reed communities (stage I, Fig. 6). These communities persisted for several millennia, during which the mire underwent changes in herb and moss cover composition (stages II, III). As a result, there are four metres of woody and woody-herbaceous fen peat deposits on Kalegubskoe mire. The central part of the mire is covered by 1.5 metres of sedge fen peat deposits from sedge-moss communities (stage IV). This is a typical situation for aapa mires, which have been developing since the early sub-Atlantic period (ca. 2500 BP) (Kuznetsov, 1986). A cooling climate and increased moisture were the driving forces in the formation of these mires, causing a rise in water level and water retention. In this speciic mire, trees have been replaced by wet herb-moss aapa complexes. Eutrophic and mesoeutrophic herb-moss mires develop in basins with an ample groundwater feed, sometimes from springs. These and mires on lakeshores together make up 13% of all the mires on the peninsula. Herb-moss mires feature a relatively diverse plant cover. The ield layer consists of various sedge species with several wetland herbs. The moss cover is composed of both Sphagna (Sphagnum obtusum, S. subsecundum, S. teres, S. centrale), and Bryidae (Warnstoria exannulata, Hamatocaulis vernicosus, Cynclidium stygium, Campylium stellatum, Paludella squarrosa, Scorpidium scorpioides, Tomentypnum nitens). The microtopography of the mires is indistinct, and the peat accumulation rate is high. There are only a few woody plants. Among them, Picea x fennica with drooping tops usually grow around hummocks, associated with groundwater springs. The lora of these mires comprises a number of rare and calciphile species, including Epipactis palustris, Malaxis monophyllos, Bistorta major, Rumex fontanopaludosus, Ligularia sibirica and Dactylorhiza traunsteineri. Dlinnoe mire (№ 7, Fig. 1) is a system of several herb-moss mire massifs, formed in narrow tectonic depressions. It consists of small ombrotrophic dwarf shrub-Sphagnum mires that are not looded by groundwater. At the centre of one of the mire massifs is Lake Chelozero. A stratigraphic proile has been established 100 metres south of the lake (Fig. 7). In this part, the depth of the mire is up to 6.5 metres. The lower strata of the deposit are made up of woody and woody-reed fen peat, suggesting that the mire developed from birch-reed communities on land. (Fig. 8, stage I). In this part of the mire, the lake has luctuated and its waters have spilled (as the lake has expanded) onto the mire surface more than once over the history of the mire. As a result, there are 0.5–1.5 m thick water lenses in the peat deposit (Fig. 7, boreholes 4, 5; Fig. 8, stages II, V). The analysis of plant succession from borehole 4 (Fig. 8) revealed a 75 cm water lens (II), suggesting that soon after 0.5 m of woody-reed peat was deposited, the mire was looded again (stage 1). Subsequently, a eutrophic reed-Sphagnum community (III) was formed, soon replaced by a meso-oligotrophic cottongrass-Sphagnum community (IV) with Sphagnum angustifolium. This succession means that there was no longer groundwater supply to the central part of the mire. Another two-metres-thick water lens (V) indicates yet another looding of the site. Eventually, the waterbed was covered with a loating mat, consisting of a mesotrophic Scheuchzeria-Sphagnum community with Sphagnum obtusum (VI), followed by a me- Reports of the Finnish Environment Institute 40 | 2014 135 so-oligotrophic cottongrass-Sphagnum community (VII) with Sphagnum magellanicum. In the deposit, the transition to an ombrotrophic stage (VIII) with Sphagnum fuscum is visible at the depth of one metre. This small (ca. 30 m wide) dwarf shrub-cottongrass-Sphagnum community in the centre of the mire has no inlux of groundwater. It is surrounded on all sides by eutrophic herb-moss communities. The vegetation dynamics of a sedge-Sphagnum community (borehole 3 in Fig. 7) are shown in Fig. 9. Also this part of the mire began with a tree-reed community (stage I), which was replaced by reed-Sphagnum communities (stages II, III). These communities persisted several millennia, resulting in 3.5-metre deposits of herb-Sphagnum fen peat. In the top 25 cm of the peat deposit, there is evidence of a recent rise in water content and reduction in low rate, which have driven plant succession at the site (stage IV). As a result, the hydrophilous Sphagnum subsecundum has increased, whereas reeds have nearly disappeared. On lakeshores, communities of herbaceous mires dominated by Carex elata spp. omskiana, C. diandra, C. cespitosa, C. vesicaria, Phragmites australis, Equisetum palustre, Comarum palustre and Menyanthes trifoliate are widespread (Fig. 10). These communities consist of over 100 vascular plant species, including a number of semi-aquatic plants that are not found in any other types of mires. Depending on the duration of spring and summer loods, the moss cover is either poor or completely missing in these mires. Their relatively shallow (1–2 m) peat deposits consist of herbaceous peat with high ash content (Kuznetsov et al. 2000). Mesotrophic tree-grass-Sphagnum mires cover 1730 ha (12%) in Zaonezhye. These small mire massifs occupy depressions of different genesis. Their tree layer consists of pine and birch stands that are between 3–4 and 6–8 metres high, with a canopy closure of 0.2–0.3. The ield layer is made up of sedges, wetland herb species and occasionally reeds. In addition, hummocks around tree trunks are often covered with wetland dwarf shrubs. There is also a continuous moss cover, dominated by Sphagnum angustifolium, with Sphagnum centrale, S. russowii, S. magellanicum and S. teres. Forested mires account for half of the total area of mires in Zaonezhye. Forested mires occur on moraine plains as well as in depressions in the ridge terrain. These mire massifs range in size from two to several hundred hectares, and nearly all of them are minerotrophic. The mires are of different genesis and their lacustrine-paludal deposits range from 0.5–1 to 5.5 metres in depth. Forested mires have a highly diverse plant cover, consisting of a wide range of tree-grass and tree-grass-moss communities. The tree stands are between 10–12 to 20–22 metres tall and their canopy closure is 0.4–0.7%. There are single-species as well as mixed stands of pine, spruce, downy birch and black alder on these mires (Kutenkov 2013 b). Forested mire communities either form separate mire massifs, or occur at the margins of other mires. Eutrophic spruce, birch and black alder stands are widespread. Their herbaceous ield layer is dominated by Filipendula ulmaria, sometimes Phragmites australis, sedges (Carex cespitosa, C. vesicaria, C. rostrata) and Calla palustris. The microtopography of these mires is characterized by wet microdepressions and high hummocks around tree trunks. Due to the high diversity of microhabitats, there is also a high diversity of plant communities: Up to 57 vascular plant species and 20 moss species have been found from one site. In forested mires, the moss cover is discontinuous and consists of a number of eutrophic species, including Sphagnum warnstorii, S. squarrosum, S. teres, S. centrale, Tomentypnum nitens, Campylium stellatum, Scorpidium revolvens, Calliergon cordifolium, Pseudobryum cinclidioides, Plagiomnium ellipticum and Calliergonella cuspidata. Sphagnum angustifolium, S. russowii and other forest bryophytes grow on the hummocks around tree trunks, together with dwarf shrub and herb species, associated with forests. Of special interest are eutrophic herb-Sphagnum pine mires, where Molinia caerulea dominates the ield layer. These mires are associated with carbonaceous bedrock and 136 Reports of the Finnish Environment Institute 40 | 2014 contain a number of calciphile species. Their moss layer is dominated by Sphagnum warnstorii, although other eutrophic species are also present. In Zaonezhye, mesotrophic grass-Sphagnum pine mires as well as bilberry-Sphagnum and horsetail-Sphagnum spruce mires are rare and small. Also ombrotrophic dwarf shrub-Sphagnum pine mires are rare. Overall, the lora of forested mires in Zaonezhye consists of 155 vascular plant species and 68 moss species. Due to their species diversity, the mires of Zaonezhye are of high conservation value (Kutenkov 2013 b). Mires conservation in Zaonezhye The Kizhy federal nature reserve was established to protect the diverse ecosystems of the skerries in the southestern part of Zaonezhye. There are also herbaceous mires on the lakeshores within the boundaries of the reserve. In addition, seven regional mire nature monuments have been established on Zaonezhye Peninsula (Tab. 2, Fig. 1). Also a number of other, both representative and unique, mires merit a conservation status (Tab. 2; Fig. 1). A feasibility study that has been carried out for the Zaonezhye landscape reserve and is under discussion at the Ministry of Nature Use and Environment of the Republic of Karelia (Gromtsev 2013). If the landscape reserve is established, all these mires will be protected and the biodiversity of mire ecosystems in Zaonezhye will be conserved. REFERENCES AЧЭТЩТЧ, V.K. & KЮгЧОЭsШЯ, O.L. 1998. . ., . . ДCШЧsОrЯКЭТШЧ ШП НТЯОrsТЭв ШП ЦТrОs ТЧ KКrОХТКЖ. – IЧ: KЮгЧОЭsШЯ, O.L. (ОН.), BТШНТЯОrsТЭв, НвЧКЦТМs КЧН МШЧsОrЯКЭТШЧ ШП ЦТrО ОМШsвsЭОЦs ТЧ ОКsЭОrЧ FОЧЧШsМКЧНТК. KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs PОЭrШгКЯШНsФ. Щ. 10–30. (IЧ RЮssТКЧ). AЧЭТЩТЧ, V.K., TШФКrОЯ, P.N. & SСОЯОХТЧ, P.F. 1993. . ., . ., . . , ДMТrО ШП ГКШЧОгСвО ЩОЧТЧsЮХК, ЭСОТr ЦОКЧТЧР КЧН МШЧsОrЯКЭТШЧЖ. – KТгСsФвТ ЯОsЭЧТФ 2: 79–87. (IЧ RЮssТКЧ). 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(55 ) ДTСО СТsЭШrв КЧН МЮrrОЧЭ sЭКЭЮs ШП ЦТrО rОsОКrМС ТЧ KКrОХТК. 55 вОКrs ЭШ MТrО EМШsвsЭОЦs LКЛШrКЭШrвЖ. − IЧ: KЮгЧОЭsШЯ, O.L., DУКМСФШЯК, T.ВЮ., ГЧКЦОЧsФТв S.R. (ОНs.), MТrО EМШsвsЭОЦs ТЧ NШrЭСОrЧ EЮrШЩО: DТЯОrsТЭв, DвЧКЦТМs, CКrЛШЧ BКХКЧМО, RОsШЮrМОs КЧН CШЧsОrЯКЭТШЧ. PrШМ. ШП IЧЭОrЧКЭТШЧКХ SвЦЩШsТЮЦ. PОЭrШгКЯШНsФ. Щ. 11–34. (IЧ RЮssТКЧ). EХТЧК, G.A., KЮгЧОЭsШЯ, O.L. & MКФsТЦШЯ, A.I. 1984. . ., . ., . . – . ДSЭrЮМЭЮrКХ КЧН ПЮЧМЭТШЧКХ ШrРКЧТsКЭТШЧ КЧН НвЧКЦТМs ШП ЦТrО ОМШsвsЭОЦs ТЧ KКrОХТКЖ. – LОЧТЧРrКН: 128 Щ. (IЧ RЮssТКЧ). EХТЧК, G.A., LЮФКsСШЯ, A.D., FТХТЦШЧШЯК, L.V. & KЮгЧОЭsШЯ, O.L. 1999. . ., . ., . ., . . ДLКЭО GХКМТКХ-HШХШМОЧО ЩКХОШЯОРОЭКЭТШЧ sЮММОssТШЧs ТЧ ЭСО ГКШЧОгСвО PОЧТЧsЮХК КЧН ЭСОТr НОЩОЧНОЧМО ШЧ LКФО OЧОРК ХОЯОХsЖ. – BШЭКЧТМСОsФв ГСЮrЧКХ 84 (6): 32–52. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 137 EХТЧК, G., LЮФКsСШЯ, A., ВЮrФШЯsФКвК, T. 2010: LКЭО GХКМТКХ КЧН HШХШМОЧО ЩКХКОШЯОРОЭКЭТШЧ КЧН ЩКХКОШРОШРrКЩСв ШП EКsЭОrЧ FОЧЧШsМКЧНТК . − TСО FТЧЧТsС EЧЯТrШЧЦОЧЭ 2010/4: 1–304. GrШЦЭsОЯ, A.N. (ОН.), 2013. . . ( .). : , ДSОХФК LКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ CСКrКМЭОrТsЭТМs, LКЧН UsО, CШЧsОrЯКЭТШЧЖ. – KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs PОЭrШгКЯШНsФ: RAS. 180 Щ. (IЧ RЮssТКЧ). HОТФФТХт, R., KЮгЧОЭsШЯ, O. & LТЧНСШХЦ, T. 1997: – CШЦЩКrТsШЧ ШП ЭСО ЯОРОЭКЭТШЧ КЧН НОЯОХШЩЦОЧЭ ШП ЭСrОО ЦТrОs ТЧ EХТЦвssКХШ NКЭЮrО RОsОrЯО. – LТЧНСШХЦ, T., HОТФФТХт, R. & HОТФФТХт, M. (ОНs.), : EМШsвsЭОЦs, ПКЮЧК КЧН lШrК ШП ЭСО FТЧЧТsС-RЮssТКЧ NКЭЮrО RОsОrЯО FrТОЧНsСТЩ. – SЮШЦОЧ вЦЩтrТsЭö 124: 63–82. HОТФФТХӓ, R., KЮгЧОЭsШЯ, O., LТЧНСШХЦ, T., AКЩКХК, K. & SСОЯОХТЧ, Щ. 2001. CШЦЩХОбОs, ЯОРОЭКЭТШЧ, lШrК КЧН НвЧКЦТМs ШП KКЮСКЧОЯК ЦТrО sвsЭОЦ, аОsЭОrЧ FТЧХКЧН. – TСО FТЧЧТsС EЧЯТrШЧЦОЧЭ 489. Щ. 1–97 IЯКЧЭОr, E.V. & KЮгЧОЭsШЯ, O. L. (ОНs.), 2007. . ., . . ( .). ДRОН DКЭК BШШФ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ. KКrОХТК. 368 Щ. (IЧ RЮssТКЧ). KШrШЭФТЧК, M. I. 1939. . . ДMКМrШПШssТХ КЧКХвsТs ШП ЩОКЭЖ. - IЧ: NОЮsМСЭКНЭ M.I. (ОН.) MОЭСШНs ПШr ТЧЯОsЭТРКЭТШЧs ШП ЩОКЭ ЦТrОs. PКrЭ II. MШsМШа. Щ. 5–59. (IЧ RЮssТКЧ). KШгХШЯК, R.P. 1971. . . ДVОРОЭКЭТШЧ КЧН sЭrКЭТРrКЩСв ЦКТЧ ЦТrО ЭвЩОs ТЧ sШЮЭС KКrОХТКЖ. − IЧ: LШЩКЭТЧ V.D. (ОН.) ArЭТМХОs ШЧ ЩХКЧЭ МШЯОr ШП KКrОХТКЧ ASSR. PОЭrШгКЯШНsФ: KКrОХТК. Щ. 73–94. (IЧ RЮssТКЧ). KЮЭОЧФШЯ, S.A. 2013 К. . . «KШrЩТ» ДKШrЩТ sШПЭаКrО ПШr ЩХШЭЭТЧР sЭrКЭТРrКЩСТМ НвЧКЦТМs ШП ЩОКЭ МШЦЩШsТЭТШЧ МСrШЧТМХОЖ. – PrШМООНТЧРs ШП ЭСО KКrОХТКЧ RОsОКrМС CОЧЭrО ШП ЭСО RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. EМШХШРТМКХ SЭЮНТОs SОrТОs 6: 171–176. (IЧ RЮssТКЧ). KЮЭОЧФШЯ, S. . 2013 Л. . . ДMТrО ПШrОsЭsЖ. – IЧ: GrШЦЭsОЯ A.N. (ОН.), SОХФК LКЧНscapes of the Zaonezhskii Peninsula: Natural Characteristics, Land Use, Conservation. Karelian Research CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 61–65. (IЧ RЮssТКЧ). KЮгЧОЭsШЯ, O. 1986. TСО sЭrЮМЭЮrО КЧН КРО ШП rТНРО-СШХХШа ККЩК ЦТrОs МШЦЩХОбОs. − PЮЛХТМКЭТШЧ ШП KКrОХТКЧ IЧsЭТЭЮЭО, JШОЧsЮЮ UЧТЯОrsТЭв 79: 73–79. KЮгЧОЭsШЯ, O.L. 2003. MТrО ЯОРОЭКЭТШЧ. − IЧ: BТШЭТМ НТЯОrsТЭв ШП KКrОХТК: МШЧНТЭТШЧs ШП ПШrЦКЭТШЧ, МШЦЦЮЧТЭТОs КЧН sЩОМТОs. GrШЦЭsОЯ, A., KТЭКОЯ, S., KrЮЭШЯ, V., KЮгЧОЭsШЯ, O., LТЧНСШХЦ, T.& ВКФШЯХОЯ, E. (ОНs.), – KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 57–63. KЮгЧОЭsШЯ, O. L. 2012. MТrО lШrК КЧН ЯОРОЭКЭТШЧ КЧН ЭСОТr МШЧsОrЯКЭТШЧ ТЧ ЭСО RОЩЮЛХТМ ШП KКrОХТК, RЮssТК. − IЧ: LТЧНСШХЦ, T. & HОТФФТХт, R. (ОНs.), MТrОs ПrШЦ ЩШХО ЭШ ЩШХО. TСО FТЧЧТsС EЧЯТrШЧЦОЧЭ 38/2012: 133–142. KЮгЧОЭsШЯ, O. L., DУКМСФШЯК, T.ВЮ., & GrКЛШЯТФ, S.I. 2000. . ., . ., . . ДMТrОsЖ − IЧ: GrШЦЭsОЯ, A., KТЭКОЯ, S., KrЮЭШЯ, V., KЮгЧОЭsШЯ, O., LТЧНСШХЦ, T. & ВКФШЯХОЯ, E. (ОНs.), Biotic diversity of Karelia: conditions of formation, communities and species. Karelian Research Centre of RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 71–83. (IЧ RЮssТКЧ). KЮгЧОЭsШЯ, O. L., SЭШТФТЧК N.V., & BrКгШЯsФКвК T.I., 1999. . ., . ., . . , « » Д FХШrК, ЯОРОЭКЭТШЧ КЧН РОЧОsТs ШП ЦТrОs ТЧ ЛЮППОr гШЧО ШП ЦЮsОЮЦ “KТгСТ”Ж. – PrШМООНТЧРs ШП KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs 1: 48−54. (IЧ RЮssТКЧ). KЮгЧОЭsШЯ, O.L. & KСШСШХШЯК, T.ВЮ. 1994. . ., . . ДIЦЩШrЭКЧЭ ЧКЭЮrО ШЛУОМЭs ТЧ KТгСТ sФОrrТОs КЧН ГКШЧОгСвО BКвЖ. − KТгСsФвТ ЯОsЭЧТФ 3: 41–55. (IЧ RЮssТКЧ). KЮгЧОЭsШЯ, O., HОТФФТХт, R., LТЧНСШХЦ, T., MтФТХт, M. & FТХТЦШЧШЯК, L. 2012. HШХШМОЧО ЯОРОЭКЭТШЧ НвЧКЦТМs КЧН МКrЛШЧ КММЮЦЮХКЭТШЧ ШП ЭаШ ЦТrОs ТЧ FrТОЧНsСТЩ PКrФ, ОКsЭОrЧ FТЧХКЧН. − IЧ: LТЧНСШХЦ, T. & HОТФФТХт, R. (ОНs.), MТrОs ПrШЦ ЩШХО ЭШ ЩШХО. TСО FТЧЧТsС EЧЯТrШЧЦОЧЭ 2012/38: 91–112. KЮгЧОЭsШЯ, O.L, AЧЭТЩТЧ, V.K. & TШФКrОЯ, P.N. 2013. . ., . ., . . ДMТrОsЖ. − IЧ: GrШЦЭsОЯ A.N. (ОН.) SОХФК LКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ CСКrКМЭОrТsЭТМs, LКЧН UsО, CШЧsОrЯКЭТШЧ. KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. P. 54–61. (IЧ RЮssТКЧ). MКФsТЦШЯ, A.I. 2005. . . “ » ДCШЧЭОЧЭ ШП ЦКМrШ- КЧН ЦТМrШОХОЦОЧЭs ТЧ ЩОКЭ НОЩШsТЭs ШП ЦТrО ОМШsвsЭОЦs ЧОКr PКНЦК ШММЮrrОЧМОЖ. − IЧ: IОsСФШ, E.P. (ОН.), EМШХШРТМКХ ЩrШЛХОЦs ШП ЦКsЭОrТЧР ШММЮrrОЧМО “SrОНЧУКУК PКНЦК”. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 72–81. (IЧ Russian). MКФsТЦШЯ, A.I. & SвrУтЧОЧ, K. 2014. BrвШЩСвЭОs. – IЧ: LТЧНСШХЦ, T., JКФШЯХОЯ, J. & KrКЯМСОЧФШ, A. (ОНs.), Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia. RОЩШrЭs ШП ЭСО FТЧЧТsС EЧЯТrШЧЦОЧЭ IЧsЭТЭЮЭО 2014/40: 179–191. PОКЭХКЧН НОЩШsТЭs ШП KКrОХТКЧ ASSR. 1979. . – MТЧТsЭrв ШП РОШХШРв ШП RЮssТКЧ FОНОrКЭТШЧ. MШsМШа. 636 Щ. (IЧ RЮssТКЧ). TвЮrОЦЧШЯ, S.N. 1976. . . ДPОКЭ НОЩШsТЭsЖ. – MШsМШа, NОНrК. 487 Щ. (IЧ Russian). TгТЧsОrХТЧР, ВЮ. D. 1938. . . ДMТrО ЯОРОЭКЭТШЧЖ. − IЧ: VОРОЭКЭТШЧ ШП USSR. BШЭКЧТМКХ IЧsЭТЭЮЭО ШП ЭСО USSR AМКНОЦв ШП SМТОЧМОs. MШsМШа–LОЧТЧРrКН. Щ. 355–428. (IЧ RЮssТКЧ). ВЮrФШЯsФКвК, T.K. 1992. . . ДGОШРrКЩСв КЧН МКrЭШРrКЩСв ШП ЦТrО ЯОРОЭКЭТШЧ ШП ЭСО EЮrШЩОКЧ RЮssТК КЧН ЧОТЛРСЛШЮrТЧР ЭОrrТЭШrТОsЖ. – SЭ.-PОЭОrsЛЮrР: KШЦКrШЯ BШЭКЧТМКХ IЧsЭТЭЮЭО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. 256 Щ. (IЧ RЮssТКЧ). 138 Reports of the Finnish Environment Institute 40 | 2014 Table 2. Protected and nominated mires. № in Fig. 1 Name 1 Pigma Area, ha 365 Type of mire massif Mire system of M* treegrass-Sphagnum and ME herb mire massifs Conservation status NM**** 2 Lan’ 30 M tree-grass-Sphagnum RC***** 3 Maloe Unitskoe 31 M tree-grass-Sphagnum RC 4 Mire near Nizhnee Pigmosero Lake 101 O** pine bog RC 5 Yuno 249 O raised bog RC near village Mikheeva Selga 79 O pine bog RC 6 Syarg 118 M tree-grass-Sphagnum RC 7 Dlinnoe 330 Mire system of ME herb-moss mire massifs RC 8 Lovosinskoe 26 O pine bog RC 9 near Nizhnee Munosero Lake 75 ME*** herb mire RC 10 Munoserskoe 28 ME herb mire RC 11 Cherkoserskoe 23 O pine bog RC 12 Koiboserskoe 331 Mire system of O raised bog and M tree-grassSphagnum massifs RC 13 Troinoe 3 46 ME aapa mire RC 14 Troinoe 6 64 O raised bog RC 15 Kalegubskoe 168 Mire system of ME aapa mire and ME herb-moss mire massifs NM 16 near Lake Lelikosero 200 O pine bog NM 17 along Lel’rechka River 95 M tree-grass-Sphagnum NM 18 near Lake Kosmosero 10,6 ME aapa mire RC 19 Zamoshye 178 ME herb mire NM 20 near Petrikovo Bay 43 ME herb mire NM 21 Near village Bojarschina 24 ME herb mire NM 22 Kosmoserskoe 379 ME forested mire RC * M –mesotrophic, **O –ombrotrophic, ***ME – mesoeutrophic, ****NM - nature monument, ***** RC –recommended for conservation Reports of the Finnish Environment Institute 40 | 2014 139 Fig. 1. Undisturbed mires in Zaonezhye. I – VI – Types of mire massifs: I – Ombrotrophic ridge-hollow bog (raised bog), II – Ombrotrophic pine-dwarf shrub-cottongrass-Sphagnum bog (pine bog), III – Mesotrophic tree-grass-Sphagnum mire, IV – Mesoeutrophic string-lark aapa mire, V – Mesoeutrophic and eutrophic herb-moss and herb mire; VI – Minerotrophic forested mire, VII – Small mires of undetermined type. 1-22 – Protected and nominated mires. 140 Reports of the Finnish Environment Institute 40 | 2014 Fig. 2. Mires drained for agriculture in Zaonezhye. 1 - eutropic, 2 - mesotrophic, 3 - ombrotrophic Reports of the Finnish Environment Institute 40 | 2014 141 Fig. 3. Central part of an ombrotrophic ridge-hollow bog. (Photo Pavel Tokarev). Fig. 4. Stratigraphic proile of the pine-dwarf shrub-Sphagnum mire. Abbreviations: peat types: eutrophic (1-2): 1- Equisetum-Sphagnum, 2- Sphagnum, mesotrophic (3-4): 3- cottongrass-Sphagnum, 4- Sphagnum, ombrotrophic (5-9): 5-pine- cottongrass, 6- cottongrass- Sphagnum, 7- cottongrass, 8- magellanicum, 9- angustifolium; 10- degree of decomposition (%), 11- borehole number, 12- till, 13- clay 142 Reports of the Finnish Environment Institute 40 | 2014 Fig. 5. Stratigraphic proile of the Kalegubskoe aapa mire. Abbreviations: peat types (1-7): fen types: 1- woody, 2- woody-reed, 3- woody-Menyanthes, 4- sedge, 5- Hypnum-reed, 6- sedge-Menyanthes, 7- Menyanthes-Sphagnum; 8- degree of decomposition (%), 9- borehole number, 10- till, 11- clay. Fig. 6. Plant succession in the central part of the Kalegubskoe mire (borehole 5). PКХКОШМШЦЦЮЧТЭв (sЭКРО): I – Betula+Pinus – Phragmites+Equisetum, II - Betula – Phragmites+ Menyanthes –Warnstoria sp.+Calliergon sЩ., III – Betula+Pinus - Phragmites+ Menyanthes, IV – Carex (chordorrhiza+limosa+rostrate+diandra)+Scheuchzeria palustris – Sphagnum sect. Subsecunda. Reports of the Finnish Environment Institute 40 | 2014 143 Fig.7. Stratigraphic proile of the Dlinnoe mire. Abbreviations: peat types: eutrophic (1-15): 1- woody, 2- woody-reed, 3- woodysedge, 4-woody-grass, 5- sedge, 6- sedge-grass, 7- Menyanthes-sedge, 8- sedge-Sphagnum, 9-reed-Sphagnum, 10- Scheuchzeria-Sphagnum, 11- grass-Sphagnum, 12- cotton grass-Sphagnum, 13- sedge-Bryales, 14-grass-Bryales, 15- Sphagnum, mesotrophic (1618): 16- Scheuchzeria-Sphagnum, 17- cottongrass-Sphagnum, 18- Sphagnum, ombrotrophic (19-20): 19- fuscum, 20- magellanicum; 21- water, 22- degree of decomposition (%), 23- borehole number, 24- till, 2- clay Fig. 8. Plant succession in the central part of the Dlinnoe mire (borehole 4). 144 Reports of the Finnish Environment Institute 40 | 2014 Palaeocommunity (stage): I – Betula – Phragmites, II – water, III – Phragmites + Sphagnum warnstorii+S. centrale, IV – Eriophorum – Sphagnum angustifolium, V –water, VI – Scheuchzeria palustris+Carex rostrate – Sphagnum obtusum, VII – Eriophorum – Sphagnum magellanicum, VIII - Eriophorum – Sphagnum fuscum. Fig. 9. Plant succession in the eutrophic part of the Dlinnoe mire (borehole 3). Palaeocommunity (stage): I – Betula+Pinus – Phragmites, II – Phragmites+Equisetum+Menyantes – Sphagnum centrale+S. teres, III - Phragmites+Carex lasiocarpa – Sphagnum teres+S. warnstorii, IV – Carex lasiocarpa+Trichophorum – Sphagnum sect. Subsecunda. Reports of the Finnish Environment Institute 40 | 2014 145 Fig. 10. Mesoeutrophic herbaceous mire (Photo: V.L. Mironov). 146 Reports of the Finnish Environment Institute 40 | 2014 2.6 Meadows in Zaonezhye Sergey Znamenskiy Institute of Biology, Karelian Research Center of Russian Academy of Sciences. 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia E-mail: seznam@krc.karelia.ru Introduction Zaonezhye Peninsula, or Zaonezhye, is one of the most important grassland areas in Karelia. The total area of seminatural grasslands in Zaonezhye is estimated at 70 km2 (excluding abandoned, reclaimed ields), or approximately 3.5% of the total area. This amount of seminatural grassland is approximately nine times more than the average for Karelia (0.39% by 2012). 90% of the grasslands are located in the eastern lowlands of Zaonezhye that historically have been more suitable for agriculture and, therefore, human settlements. However, since the middle of the 20th century even this part of the region has not been able to meet the needs of modern intensive agriculture. People have moved out of villages, livestock has been drastically decreased and arable land has been abandoned. The decrease in cattle farming has caused a decline in hay meadows and pastureland. As a result, local grasslands have been reforestated. At the same time grassland area has slightly increased due to the growth of grassland vegetation on abandoned ields. These processes became even more drastic during the 1990s economic crisis. Large cattle farms almost disappeared, while small private farms became increasingly unproitable due to cheap dairy and meat products, imported from other regions. Nowadays extensive meadow landscapes can be found in the vicinity of the Tolvuya village (over 1000 hectares in total), in the Kizhi archipelago (ca. 1000 ha) and near the Kuzaranda village (ca. 800 hectares). Large grassland areas (over 100 ha) are located also close to settlements, including Lambasruchey, Velikaya Guba, Putka and Padmozero. Reports of the Finnish Environment Institute 40 | 2014 147 History of the study of the Zaonezhye’ grasslands The grasslands of Zaonezhye are probably the best studied in the Republic of Karelia. In the middle of the 20th century, Marianna Ramenskaya conducted reseach in the former Zaonezhye municipality. Discoveries made by her group are included in the monograph ‘Meadow vegetation of Karelia’ (Ramenskaya, 1958). This publication is still considered the basic work on Karelian grasslands. Biogeographically, the grasslands of Zaonezhye are a part of the Zaonezhye subprovince of the Southeastern grassland province. The subprovince also includes western parts of Medvezhegorsk and eastern parts of Kondopoga municipalities. On the whole, Zaonezhye is one of the most favorable areas for agriculture and also meadow vegetation in Karelia. First, the geological diversity of the region, especially its carbon-rich shungite mineraloids, provides dark and fertile soils. These soils maintain a better thermal regime during the long, light subpolar summer months. Secondly, the warm and humid climate of Zaonezhye is favourable for agriculture. The mean annual temperature is even higher here than in northern Ladoga. As a consequence, Zaonezhye has become one of the most important agricultural centres in the Russian North. As a result of traditional agricultural practises, grassland vegetation is well developed in Zaonezhye. In her monograph, Marianne Ramenskaya describes the rich vegetation of uncultivated areas in Zaonezhye as follows: “There is indeed a rich vegetation on the dark-coloured, gravel-rich uncultivated soils of Zaonezhye. Uncultivated land is exceptionally abundant, as stony soils are being abandoned due to dificulties in their mechanical treatment.” (p. 55). Unfortunately, the chapter on uncultivated land does not include information about its vegetation structure. Ramenskaya described in general terms six groups of grassland vegetation from dry to mesic meadows, three of which were found in Zaonezhye. In the 1980s and 1990s, Valentina Yudina studied meadows in Zaonezhye and later published the results on meadow vegetation on the islands of Kizhi and Volkostrov (Yudina 1999) as well as on mainland Kizhi (Yudina 2000). Yudina divided seven or eight associations of mesic grassland vegetation using the dominant approach. Syntaxa were named after their dominant vegetation type, e.g. “herb-rich” or “leguminous herb-rich”. During the late 1990s and early 2000s, Sergey Znamenskiy carried out ield studies on the Kizhi archipelago as well as in the vicinity of Tolvuya and Kuzaranda. As a result of these studies, Znamenskiy described ive vegetation associations based on ecology and topography. Different vegetation associations have different soil features, including soil nitrogen level and grain size. Each association is characterized by an ecologically uniform group of indicator species occurring in certain environmental conditions. In 2012 Znamenskiy also studied meadows of the western selkä area of Zaonezhye. Consequently, the classiication of grasslands in southern boreal Karealia now consists of four associations of dry and mesic meadows. Nitroilous tall-weed assosiations of Antriscetum sylvestris (Fig. 1) are one of the most widely distributed grassland associations in Zaonezhye. These associations occupy a large part of abandoned ields and hay meadows where the cessation of agriculture has resulted in the accumulation of dead litter, combined with the eutrophication of soils. A very low species density (on average 12-14 species/m2) and a large amount of nitrophilous species characterize these communities. Indicator species include Anthriscus sylvestris (L.) Hoffm., Artemisia vulgaris L., Heracleum sibiricum L., Dactylis glomerata L., Elymus repens (L.) Gould and Urtica dioica L., which are also dominant species in these communities. Depending on the history of the grassland vegetation, species from other ecological groups also occur as subdominant or satellite species. Also Siberian Hogweed (Heracleum sibiricum) is characteristic of 148 Reports of the Finnish Environment Institute 40 | 2014 the Antriscetum communities in Zaonezhye. However, Siberian Hogweed is mainly found in the eastern parts of the region, while Anthriscus sylvestris is more common in the western parts of Zaonezhye, as well as in southern boreal Karelia in general. As mentioned previously, the biodiversity of the Antriscetum communities is very low. However, their species pool can consist of up to 60-70 species of vascular plants. Therefore, Antriscetum communities can be turned into normal grassland with a few years of habitat management. Mesic meadows in Zaonezhye are divided into two associations that share a proportion of mesophytic plant species, including Achillea millefolium L. Campanula patula L., Galium album L., Hypericum maculatum Crantz., Lathyrus pratensis L., Phleum pratense L., Ranunculus acris L., Trifolium pratense L. Vicia cracca L and Veronica chamaedrys L. In the mesic meadows of Zaonezhye, Brown Knapweed (Centaurea jacea L.) is common, whereas Wig Knapweed (C. phrygia L.) is relatively rare, unlike in the rest of southern boreal Karelia. Also a third knapweed species, Greater Knapweed (C. scabiosa L.), occurs more frequently here than in neighbouring parts of Karelia. Tall grass association Magnograminetum (Fig. 2, 2a) occurs mainly on moderately humid clay soils on lacustrine plains and lat-topped eskers. This association is particularly common on the eastern plains of Zaonezhye. Indicator species include Carex ovalis Gooden., Cerastium fontanumBaumg., Festuca pratensis Huds., Leontodon autumnalis L. and Ranunculus repens L. Wood Cudweed (Gnaphalium sylvaticum L.) is practically absent here, unlike in the Magnograminetum grasslands of the Olonets and Pryazha municipalities. Nitrophilous species, characteristic of Antriscetum sylvestris associations (particularly Anthriscus sylvestris and Dactylis glomerata), can form a large part of the community. Sometimes these species can even become subdominant. One ecological variation of the Magnograminetum association is the tall grass vegetation of lacustrine clay deposits, with codominant Tussock grass (Deschampsia caespitosa (L.) Beauv.). In this variation, characteristic species are generally the same but the species density is lower than in the Magnograminetum association (13-14 in comparison with 19-20 species/m2). Another association of mesic meadows in Zaonezhie is more rare but much more biologically diverse: Forb-rich association Varioherbetum (Fig. 3) occurs on sandy soils on luvioglacial deposits and moraines. These associations grow on stony soils on steep slopes where mechanical soil treatment is dificult. Therefore, these sites have been soon abandoned and their vegetation has become rare. At present forb-rich meadows can only be found on small pastures near old villages. Nowadays there is almost no permanent population in smaller villages and, thus, no livestock. As a result, meadows are declining drastically as they turn into forests or nitrophilous tall-weed vegetation. Characteristic species for this association include Campanula glomerata L., Carum carvi L., Dianthus deltoides L., Festuca rubra L., Fragaria vesca L., Knautia arvensis (L.) Coult., Pimpinella saxifraga L., Plantago lanceolata L. and Plantago media L. Even though Rough Hawkbit (Leontodon hispidus L.) is a common indicator species of the Varioherbetum association in southern boreal Karelia, it is absent in Zaonezhye. However, Spotted Cat’s-ear (Hypochoeris maculata L.) is relatively common. There is also a wide range of satellite species in the association, including a number of meadow and forest plant species. This association is of crucial importance to grassland biodiversity in Zaonezhye. The species pool of Varioherbetum communities can include up to 7080 species of vascular plants. (There are 100-130 species within a single community in some Varioherbetum sites of southern Karelia.) The avarage species density is ca. 18-22 species/m2. A relatively rare association Deschampsietum lexuosae, or rocky meadows (Fig. 4), represents dry grasslands. These associations occur on shallow soils that cover neutral or slightly acidic bedrock outcrops. These meadows have a relatively high Reports of the Finnish Environment Institute 40 | 2014 149 species diversity (17-20 species/m2 and 70-80 vascular plants in the species pool). In addition to Wavy Hair-grass (Deschampsia lexuosa (L. Trin.), characteristic species include plants of rocky vegetation and boreal forests, such as Antennaria dioica (L.) Gaertn., Festuca ovina L., Luzula multilora L.., Rumex acetosella L., Vaccinium vitis-idaea L., Vaccinium myrtillus L. and Veronica oficinalis L. Another important species is Matgrass (Nardus stricta L.), which used to be a common species in Karelia half a century ago but is now becoming increasingly rare. Currently it occurs as a subdominant species in Deschampsietum lexuosae meadows only. Rare species such as orchids can grow on more or less basic rocks (e.g. dolomites). Future of grasslands in Zaonezhye The grasslands of Zaonezhye are declining rapidly. Between 1946 and 2000 grassland area in Karelia decreased 3-4 times (Znamenskiy 2000) and it continues to decrease now. Moreover, grasslands are becoming less diverse. Unmanaged meadows are turning into species-poor tall-weed communities that nowadays occupy more than 80% of the grassland area. One of the most endangered meadow associations is the forb-rich association, which is the main source of loristic diversity in Zaonezhye. Also rocky meadows also important, although these meadows are less endangered due to periodic droughts. The droughts regulate the regrowth of trees, which makes grassland vegetation more sustainable. However, even these communities need cattle grazing and mowing, which have nearly ceased as local villages have been converted into summer cottage communities. Nowadays traditional agriculture has concentrated on the outskirts of large villages, such as Velikaya Guba, Tolvuya or Kuzaranda, while the rest of the area is characterized by irregular land use. Unfortunately the future of grasslands in Zaonezhye does not look good. Even the development of protected areas does not help grasslands since meadow protection requires regular traditional agricultural activities. At present, agricultural activities are not allowed in the management plans of protected areas and even if they were, it would be dificult to arrange grazing and mowing there in practice. At the moment, the only opportunities for meadow protection exist on Kizhi Island where mowing is carried out regularly within the territory of the Kizhi open-air museum. However, local population should be encouraged to practice part-time small-scale farming part. In addition, regulations on small pastures and hay meadows within protected areas should be simpliied in order to protect at least some of the grassland biodiversity in Zaonezhye. Restoration of forest and tall-weed communities into meadows has not been studied enough and could be problematic. REFERENCES RКЦОЧsФКвК, M.L. 1958. ДMОКНШа ЯОРОЭКЭТШЧ ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ. 400 Щ. (IЧ RЮssТКЧ). ВЮНТЧК, V.F. 1999. . . ДMОКНШа ЯОРОЭКЭТШЧ ШП KТгСТ КЧН VШХФШsЭrШЯ ТsХКЧНsЖ. − IЧ: PrШМООНТЧРs ШП KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. BТШРОШРrКЩСв ШП KКrОХТК 1: 75–79. (ТЧ RЮssТКЧ). ВЮНТЧК, V.F. 2000. . . ДMОКНШаsЖ. – IЧ: GrШЦЭsОЯ, A.N. & KrЮЭШЯ, V.I. (ОНs.), BТШНТЯОrsТЭв ТЧЯОЧЭШrТОs КЧН sЭЮНТОs ТЧ ГКШЧОsСвО PОЧТЧsЮХК КЧН NШrЭСОrЧ sСШrО ШП LКНШРК LКФО. PОЭrШгКЯШНsФ. Щ. 84–93 (ТЧ Russian). ГЧКЦОЧsФТв, S.R. 1999. . . ДTСО ЦШНОrЧ sЭКЭЮs КЧН ЭСО КЭЭОЦЩЭ ЭШ ПШrОМКsЭ ЭСО НОЯОХШЩЦОЧЭ ШП ЦОКНШа МШЦЦЮЧТЭТОs ШП KТгСТ ТsХКЧНЖ. − IЧ: PrШМООНТЧРs ШП KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. BТШРОШРrКЩСв ШП KКrОХТК 1: 66–74. (IЧ RЮssТКЧ). ГЧКЦОЧsФТв, S.R. 2000. . . TrКНТЭТШЧКХ rЮrКХ ЛТШЭШЩОs ТЧ KКrОХТК. ДTrКНТЭТШЧКХ rЮrКХ ЛТШЭШЩОs ТЧ ЭСО NШrНТМ МШЮЧЭrТОs, ЭСО BКХЭТМ sЭКЭОs КЧН ЭСО RОЩЮЛХТМ ШП KКrОХТКЖ. − TОЦКNШrН 609: 49–55. 150 Reports of the Finnish Environment Institute 40 | 2014 ГЧКЦОЧsФТв, S.R. 2005. . . ( ) ДDrв КЧН ЦОsТМ ЦОКНШа ЯОРОЭКЭТШЧ ШП ГКШЧОгСвО (KКrОХТК)Ж − IЧ: PrШМООНТЧРs ШП KКrОХТКЧ RОsОКrМС CОЧЭrО ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. KКrОХТК 8: 168–177. (IЧ RЮssТКЧ). ГЧКЦОЧsФТв, S.R. 2013. . . ДMОКНШаsЖ. − IЧ: GrШЦЭsОЯ A.N. (ОН.) SОХФК ХКЧНsМКЩОs ШП ЭСО ГКШЧОгСsФТТ PОЧТЧsЮХК: NКЭЮrКХ МСКrКМЭОrТsЭТМs, LКЧН UsО, CШЧsОrЯКЭТШЧ. PОЭrШгКЯШНsФ Щ. 75–81. (IЧ RЮssТКЧ). Fig. 1. Nitroilous tall-weed associations of Anthriscetum sylvestris (Photo Sergey Znamenskiy). Fig. 2. Tall grass association Magnograminetum (Photo Sergey Znamenskiy). Reports of the Finnish Environment Institute 40 | 2014 151 Fig. 3. Forb-rich association Varioherbetum (Photo Sergey Znamenskiy). Fig. 4. Deschampsietum lexuosae association, (rocky meadow) (Photo Sergey Znamenskiy). 152 Reports of the Finnish Environment Institute 40 | 2014 3 Flora and fauna in Zaonezhye Peninsula area 3.1 Vascular plant lora of Zaonezhye Peninsula Alexei V. Kravchenko*, Pertti Uotila**, Mikko Piirainen** and Alexander N. Sennikov** *Forest Research Institute of the Karelian Research Center of the Russian Academy of Sciences, Petrozavodsk, 11 Pushkinskaya St., RU-185910 Petrozavodsk, Karelia, Russia ** Botany Unit, Finnish Museum of Natural History, P.O.Box 7, FI-00014 University of Helsinki, Finland. Introduction Zaonezhye Peninsula is located in the Zaonezhye loristic district of Karelia (Ramenskaya 1960, 1983) as well as in the biogeographic province of Karelia onegensis (Kon), according to the biogeographic division of the Grand Duchy of Finland and adjacent Russia, developed by 19th century Finnish botanists and zoologists. Earlier the whole Karelia east of the Grand Duchy had been treated as a single region called Russian Karelia or Karelia rossica (Nylander & Saelan 1859). Karelia onegensis was delineated on the map for the irst time in the irst volume of Conspectus Florae Fennicae (Hjelt 1888) and the second edition of Herbarium Musei Fennici (Saelan et al. 1889). Since then its boundaries have been relatively stable compared to the boundaries of other provinces where there have been sometimes considerable changes (for Kola Peninsula, see Uotila 2013). The system of biogeographic provinces of East Fennoscandia has been regularly used in both publications and herbarium labels by northern European naturalists from the late 19th century up to the present day. Finnish botanist and phytogeographer Johan Petter Norrlin was a key person in developing the biogeographic division of East Fennoscandia. In 1870 he studied the vast territory of Zaonezhye (in its broad sense) up to Lake Segozero in the north, Petrozavodsk in the south and the border between the Olonets Province and the Grand Duchy of Finland in the west (i.e. practically the whole catchment area of River Suna). Norrlin provided a lot of information on the lora and vegetation of the territory. As a result, substantial differences between Zaonezhye and neighbouring territories Reports of the Finnish Environment Institute 40 | 2014 153 became evident (Norrlin 1871), which served as the background for recognizing the region as a separate biogeographic province. Fig. 1. The title page of Norrlin’s lora. On the basis of Norrlin’s inventories and subsequent studies by other Finnish botanists, Marianna L. Ramenskaya (1960, 1983) developed the loristic division of Karelia. The boundaries of her Zaonezhye loristic district coincide to a great extent with the boundaries of Karelia onegensis. Due to the natural border formed by Lake Onega, there is no difference between the eastern boundaries of the biogeographic province and the loristic district. Also the northern and southern boundaries are very similar. However, the western boundaries of Karelia onegensis and Zaonezhye loristic district differ substantially. Ramenskaya did not include the upper and middle parts of the Suna river basin in the Zaonezhye loristic district. These areas belong to the West Karelian Highlands that have a rather week relation to Zaonezhye (in both its broad and narrow sense). According to the division of Karelian nature, developed by 154 Reports of the Finnish Environment Institute 40 | 2014 Afanasiy I. Marchenko (1956), the western boundary of the Zaonezhye nature district is even further east, roughly along the 64° E longitude. History of loristic studies on the peninsula The nineteenth century Alexander K. Günther, who was a pharmacist at the Aleksandrovsk iron factory and later became the chief state forester of Olonets Province, carried out the irst studies in Zaonezhye Peninsula in 1863. There is a large amount of data collected, relating to the northernmost part of Zaonezhye as well as Kizhi and Klimentskiy islands. Günther (1867, 1880) published his observations of the lora of Obonezhie (i.e. the area around Lake Onega, including Zaonezhye in its broad sense). The few herbarium specimens he collected are deposited partly in the herbarium of St. Petersburg University (LECB), partly in the Botanical Museum of the University of Helsinki (H). In the same year 1863, the area was studied by two Finnish botanists, lecturer August Kullhem and student Theodor Simming (Norrlin 1871). They collected a lot of herbarium specimens, including some very rare species that have not been discovered since. Unfortunately, Kullhem and Simming did not publish their results. Their collections are located in H. J. P. Norrlin studied Zaonezhye for the whole summer of 1870. He made a few journeys together with Günther who called him «…my dear fellow researcher of the area» (Günther 1880: 11). Norrlin’s results, together with the data collected by Günther, Kullhem and Simming, were presented in general terms in the classic monograph of the lora of Karelia Onegensis (Norrlin 1871); the general part of the lora was also his doctoral thesis in botany. It included an annotated list of species of vascular plants and it was the irst detailed lora of any region in Karelia. The lora was divided into three areas – western, central and eastern – that were usually indicated in the list of taxa. The eastern area corresponds with Zaonezhye. For rare and phytogeographically or otherwise interesting species also localities were listed and features in variation, ecology and phytogeography were given. However, Norrlin only visited the surroundings of Velikaya Guba, Tolvuya and Shunga villages on the peninsula. Despite of its limitations, his work remains the main source on the lora of Zaonezhye for more than hundred years. Norrlin collected a large amount of herbarium specimens, which are deposited in H. At the end of the 19th century, also other Finnish scientists visited the area. In 1888 Norrlin’s student Alfred Oswald Kihlman (later Kairamo), better known for his expeditions to the Kola Peninsula and his later work in plant ecology, studied the surroundings of Kyappyaselkya, Kuzaranda and Shunga villages during his travel across the peninsula to Petrozavodsk (Virtanen 2014). Kihlman got advice on his excursion from Günther. In 1896 Bertil R. Poppius, a Finnish entomologist, made an entomological excursion to Karelia onegensis (see Jakovlev et al. 2014) and collected dozens of herbarium specimens especially from Zaonezhye Peninsula. Kihlman and Poppius visited localities that had been studied before by Norrlin, and collected some very rare species. Their studies can be considered one of the irst examples of monitoring lora. Unfortunately, only very little was published (Kihlman 1888, 1890). However, important indings by Kihlman and Poppius as well as previous researchers were published in Hjelt’s Conspectus (Hjelt 1888–1926). The specimens collected by Kihlman and Poppius are in H. In 1898 Aimo Kaarlo Cajander (another student of Norrlin, who later became professor of silviculture and three times Prime Minister of Finland) and Johan Ivar Lindroth (later Liro; who became professor of plant pathology in Helsinki) visited the southeastern corner of the territory, namely Kizhi, Klimenetskiy (village of Sennaya Guba), Uima and Yuzhnyi Oleniy Islands. They collected large number of specimens, Reports of the Finnish Environment Institute 40 | 2014 155 which are deposited in H. In addition to a brief report on their travel (Cajander & Lindroth 1900), there is a manuscript with a list of sites where observations and collections were made in the Archives of Botanical Museum, Helsinki (Kravchenko et al. 2005; Ahti & Boychuk 2006). The following century At the beginning of the 20th century, Saint Petersburg Society of Naturalists initiated a loristic study of Obonezhie. Petrozavodsk was the starting point of the long expedition of Eduard K. Bezays and A. Verdi in 1907 that ended in Povenets. They visited several places in the eastern shores of Zaonezhye Peninsula and the western shores of Unitsa Bay. The results of the excursion were soon published (Bezays 1911); in addition to the lora of each place studied, even environmental conditions such as landscape, relief, soils and features of land use were described in detail. Unfortunately, some published records are unreliable due to erroneous identiications. The rich collections are kept in Komarov Botanical Institute in St. Petersburg (LE). In 1927 Valentina A. Koroleva studied weeds in South Karelia and visited ca. 30 villages in Zaonezhye Peninsula. In the paper appeared very soon (Koroleva 1927–1928) she listed the main weeds of different crops as well as provided an annotated list of weeds of the entire region, where places in Zaonezhye were mentioned for some rather rare species. Specimens are stored in Herbarium of the N.I.Vavilov Institute of Plant Industry, St. Peterburg (WIR). The next period of loristic studies in Zaonezhye was during the Second World War. In 1941, on the initiative of the Geographical Society of Finland, the Executive committee on research of natural resources of East Karelia (i.e. Republic of Karelia) was established. Besides other natural resources, the lora and vegetation of the region were subjects of the study (Kravchenko & Uotila 1995). The loristic studies focused mainly on settlements and their surroundings, especially along roads. Thus, in 1942 the Swedish botanist Benkt Sparre, who served as a volunteer in the Finnish army, studied the lora of Azhepnavolok village and its vicinities (Sparre 1945). He gave exact localities for the most interesting species and collected 160 specimens from the area. In the same year, Aarno Kalela (son of A. K. Cajander and later professor of botany in Helsinki) visited Unitsa village where he collected a small number of herbarium specimens. The specimens collected by Sparre are housed in the Swedish Museum of Natural History, Stockholm (S), with a few duplicates in H, and the specimens collected by Kalela are housed in H. In 1943 two Finnish botanists, Lars Fagerström (later curator at the Botanical Museum, Helsinki) and Hans Luther (later professor of botany in Helsinki), visited the villages of Shunga, Tolvuya, Velikaya Niva and Velikaya Guba (and areas between the villages, including minor settlements) as well as Bolshoy Klimenetskiy Island. Even though they studied the area for only ive days, Fagerström and Luther prepared a detailed article on their excursion (Fagerström & Luther 1946), in which the most interesting indings were reported with their exact localities. They also presented an overview of previous inventories of the area. Furthermore, Luther, an aquatic plant botanist, prepared a special publication on the rare Caulinia lexilis (as Najas lexilis; Luther 1945), which was found from Velikaja Guba. Their herbarium collections are in H. During the same summer, Viljo Kujala (later professor of forest biology at the Forest Research Institute, Helsinki) travelled in the area and stayed longer, especially in Velikaya Guba. He collected several specimens and wrote a manuscript of his observations on plants; these specimens and the manuscript are in H. The next stage of studies in the area refers to the work of M. L. Ramenskaya, who in her time was a key igure in Karelian botany. She prepared the irst manual on the 156 Reports of the Finnish Environment Institute 40 | 2014 lora of Karelia (Ramenskaya 1960; see also Ramenskaya 1983; Ramenskaya & Andreeva 1982) and she also published a monograph on the meadows in Karelia with an enormous amount of relevés (Ramenskaya 1958). In the period between 17th August and 3rd September 1952, together with her pupil Vera A. Zaykova, Ramenskaya studied the northern part of Zaonezhye; the localities include minor settlements around the villages of Kuzaranda (Al’imovo, Koshkino and Shirokie Polya), Tolvuya (Adrianovskaya, Belokhino (Belokhinskaya), Voronino (Voroninskaya), Zagor’e, Kar-navolok, Padmozero and Pikalevskaya), Shunga (Bor Pudantsev, Deriguzovo, Enina Gora, Zagorskoe, Karpin Navolok, Krestnaya Gora, Putkozero and Seleznevo), and also the village of Velikaya Niva. A large number of relevés were studied, and a lot of specimens were collected. According to her notebook (preserved in the archives of the Karelian Research Centre of the Russian Academy of Sciences), they collected 143 (!) specimens in one day (18th August) only. Even though Ramenskaya worked for the Karelian Research Centre, the collected material is now in the herbarium of the Petrozavodsk State University (PZV). In 1964 Ramenskaya’s specimens – altogether more than 20 000 of them (including many duplicates from LE) – were moved from the Karelian Research Centre – from an unequipped and wet room without heating – to the University. Thus, the collection has been rescued (Gnatyuk 1995; Zaykova et al. 1995). Nevertheless, some specimens have been lost (Zaykova et al. 1995). After Ramenskaya, there was a long break in loristic research in Zaonezhye. Only Eugenia A. Klyukina studied the aquatic lora of few lakes (Valgomozero, Vangozero, Vikshezero, Kosmozero, Padmozero and Putkozero) in 1961 (Klyukina 1965). However, some records are unreliable and the determinations cannot be veriied in lack of voucher specimens. In 1979, Nina I. Ronkonen visited the northeastern part of the territory. She collected information mainly about species that are very rare and potentially in need of protection; the obtained data were taken into account when preparing the irst Red Data Book of Karelia (Volkov & Lapshin 1985). Ronkonen’s collections are kept in the herbarium of the Karelian Research Centre in Petrozavodsk (PTZ). Recent decades Alexei V. Kravchenko studied a number of sites throughout Zaonezhye in 1983, 1988, 1989, 1993, 1998, 1999 (together with M. Kashtanov), 2002–2004, 2007, 2010, 2012 and 2013 (Kravchenko & Sazonov 1992, Kravchenko 1993, Kravchenko et al. 2000 a, Kravchenko & Timofeeva 2012; for the trips in 2004 and 2013 see below). A large number of specimens were collected and later deposited in PTZ. Fig. 2. Alexei Kravchenko on dry meadow near Kuzaranda village, July 2004 (Photo Tapio Lindholm). Reports of the Finnish Environment Institute 40 | 2014 157 Floristic research on the islands of the peninsula continued in the 1980s, mainly within the boundaries of the protected area of Kizhskiy Reserve. As a result, lists of vascular plants of Kizhi Island (Shtan’ko & Lantratova 1985, Kravchenko & Sazonov 1992) as well as the other islands of the area (Kuznetsov 1993, 1997) were published. The largest amount of information was collected from Kizhi Island as well as adjacent islands and the mainland shore by Oleg L. Kuznetsov and his student Elena S. Drosdova. Numerous specimens are kept in PTZ. At the time, also the most important nature protection areas, including botanical sites, were designated (Khokhlova & Semina 1988, Antipin et al. 1994, Kuznetsov & Khokhlova 1994, Khokhlova & Kuznetsov 1996, Kravchenko et al. 2000 a, b, Kuznetsov et. al. 2000). After more than a 30-year break, the study of meadows continued in 1985–1987 (Drozdova 1987). At that time, mires in the vicinities of Lambasruchey and Karasozero villages were studied (Dyachkova et. al. 1993, Antipin et. al. 1994). All the results were documented and some specimens were stored in PTZ. In 1997–2000, a postgraduate student Maksim V. Kashtanov studied the northern part of the peninsula as well as its islands (Kashtanov 1997, 1998 a, b, 1999 a, b). Kashtanov also studied Azhepnavolok village and obtained new data on the lora of the village, studied ca. 60 years earlier by Sparre (Kashtanov 1999 b). Furthermore, he compiled lists of species for 18 islands of the peninsula. Kashtanov collected a great number of specimens, which are kept mainly in PTZ, but also in PZV. Within the framework of several projects sponsored by the Finnish Ministry of the Environment, including an inventory of biological diversity of Zaonezhye Peninsula, further research in the area was carried out in 1998 and 1999. During this time, Oksana A. Butskikh, Alexander M. Kryshen’ and Vera V. Timofeeva visited the vicinities of Kosmozero village, Lakes Kalozero and Chelozero as well as the southern part of Svyatukha Bay of Lake Onega. Collected specimens are kept in PTZ. Within the framework of the last project in 1999, O. L. Kuznetsov and Natalia V. Stoykina studied mires and collected mire plants (Kuznetsov et al. 2000). In addition, Stanislav A. Kutenkov studied paludiied forests in 2002 and 2012 (Kutenkov 2006, 2013). The few collected specimens are kept in PTZ. From 1998 to 2004 Natalia V. Markovskaya studied the distribution and population age structure of orchid species on the islands (Dyachkova & Markovskaya 2003, Markovskaya & Dyachkova 2003, Markovskaya 2004, 2005, Markovskaya et al. 2007). A small number of samples were deposited in PZV. A Russian-Finnish expedition was arranged to the area in 3rd–6th July 2004. Participants from Russia included Elena P. Gnatyuk, A. V. Kravchenko, A. M. Kryshen’ and O. L. Kuznetsov; and from Finland Tapio Lindholm, Mikko Piirainen, Rauno Ruuhijärvi and Pertti Uotila. They visited several islands: Bolshoi Klimenetsky (Klimetsky Nos Cape and Lukovo Cape), Bolshoi Lelikovsky (Radkolye Cape), Megostrov, Paleostrov, Rechnoy, Shunevskiy and Yuzhnyi Oleniy islands, and also the mainland shores in the neighbourhood of Kuzaranda and Tipinitsy villages. A relatively large number of specimens were collected; specimens collected by the Russian participants were deposited in PTZ, and those by the Finnish participants in H. Since 1999 the study of meadows has continued, mainly on Kizhi Island but also on other islands (Yudina 1999, 2000; Znamenskiy 1999, 2000, 2005 a, b, 2010, 2013; Yudina & Stoykina 2005; Timofeeva 2013; Znamenskiy & Timofeeva 2013). As a result, relevés as well as extensive lists of meadow species have been provided. Collections (which are not rich) are in PTZ. In 2009 and 2010, teachers and students of the Petrozavodsk State University studied the shores of Kizhi Island and some other islands (Morozova et al. 2010, 2011); the collected material is kept in PZV. Vera V. Timofeeva studied the mainland opposite Kizhi Island in 2011 (Timofeeva & Nikolaeva 2012), and Unitsa Bay in 2013. In addition, she carried out inventories of 158 Reports of the Finnish Environment Institute 40 | 2014 plants in several lakes (Verkhnee Myagrozero, Gizhozero, Kovshozero, Kondozero, Lelikozero) in 2011–2013. Relatively abundant collections are stored in PTZ. In 2013, two Russian-Finnish expeditions were arranged as pilot projects in the framework of BPAN project leaded by Finnish Environment Institute. During these expeditions, surroundings of Kaskoselga, Lipovitsy, Oyatevstchina, Polya, Tambitsy, Tipinitsy, Vegaruksa, Velikaya Guba, Uzkaya Salma and Zubovo villages, and Lake Rugozero were visited. The participants of the expedition included botanists, zoologists and ecologists. A number of loristic observations were made mainly by A. V. Kravchenko and Kimmo Syrjänen, although botanical data were collected also by Timo Kuuluvainen, Olli Manninen, Jyri Mikkola, and Olli-Pekka Tikkanen. The collected specimens are deposited mainly in PTZ, but also in the herbarium of the University of Turku (TUR). During the last two decades rich loristic material, including ca. 2000 herbarium specimens and a great amount of loristic ield notes, has been collected from Zaonezhye. However, although many papers have been published, detailed data have been included in only a few of them, mainly dealing with red-listed species (Kravchenko et al. 2000 a) and the lora of the planned Zaonezhye Landscape Reserve (Kravchenko & Timofeeva 2013). Information from Zaonezhye was also taken into account in the preparation of the Red Data Book of Republic of Karelia (Ivanter & Kuznetsov 2007). Fig. 3. Pertti Uotila, Elena Gnatyuk and Margarita Boychuk on dry meadow near Kuzaranda village, July 2004 (Photo Tapio Lindholm). Reports of the Finnish Environment Institute 40 | 2014 159 Present knowledge Despite the long history of botanical studies in Zaonezhye, loristic knowledge of this fairly limited territory is still variable. There is relatively comprehensive data available from the southeastern islands, so called Kizhi Skerries (Kizhi Island and numerous surrounding islands as well as a narrow strip of the mainland), and from the northeastern part of Zaonezhye (Tolvuya – Shunga area), as well as from areas along the main roads. However, less data are available from the northwestern part of Zaonezhye. Nevertheless, it is assumed that indigenous species are relatively well known because very few indigenous species have been found since Norrlin’s studies. However, according to available data, many indigenous species are considered rare. But this is rather an artefact, and their distribution will be clariied in the future. In total, ca. 530 indigenous species have been discovered from Zaonezhye Peninsula (excluding microspecies of Ranunculus auricomus, R. cassubicus, R. fallax, Hieracium, Pilosella, and Taraxacum). In earlier studies (Norrlin 1871; Fagerström & Luther 1946), a relatively large number of species were considered unique for Zaonezhye (in its broad sense). However, at present only one of them, Polemonium boreale, is only known in Karelia from the area. Other extremely rare species include Caulinia lexilis, which is known in Karelia from only three localities, two of which are in Zaonezhye; and Helianthemum nummularium, which is known from two localities in Karelia, one of which is in Zaonezhye. Many other species are more frequent in Zaonezhye than in any other region of Karelia, namely Ulmus laevis, Myosoton aquaticum, Cotoneaster antoninae, C. melanocarpus, Chaerophyllum aromaticum, Cuscuta europaea, Pseudolysimachion spicatum, Lycopus europaeus, Eupatorium cannabinum, Potamogeton friesii, P. rutilus, Carex muricata. The majority of these species belong to thermophilous species. About 60 species in Zaonezhye have a mainly southern distribution. Many of them grow near the northern limits of their distribution areas. Some, like Carex muricata, Chaerophyllum aromaticum, Odontites vulgaris and Cuscuta europaea, occur here in their northernmost known localities in Russia; while others, like Dracocephalum ruyschiana and Pseudolysimachion spicatum, are in their northernmost localities in Fennoscandia. In Karelia, Zaonezhye provides the northernmost known localities for species, including Stellaria alsine, Ulmus laevis, Corydalis bulbosa, Myosoton aquaticum, Chaerophyllum aromaticum, Cuscuta europaea, Pseudolysimachion spicatum, Glyceria maxima and Scolochloa festucacea. Fig. 4. Rubus humulifolius (Photo Kimmo Syrjänen). 160 Reports of the Finnish Environment Institute 40 | 2014 Fig. 5. Eupatorium cannabinum (Photo Kimmo Syrjänen). There is a number of southern species that are not rare in Zaonezhye and often play a signiicant part in the composition of plant communities. These species include woody plants Tilia cordata, Ulmus glabra, Alnus glutinosa, Lonicera xylosteum, Daphne mezereum and Solanum dulcamara as well as several herbs, like Polygonatum odoratum, Iris pseudacorus, Campanula persicifolia, Viola mirabilis and Chaerophyllum aromaticum. There is also a small number of northern species, including Woodsia alpina, Cerastium alpinum, Saxifraga nivalis and Poa alpina, occupying outcrops of bedrock, sometimes together with southern species. In addition, Astragalus subpolaris and Oxytropis sordida have been found from dry pine forests. In Zaonezhye, all northern species are very rare, in contrast to northern Lake Ladoga where a small number of northern species are known from several, sometimes dozens of localities; see, e.g., Heikkilä et al. (1999). Some eastern («Siberian») species, e.g., Atragene sibirica, Lonicera pallasii, Aconitum septentrionale, Viola selkirkii, Rubus humulifolius, Ligularia sibirica and Saussurea alpina, can be found from Zaonezhye close to the western limit of their distribution areas. Without certain features of the region, the number of species with mainly eastern distribution could be higher. First, Lake Onega forms a natural barrier to the east. Secondly, if species have managed to jump over or get around the lake, they cannot move further west because of the rivers running east towards Lake Onega and the watershed blocking them in the west. River basins play an essential role in spreading many species. Good examples include Atragene sibirica and Rubus humulifolius that are common especially on the shores of water bodies east of Lake Onega. Reports of the Finnish Environment Institute 40 | 2014 161 Fig. 6. Carex rhynchophysa (Photo Kimmo Syrjänen). Fig. 7. Diplazium sibiricum (Photo Kimmo Syrjänen). Sandy beaches are sometimes inhabited by a few species typical for seashores, including Lathyrus aleuticus, Calamagrostis meinshausenii, Festuca arenaria and Leymus arenarius. Long-term land use has enriched the lora with alien species; their total number in Zaonezhye is ca. 220 (ca. 30% of the vascular lora). The composition of alien lora 162 Reports of the Finnish Environment Institute 40 | 2014 has changed during the course of the past decades. Some weeds, such as Apera spica-venti and Centaurea cyanus, that were common and abundant decades ago have totally disappeared. At the same time, many newcomers have appeared during recent decades, including aggressive invasive species such as Heracleum sosnowskyi and Impatiens glandulifera. In the future, many new species – mainly escapees of ornamental, edible and medicinal plants – are likely to be recorded in the area. Such species have been discovered during the past ive years from, for instance, the villages of Lambasruchey, Pod’elniki, Ruch’i, Shunga, Tolvuya and Velikaya Guba. The large numbers of threatened species and their localities, as well as the number of indicators of biologically valuable forests demonstrate the value of Zaonezhye Peninsula for the lora of Karelia. On the basis of several relatively common and widespread indicator species, all the forests on the peninsula could be considered biologically valuable. This means that practically the whole peninsula, which is more or less covered by forests, is biologically valuable. Table l. The richest plant families in Karelia onegensis, in Zaonezhye Peninsula, and in two protected areas inside the Zaonezhye Peninsula: Kizhi Federal Zoological Reserve (Kizhi Skerries), and the planned Zaonezhye Landscape Reserve. Note that the status indigenous/introduced (alien) was revised for the lora in Kravchenko (2007), thus the numbers of indigenous species given in Gnatyuk et al. (2003 b), which is not revised here, can in few families exceed those for the whole Zaonezhye Peninsula. Karelia onegensis * Zaonezhye Peninsula Kizhi Federal Zoological Reserve ** Planned Zaonezhye Landscape Reserve *** Acreage ca. 30 000 km2 ca. 3 000 km2 500 km2 1100 km2 Family Number of indigenous species / (%) Ordinal number Number of indigenous species / (%) Ordinal number Number of indigenous species / (%) Ordinal number Number of indigenous species / (%) Ordinal number Cyperaceae 69 (10.2) 1 56 (10.4) 1 45 (9.7) 1 42 (9.8) 1 Poaceae 60 (8.9) 2 42 (8.0) 2 35 (7.5) 2 37 (8.5) 2 Asteraceae **** 44 (6.5) 3 41 (7.6) 3 32 (6.9) 3 37 (8.5) 2 Rosaceae 35 (5.2) 4 24 (4.5) 6 28 (6.0) 4 18 (4.1) 5 Ranunculaceae 29 (4.3) 5 25 (4.6) 4 21 (4.5) 5 18 (4.1) 5 Scrophulariaceae 29 (4.3) 5 25 (4.6) 4 18 (3.9) 6 21 (5.0) 4 Caryophyllaceae 27 (4.0) 7 24 (4.5) 6 17 (3.6) 7 18 (4.1) 5 Orchidaceae 27 (4.0) 7 18 (3.3) 8 15 (3.2) 8 15 (3.5) 8 Polygonaceae 19 (2.8) 9 15 (2.8) 9 14 (3.0) 10 9 (2.1) . Brassicaceae 17 (2.5) 10 7 (1.3) . 9 (1.9) . 7 (1.6) . Lamiaceae 15 (2.2) . 13 (2.4) . 15 (3.2) 8 10 (2.3) . Juncaceae 14 (2.1) . 15 (2.8) 9 8 (1.7) . 11 (2.5) 9 Salicaceae 16 (2.4) . 11 (2.0) . 10 (2.1) . 11 (2.5) 9 Total number in the ten richest families / (%) 356 (52.8) 287 (53.2) 240 (51.6) 228 (52.5) 674 539 465 434 Province / Area Total number of indigenous species * Gnatyuk et al. (2003 a); ** Gnatyuk et al. (2003 b); *** Kravchenko & Timofeeva (2013). **** As to Hieracium and Pilosella, all microspecies of each section have been counted as one (collective) species, 4 in Hieracium and 4 in Pilosella. Reports of the Finnish Environment Institute 40 | 2014 163 List of vascular plant species of Zaonezhye, with annotations for threatened and indicator species Explanations The nomenclature mainly follows Kravchenko (2007), and some important synonyms have been given in parentheses. The red-listed and indicator species as well as aliens have been marked with symbols in front of the species name. * red-listed species. ** indicator of biologically valuable forests for Northwest Russia (Andersson et al. 2009). a alien. Each species is provided by an estimation of frequency (printed in bold italics) in Zaonezhye according to the following scale: rr (very rare), r (rare), str (fairly rare), p (here and there), stfq (fairly frequent), fq (frequent and very frequent). For red-listed and indicator species, as well as for some other interesting species, the documentation is given by listing localities with herbarium specimens and related publications. A herbarium specimen is indicated by the year of collecting and collector’s surname (in italics). For the herbaria in which the specimens are kept, see the paragraph History of loristic studies. In a few cases the relevant herbarium is mentioned in the list. Frequencies and localities given by Norrlin (1871) are given within parentheses. An asterisk means that the frequency is given by Norrlin for the whole Karelia onegensis (including Zaonezhye Peninsula), not separately for Zaonezhye Peninsula and Kizhi = Svyatnavolok. The threat categories according to 3 different sources are given at the end of the relevant species descriptions: RDB RF = Red Data Book of Russian Federation (Trutnev et al. 2008), the respective IUCN categories given in parenthesis: 1– ДЮЧНОr ЭСО rТsФ ШП ОбЭТЧМЭТШЧЖ (= МrТЭТМКХХв endangered) 2– ДЧЮЦЛОr ШП ТЧНТЯТНЮКХs Тs НОМХТЧТЧРЖ (= ОЧНКЧРОrОН) 3– ДrКrОЖ (ЭСТs МКЭОРШrв МШЯОrs ЩКrЭ ШП IUCN ЯЮХЧОrКЛХО + ЧОКr ЭСrОКЭОЧОН) RDB RK = RОН DКЭК BШШФ ШП RОЩЮЛХТМ ШП KКrОХТК (IЯКЧЭОr & KЮгЧОЭsШЯ 2007), ЭСО rОsЩОМЭТЯО IUCN МКЭОРШrТОs РТЯОЧ ТЧ ЩКrОЧЭСОsТs: 1– ДЮЧНОr ЭСО rТsФ ШП ОбЭТЧМЭТШЧЖ – 1 (CR, critically endangered), 2– ДЧЮЦЛОr ШП ТЧНТЯТНЮКХs Тs НОМХТЧТЧРЖ – 2 (EN, endangered) 3– ДrКrОЖ – 3 (VU) + 3 (NT) + 3 (LC) (= ЯЮХЧОrКЛХО + ЧОКr ЭСrОКЭОЧОН + ХОКsЭ concern) 4– ДМКЭОРШrв ЮЧФЧШаЧЖ – 4 (DD, НКЭК НОiМТОЧЭ) Note that for the categories given in Red Data Book of Karelia, the erroneous category 3 (LC) Тs МШrrОМЭОН ЭШ 3 (NT). 164 Reports of the Finnish Environment Institute 40 | 2014 RDB EF = RОН DКЭК BШШФ ШП EКsЭ FОЧЧШsМКЧНТК (KШЭТrКЧЭК ОЭ КХ. 1998): 1 – Endangered, 2 – Vulnerable 3 – Rare 4 – Declining ? – Data Deicient Note. Special attention as source of information must be paid to the maps in Hultén (1971). These are handmade maps, for Karelia mainly completed in Helsinki, where information about specimens, literature and archives were added by pencil to the maps of the irst edition of Hultén (1950). At the time, there was no demand for detailed documentation of each dot and the work was done in a short time, using not very detailed maps. As a result, there may be inaccuracies in the locations of the dots, and the maps should be understood more as indicators of general distributions than exact locations of single indings. On the other hand, V. Kujala, one of the persons who commented on the maps and added information especially about Karelia, may have added dots from primary data unknown from other sources, due to his extensive travels in Karelia onegensis during the war. Dubious and erroneously recorded species are given at the end of the list. Huperzia selago (L.) BОrЧС. Об SМСrКЧФ & MКrЭ. – Str. (Norrlin 1871: *Stfq.) Diphasiastrum complanatum (L.) HШХЮЛ – Str. (Norrlin 1871: *Fq.) Lycopodium annotinum L. – Fq. (Norrlin 1871: *Fq.) Lycopodium clavatum L. – Stfq. (Norrlin 1871: *Stfq.) Selaginella selaginoides (L.) P. BОКЮЯ. Об SМСrКЧФ & MКrЭ. – Str. (Norrlin 1871: Fq ТЧ NА ЩКrЭ.) *Isoёtes echinospora DЮrТОЮ – P, ЛЮЭ fq in Kizhi Skerries: more than 30 registered localities. (NШrrХТЧ 1871: SСЮЧРК, V. GЮЛК, ОЭМ.) – RDB RF: 2, RDB RK: 3 (LC) *Isoёtes lacustris L. – P: more than 30 registered localities. (Norrlin 1871: Stfq.) – RDB RF: 3, RDB RK: 3 (LC) Equisetum arvense L. – Fq. (Norrlin 1871: *Fq.) EquТsetum luvТatТle L. – Fq. (Norrlin 1871: *Fqq.) Equisetum hyemale L. – Str. (Norrlin 1871: Str: Shunga, etc.) Equisetum palustre L. – Fq. (Norrlin 1871: *Fq–fqq.) Equisetum pratense EСrС. – Fq. (Norrlin 1871: *Stfq–fq.) Equisetum scirpoides MТМСб. – Rr, rОМОЧЭ rОМШrНs: RОМСЧШв IsХ. (2004 Kravchenko). (Norrlin 1871: Azhepnavolok, fq in Padmozero.) Equisetum sylvaticum L. – Fq. (Norrlin 1871: *Fq–fqq.) Equisetum variegatum SМСХОТМС. Об F. АОЛОr & D. MШСr – Rr. Ashepnavolok (1870 Norrlin, 1896 Poppius); TКЦЛТЭsв – KКsФШsОХРК (2013 Syrjänen). *Botrychium boreale MТХНО – Rr: Azhepnavolok (1996 Kashtanov; KrКЯМСОЧФШ ОЭ. КХ. 2000 К). – RDB EF: 3, RDB RK: 3 (LC) *Botrychium lanceolatum (S. G. GЦОХ.) йЧРsЭr. – Rr: KЮгКrКЧНК (HЮХЭцЧ 1971); B. KХТЦ., Motalovo (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ. КХ. 2000 К). – RDB EF: 4, RDB RK: 3 (NT) Botrychium lunaria (L.) Sа. – Str. (Norrlin 1871: P–stfq.) BotrycСТum multТidum (S. G. GЦОХ.) RЮЩr. – R: ЛОЭаООЧ PrШsОЯsФКвК КЧН BШХ ГКrОЯШ ЯТХХКРОs (FКРОrsЭröЦ & LЮЭСОr 1946); AгСОЩЧКЯШХШФ (SЩКrrО 1945); MОНЯОНОЯШ (1979 Ronkonen); VОrФСЧОО MвКРrШгОrШ (2012 Bogdanova PTГ; 2012 TТЦШПООЯК). – RDB EF: 3 Ophioglossum vulgatum L. – R: Okatovstchina (1952 Ramenskaya & Zaykova); ЛОЭаООЧ VШrШЧТЧsФШО КЧН TШХЯЮвsФТв BШr ЯТХХКРОs (1952 RКЦОЧsФКвК, ШЛs.); TШХЯЮвК (HЮХЭцЧ 1971); Reports of the Finnish Environment Institute 40 | 2014 165 KТгСТ КrОК (HЮХЭцЧ 1971); LТМСФШЯ IsХ. (1998 Kashtanov; KrКЯМСОЧФШ ОЭ. КХ. 2000 К); BШХ. KХТЦ, KШsОХ′РК (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ. КХ. 2000 К); V. GЮЛК (2010 Kravchenko). – RDB EF: 3 Pteridium latiusculum (DОsЯ.) HТОrШЧ. Об Fr. (Pteridium pinetorum C. N. Page & R. R. Mill, P. aquilinum L., s. ХКЭ.) – Stfq. (Norrlin 1871: Fq.) Thelypteris palustris Schott – R. Phegopteris connectilis (MТМСб.) АКЭЭ – Fq. (Norrlin 1871: Fq.) Dryopteris carthusiana (VТХХ.) H. P. FЮМСs – Fq. (Norrlin 1871: Fqq; ТЧМХ. D. expansa) Dryopteris cristata (L.) A. GrКв – R: ca. 10 current records. ** Dryopteris expansa (C. PrОsХ) FrКsОr-JОЧФ. & JОrЦв – Str–stfq. DryopterТs ilТx-mas (L.) SМСШЭЭ – Fq. (Norrlin 1871: Fq.) AtСyrТum ilТx-femТna (L.) RШЭС. – Fq. (Norrlin 1871: Fq.) Cystopteris fragilis (L.) BОrЧС. – Stfq. (Norrlin 1871: Stfq.) **Diplazium sibiricum (TЮrМг. Об G. KЮЧгО) SК. KЮrКЭК – Rr: rОМОЧЭ rОМШrНs B. LОХТФ. IsХ. (2004 Kravchenko); RОМСЧШв IsХ. (2004 Kravchenko, Piirainen); PКХОШsЭШЯ IsХ. (2004 Uotila); Lipovitsy (2013 Syrjänen). (Norrlin 1871: Dianova Gora.) Gymnocarpium dryopteris (L.) NОаЦКЧ – Fq. (Norrlin 1871: *Fqq.) *Woodsia alpina (BШХЭШЧ) GrКв – Rr: Gizhozero (2012 Timofeeva; KrКЯМСОЧФШ & TТЦШПООЯК 2013). – RDB EF: 3, RDB RK: 3 (VU) Woodsia ilvensis (L.) R. Br. – Stfq. (Norrlin 1871: Suoyarvi, Shunga.) **Matteuccia struthiopteris (L.) TШНКrШ – Str. (Norrlin 1871: R.) *,**Asplenium septentrionale (L.) HШППЦ. – Str: МК. 16 ХШМКХТЭТОs TШХЯЮвК – KХТЦ NШs КЧН ЛОЭаООЧ BЮЭОЧОЯШ КЧН ГКsОХОгСвО ЯТХХКРОs (FКРОrsЭröЦ & LЮЭСОr 1946); TОХ′ЩШгОrШ (1952 Ramenskaya & Zaykova PTГ, PГV); SЩТrШЯФК (1979 Ronkonen, 2012 Timofeeva); FШЦТЧШ (1988 KrКЯМСОЧФШ, ШЛs.); LКФО KШгЦШгОrШ, SТХ’ЧвТ IsХ. (1999 Butskih, Kryshen & Timofeeva); KШsЦШгОrШ (1999 Butskih, Kryshen & Timofeeva); PКХОШsЭrШЯ (1999 Kravchenko & Kashtanov, 2004 Uotila); B. KХТЦ., PОrЯвО GКrЧТЭsв & VЭШrвО GКrЧТЭsв (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К), LЮФШЯвТ CКЩО (2004 Kravchenko, Uotila); RОМСЧШв IsХ (2004 Lindholm PTГ); B. LОХТФ. (2004 Kravchenko); VКЧМСШгОrШ (2006 Talbonen PTГ, 2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013); VОФСФШгОrШ (2012 Kravchenko); UЧТЭsФКвК BКв, SОЯОrЧвТ SШФШХТв IsХ. (2013 Timofeeva). (NШrrХТЧ 1871: VОРШrЮФsК.) – RDB EF: 4, RDB RK: 3 (LC→NT) **Asplenium trichomanes L. – R: МК. 9 ХШМКХТЭТОs AгСОЩЧКЯШХШФ (SЩКrrО 1945); SЯвКЭЮФСК BКв, Zimnaya Mt. (1989 Kravchenko); KШsЦШгОrШ (1999 Timofeeva, Rudkovskaya & Kryshen); V. NТЯК (1999 Timofeeva & Rudkovskaya PTГ); B. LОХТФ. (2004 Kravchenko, Uotila); LКФО Ladmozero (2012 Kravchenko, 2012 Rudkovskaya PTГ); VОФСФШгОrШ (2012 Kravchenko); UЧТЭsФКвК BКв, ЦКТЧХКЧН КЭ SШФШХТв IsХ. (2013 Timofeeva). (Norrlin 1871: Shunga.) Polypodium vulgare L. – Fq. (Norrlin 1871: Stfq–fq.) Picea abies (L.) KКrsЭ. – R. (Norrlin 1871: *Fqq; ТЧМХ. P. × fennica.) P. × fennica (Regel) Kom. (P. abies × obovata) – Fq: the most common taxon of Picea in Zaonezhye and the entire Karelia. P. obovata LОНОЛ. (P. abies sЮЛsЩ. obovata (LОНОЛ.) DШЦТЧ) – Str. (NШrrХТЧ 1871: V. GЮЛК.) Pinus sylvestris L. – Fq. (Norrlin 1871: *Fqq.) Juniperus communis L. – Fq. (Norrlin 1871: *Fqq.) Nuphar lutea (L.) SТЛЭС. & SЦ. – Fq. (Norrlin 1871: Fq.) Nuphar pumila (TТЦЦ) DC. – Str. Nuphar × spenneriana Gaudin (N. lutea × pumila (TТЦЦ) DC.) – R. (NШrrХТЧ 1871: V. GЮЛК.) Nymphaea × borealis Camus (N. alba × candida) – R. Nymphaea candida J. PrОsХ & C. PrОsХ – Fq. (Norrlin 1871: Fq ТЧ V. GЮЛК, Кs N. alba L. s. lat.) Ceratophyllum demersum L. – Rr: Putkozero (Shunga) (1952 Ramenskaya & Zaykova; 2012 Kravchenko); PКНЦШгОrШ (KХвЮФТЧК 1965). (NШrrХТЧ 1871: SСЮЧРК.) a Aconitum × cammarum auct. (A. × stoerkianum KШОХХО) – Rr: V. GЮЛК (2010 Kravchenko); TШХЯЮвК (2011 Timofeeva). 166 Reports of the Finnish Environment Institute 40 | 2014 **Aconitum septentrionale Koelle (A. lycoctonum L. sЮЛsЩ. septentrionale (KШОХХО) KШrsС.)– Fq. (Norrlin 1871: Fq.) **Actaea erythrocarpa (FТsМС.) KШЦ. – Str: Azhepnavolok (1996 Kashtanov); BЮФШХЧТФШЯsФТв IsХ. (1999 Kashtanov); KШХРШsЭrШЯ (1986 Kuznetsov); LКФО CСОХШгОrШ (1999 Rudkovskaya & Timofeeva); MОРШsЭrШЯ IsХ. (2004 Kravchenko); PКХОШsЭrШЯ IsХ. (1999 Kravchenko & Kashtanov); RОМСЧШв IsХ. (2004 Kravchenko); VШХФШsЭrШЯ (1996 Kuznetsov). IЧ МШЦЦЮЧТЭТОs domiЧКЭОН Лв Pinus sylvestris, Picea abies, Alnus incana and A. glutinosa, ЛШЭС ТЧ ШХН-РrШаЭС КЧН ЦТННХО КРОН ПШrОsЭs (ТЧ ЭаШ ХШМКХТЭТОs ЭСО ЦОКsЮrОН КРО ШП ЭrООs аКs МК. 60 вОКrs). Actaea spicata L. – Stfq. (Norrlin 1871: Stfq.) Anemonoides nemorosa (L.) HШХЮЛ (Anemone nemorosa L.) – Str: mainly in Kizhi Skerries КЧН ТЧ ЮЩ ЭШ 5–10 Ц аТНО ЧКrrШа sЭrТЩО КХШЧР ЭСО sСШrОs ШП LКФО OЧОРК. (Norrlin 1871: B. Klim. (Simming, Günther).) a Aquilegia vulgaris L. – Rr: V. GЮЛК (2012 KrКЯМСОЧФШ, ШЛs.). **Atragene sibirica L. (Clematis alpina (L.) MТХХ. sЮЛsЩ. sibirica (MТХХ.) KЮЧЭгО) – R: Kuzaranda (no date Günther H; 1896 Poppius); FШЦТЧШ (1988 Kravchenko; KrКЯМСОЧФШ ОЭ КХ. 2000 К); SЩТrШЯШ (2001 Shelekhov PTГ); RОРТЦКЭФК (2012 Kravchenko); TКЦЛТЭsв – KКsФШsОХga (2013 Syrjänen). CШХХОМЭОН ПrШЦ sОМШЧНКrв ПШrОsЭs НШЦТЧКЭОН Лв МШЧТПОrs Шr КsЩОЧ. TСО sЩОМТОs Тs ПКТrХв МШЦЦШЧ ОКsЭ ШП LКФО OЧОРК, Кs аОХХ Кs ШЧ ТsХКЧНs ЛОЭаООЧ ГКШЧОгСвО КЧН E sСШrО ШП LКФО OЧОРК аСТМС КrО ПШrЦОН ШП ЦШrКТЧО Шr sКЧН НОЩШsТЭs (КХЦШsЭ КХХ ШП ЭСОsО ТsХКЧНs ХТО ШЮЭsТНО ЭСО ГКШЧОгСвО КrО НОХТЦТЭОН СОrО). IЧ KКrОХТК ТЭ Тs ЯОrв rКrО КХsШ ШЧ ЭСО А sСШrОs ШП LКФО OЧОРК, ЛЮЭ ТЧ NNА ЭСО КrОК ОбЭОЧНs ЮЩ ЭШ LКФО SОРШгОrШ (HЮХЭцЧ 1971). – RDB EF: 3 *Batrachium confervoides Fr. (B. eradicatum (LКОsЭ. Об NвЦКЧ) Fr., Ranunculus confervoides (Fr.) Fr., R. eradicatus (LКОsЭ. Об NвЦКЧ) F. JШСКЧsОЧ) – R: PЮЭФШгОrШ (KХвЮФТЧК 1965); Shiltya (1999 Butskikh, Kryshen & Timofeeva; KrКЯМСОЧФШ ОЭ КХ. 2000 К); RШРШsЭrШЯ IsХ. (1999 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); KКгСЦК (2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013). RКrО ЭСrШЮРСШЮЭ KКrОХТК, ЦШrО МШЦЦШЧ ТЧ ЭСО ЧШrЭС-аОsЭОrЧЦШsЭ ЩКrЭ (О.Р. ТЧ ЭСО PККЧКУтrЯТ КrОК). – RDB RK: 3 (LC→NT) Batrachium dichotomum (SМСЦКХС.) TrКЮЭЯ. (Ranunculus peltatus Schranck, s. lat.) – Stfq, especially in Kizhi Skerries. (Norrlin 1871: *Fq.) Caltha palustris L. – Fq. (Norrlin 1871: *Fqq.) a Consolida regalis GrКв – Rr: TШХЯЮвК (GüЧЭСОr 1880; KШrШХОЯК 1927–1928; FКРОrsЭröЦ & LЮЭСОr 1946; 1952 Ramenskaya & Zaykova PTГ, PГV; 1993 Antikainen PTГ); PКНЦШгОrШ (BОгКТs 1911; 1979 Ronkonen.) a Delphinium × cultorum VШss. – R: B. KХТЦ., SОЧЧКвК GЮЛК (1998 Kashtanov; KrКЯМСОЧФШ 2007). *Delphinium elatum L. – Rr: Unitsa (1942 Kalela; HЮХЭцЧ 1971). – RDB EF: 3, RDB RK: 3 (VU) *Ficaria verna (L.) HЮНs. – Rr: B. Klim., Seredka (1988 Kuznetsov; KЮгЧОЭsШЯ 1993). – RDB EF: 3, RDB RK: 3 (LC→NT) a Myosurus minimus L. – Rr: VЭШrвО GКrЧТЭsв (1998 Kashtanov); KЮгКrКЧНК (2004 Kravchenko & Kuznetsov). Ranunculus acris L. – Fq. (Norrlin 1871: *Fqq.) Ranunculus auricomus L. aggr. – Fq. (Norrlin 1871: *Fq.) Ranunculus cassubicus L. aggr. – Rr: B. KХТЦ., LКФО OЛШгОrШ (1997 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); UЧТЭsФКвК BКв, ЦКТЧХКЧН КЭ GКЯШsЭrШЯ IsХ. (2013 Timofeeva). (Norrlin 1871: B. KХТЦ. (KЮХХСОЦ).) – RDB RK: 3 Ranunculus fallax (АТЦЦ. & GrКЛ.) SХШЛШНК КРРr. – Rr: Kizhi (Kuznetsov 1993, no speciЦОЧs КЯКТХКЛХО). Ranunculus lammula L. – R: ЦКТЧХв ТЧ KТгСТ SФОrrТОs. (NШrrХТЧ 1871: SЯвКЭШУЧШs (SТЦЦТЧР); Kizhi (Günther).) Ranunculus lingua L. – Stfq. (NШrrХТЧ 1871: V. GЮЛК stfq; SСЮЧРК.) Ranunculus polyanthemos L. – Stfq. (NШrrХТЧ 1871: ЛОЭаООЧ V. GЮЛК КЧН VОРШrЮФsК.) Ranunculus repens L. – Fq. (Norrlin 1871: Stfq.) Reports of the Finnish Environment Institute 40 | 2014 167 Ranunculus reptans L. – Fq. (Norrlin 1871: *Fq.) Ranunculus sceleratus L. – Stfq. (Norrlin 1871: Stfq.) **Ranunculus subborealis TгЯОХ. (R. acris sЮЛsЩ. borealis (RОРОХ) NвЦКЧ) – Rr: Lipovitsy (2013 Kravchenko). *Thalictrum aquilegiifolium L. – R: KЮгКrКЧНК (HЮХЭцЧ 1971); TШХЯЮвК (HЮХЭцЧ 1971); KrШФСino (1952 Ramenskaya & Zaykova: KrКЯМСОЧФШ ОЭ КХ. 2000 К); ЛОЭаООЧ V. NТЯК КЧН VОРШrЮФsК (1896 Poppius); CСКЩШгОrШ (1896 Poppius); KКгСЦК (2013 Kravchenko); LТЩШЯТЭsв (2013 SвrУтЧОЧ, ШЛs.); TКЦЛТЭsв (2013 SвrУтЧОЧ, ШЛs.). – RDB EF: 3, RDB RK: 3 (NT) Thalictrum lavum L. – Fq. (Norrlin 1871: Fq.) Thalictrum simplex L. – R: SСЮЧРК (NШrrХТЧ 1871); AгСОЩЧКЯШХШФ (SЩКrrО 1945); KЮгКrКЧНК (HЮХЭцЧ 1971); TОХвКЭЧТФШЯШ (KЮгЧОЭsШЯ 1997); KТгСТ (KЮгЧОЭsШЯ 1993; 2007 Znamenskiy PTГ); VШХФШsЭrШЯ (1996 Kuznetsov; KЮгЧОЭsШЯ 1997); RОМСЧШв IsХ. (2004 Kravchenko). – RDB EF: 4 Trollius europaeus L. – Fq. (Norrlin 1871: Fq.) a Chelidonium majus L. – R. Kizhi (Norrlin 1871: Svyatnavolok (Simming, Günther).) a Papaver pseudoorientale (FОННО) MОНа. – Rr: Kizhi (2011 Timofeeva.) a Papaver somniferum L. – Rr: TШХЯЮвК (2011 Timofeeva); V. GЮЛК (2011 Timofeeva); KКгСЦК (2012 Kravchenko). **Corydalis solida (L.) CХКТrЯ. – R: ЦКТЧХв ТЧ KТгСТ SФОrrТОs, KТгСТ КЧН ПОа КНУКМОЧЭ ТsХКЧНs КЧН ЦКТЧХКЧН (KЮгЧОЭsШЯ 1993), Кs аОХХ Кs BОrОгШЯОЭs IsХ. Лв KХТЦ NШs ТЧ ЭСО NШrЭС (1988 Kuznetsov). a FumarТa oficТnalТs L. – Str. (Norrlin 1871: Fq.) *Ulmus glabra HЮНs. – R: TШХЯЮвК (HЮХЭцЧ 1971); LКНЦШгОrШ, SвЩЮЧ GШrК (1989 KrКЯМСОЧФШ, ШЛs.; KrКЯМСОЧФШ ОЭ КХ. 2000 К); OвКЭОЯsЭМСТЧК (1992 Kuznetsov; KЮгЧОЭsШЯ 1993); B. KХТЦ. (HЮХЭцЧ 1971), B. KХТЦ., KШsОХ′РК (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К) КЧН VШrШЛ’Т (2007 Kravchenko); NТгСЧОО MвКРrШгОrШ (2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013); LТЩШЯТЭsв, LКФО BОгНШЧЧШО (2013 Syrjänen). – RDB EF: 3, RDB RK: 3 (LC→NT) *Ulmus laevis PКХХ. – Stfq ШЧ LКФО OЧОРК sСШrОs ТЧ KТгСТ SФОrrТОs (ФЧШаЧ ПrШЦ КЭ ХОКsЭ 30 ХШМКХТЭТОs); ШЮЭsТНО sСШrОs ШЧХв V. NТЯК (HЮХЭцЧ 1971). (NШrrХТЧ 1871: SЯвКЭЧКЯШХШФ (KТгСТ).) – RDB EF: 3, RDB RK: 3 (LC→NT) *aHumulus lupulus L. – Rr: Paleostrov (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3, RDB RK: 3 (NT); МЮХЭТЯКЭОН КЧН ОsМКЩОН ТЧ ЭСО КrОК, КЧН ЭСОsО ШММЮrrences are not protected. Urtica dioica L. – Fq. (Norrlin 1871: Fq.) a Urtica urens L. – Rr, ЭСО ШЧХв rОМОЧЭ rОМШrН: V. GЮЛК (1999 Timofeeva). (Norrlin 1871: *Fq.) Alnus glutinosa (L.) Gaertn. – Stfq. (Norrlin 1871: Fq ТЧ TШХЯЮвК – V. GЮЛК – VОРШrЮФsК КrОК, also Dianova Gora.) Alnus × hybrida Gaertn. (A. × pubescens TКЮsМС) – R. (NШrrХТЧ 1871: V. GЮЛК.) Alnus incana (L.) MШОЧМС – Fq. (Norrlin 1871: *Fqq). VКr. argentata Norrlin (A. argentata (NШrrХ.) TгЯОХ.) НОsМrТЛОН Лв NШrrХТЧ (1871: 168) ШЧ ЭСО ЛКsТs ШП ЭСО ЦКЭОrТКХ МШХХОМЭОН ПrШЦ ЭСО КrОК (SСЮЧРК, AгСОЩЧКЯШХШФ & V. GЮЛК). Betula nana L. – Fq. (Norrlin 1871: *Fq–fqq.) *Betula pendula RШЭС – Fq. (Norrlin 1871: *Fq.) *VКr. karelica (MОrМФХ.) HтЦОЭ-AСЭТ Тs ФЧШаЧ ПrШЦ ЭСО ОЧЭТrО ГКШЧОгСвО (SШФШХШЯ 1950; AЭХКs.., 1973), КЧН ЭСО ЧЮЦЛОr ШП ФЧШаЧ ЭrООs аКs ОsЭТЦКЭОН ЭШ ЛО МК. 3 500 (LКЮr 1997). HШаОЯОr, ЧШаКНКвs ЭСТs rКМО Тs ЮЧНОr ЭСrОКЭ to disappear from the peninsula due to negative ecological and genetic factors and illegal МЮЭЭТЧРs (VОЭМСТЧЧТФШЯК ОЭ КХ. 2013). – RDB RK: 2 (EN) Betula pubescens Ehrh. – Fq. (Norrlin 1871: *Fqq.) Montia fontana L. – Rr, ШЧХв ТЧ KТгСТ SФОrrТОs: BШвКrsЭМСТЧК (KЮгЧОЭsШЯ 1993); B. LОХТФ. (1998 Kashtanov); ГЮЛШЯШ (2012 Kravchenko); PШН’ОХЧТФТ (2012 KrКЯМСОЧФШ, ШЛs.). (NШrrХТЧ 1871: *Stfq–fq.) a Agrostemma githago L. – OЧХв ШХН rОМШrНs: KТгСТ (HЮХЭцЧ 1971). 168 Reports of the Finnish Environment Institute 40 | 2014 Alsine media L. (Stellaria media (L.) CТrТХХШ) – Fq. (Norrlin 1871: *Fqq.) Arenaria serpyllifolia L. – Fq. (Norrlin 1871: Fq.) *Cerastium alpinum L. – Rr: MОХШТРЮЛК (HЮХЭцЧ 1971); B. KХТЦ., SОЧЧКвК GЮЛК (1898 LТЧНrШЭС & CКУКЧНОr) КЧН GrвгЧКЯШХШФ CКЩО (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). (NШrrХТЧ 1871: SСЮЧРК). – RDB RK 3: (NT) Cerastium holosteoides Fr. (C. fontanum BКЮЦР. sЮЛsЩ. vulgare (HКrЭЦ.) GrОЮЭОr & BЮrНОЭ) – Fq. (Norrlin 1871: *Fqq.) Cerastium scandicum (H. GКrЭЧОr) KЮгОЧ. (C. fontanum sЮЛsЩ. fontanum) – R. (Norrlin 1871: AгСОЩЧКЯШХШФ КЧН VОРШrЮФsК; Кs C. alpestre HКrЭЦ.) CoccygantСe los-cuculТ (L.) RМСЛ. (LycСnТs los-cuculТ L.) – Fq. (Norrlin 1871: *Fq–fqq.) *Dianthus arenarius L. s. sЭr. – Rr: B. Lelik., Radkol’e Cape (1988 Kuznetsov: Kuznetsov 1997). – RDB RK: 3 (LC→NT) a Dianthus barbatus L. – R: ПОа rОМШrНs КПЭОr 2007. Dianthus deltoides L. – Fq. (Norrlin 1871: Stfq.) Dianthus superbus L. – Rr: TШХЯЮвК (HЮХЭцЧ 1971). Hylebia nemorum FШЮrr. (Stellaria nemorum L.) – Str. a Melandrium album (Mill.) Garcke (Silene latifolia PШТr. sЮЛsЩ. alba (Mill.) Greuter & BurНОЭ) – Fq. (Norrlin 1871: Fqq.) a Melandrium dioicum (L.) Coss. & Germ. (Silene dioica (L.) CХКТrЯ.) – R: ПОа rОМШrНs КПЭОr 1999. Moehringia trinervia (L.) CХКТrЯ. – Stfq. (NШrrХТЧ 1871: V. GЮЛК.) Myosoton aquaticum (L.) MШОЧМС. – Stfq ТЧ KТгСТ SФОrrТОs: irsЭ rОМШrНОН ПrШЦ KТгСТ IsХ. (1898 Cajander & Lindroth; CКУКЧНОr & LТЧНrШЭС 1900); ЧЮЦОrШЮs rОМОЧЭ МШХХОМЭТШЧs (KЮгЧОЭsШЯ 1997; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3 a Oberna behen (L.) IФШЧЧ. (Silene vulgaris (MШОЧМС) GКrМФО) – Fq. (Norrlin 1871: *Stfq–fq.) a Psammophiliella muralis (L.) IФШЧЧ. (Gypsophila muralis L.) – OЧХв ШХН rОМШrНs: ЛОЭаООЧ TШХЯЮвК КЧН KШsЦШгОrШ (NШrrХТЧ 1871). Sagina nodosa (L.) FОЧгХ – Str. (Norrlin 1871: Stfq ТЧ NE (AгСОЩЧКЯШХШФ – PКНЦШгОrШ).) Sagina procumbens L. – Stfq. (Norrlin 1871: *Fq.) a SaponarТa oficТnalТs L. – Rr, ПОа rОМШrНs КПЭОr 2010. Scleranthus annuus L. – Str. Scleranthus polycarpos L. – Fq. *Silene nutans L. – OЧХв ШХН rОМШrНs: MТгСШsЭrШЯ (BОгКвs 1911); KЮгКrКЧНК (H; BОгКвs 1911); HКrХШЯШ (HЮХЭцЧ 1971). – RDB RK: 3 (LC→NT) a Spergula sativa Boenn. (S. arvensis L. sЮЛsЩ. sativa (MОrЭ. & А. D. J. KШМС) ČОХКФ.) – P. (Norrlin 1871: *Fq, as S. arvensis s. lat.) a Spergularia rubra (L.) J. PrОsХ & C. PrОsХ – P. (Norrlin 1871: Shunga.) Stellaria alsine GrТЦЦ – Rr: KХТЦ NШs КЧН VОРШrЮФsК (HЮХЭцЧ 1971); TЮrКsЭКЦШгОrШ (2012 Kravchenko). Stellaria crassifolia EСrС. – Rr: KКsФШsОХРК (2013 SвrУтЧОЧ, ШЛs.); TКЦЛТЭsв (2013 SвrУтЧОЧ, ШЛs.). Stellaria fennica (MЮrЛ.) PОriХ – R: TТЩТЧТЭsв, VКrЧКЯШХШФ (2004 Piirainen); B. KХТЦ., KШЧНК (2004 Uotila), VШrШЛ’Т (2007 Kravchenko); RОМСФК (2012 Kravchenko); VОrФСЧОО MвКРrШгОrШ (2012 Kravchenko); LКФО RЮРШгОrШ (2013 Kravchenko). Stellaria graminea L. – Fq. (Norrlin 1871: *Fqq.) Stellaria holostea L. – Rr: B. Klim., Klimenitsy (2004 Kravchenko, 2004 Piirainen). Stellaria longifolia MüСХ. Об АТХХН. – Rr: Padmozero (1993 Kravchenko); RОМСЧШв IsХ. (2004 Kravchenko); V. GЮЛК (2013 Kravchenko). Stellaria palustris HШППЦ. – Stfq. Viscaria viscosa (Scop.) Aschers. (Lychnis viscaria L.) – R. a AmarantСus retrolexus L. – Rr: Shunga (2011 Timofeeva). a Atriplex prostrata Boucher ex DC. (A. latifolia АКСХОЧЛ.) – Rr: V. NТЯК (1999 Timofeeva & Rudkovskaya). a Atriplex patula L. – R. a Chenopodium album L. – Fq. (Norrlin 1871: *Fqq; ТЧМХ. C. suecicum.) a Reports of the Finnish Environment Institute 40 | 2014 169 Chenopodium glaucum L. – R. Chenopodium polyspermum L. – R. a Chenopodium suecicum MЮrr – Str. Bistorta oficТnalТs DОХКrЛrО – Str. (NШrrХТЧ 1871: SСЮЧРК, TШХЯЮвК.) Bistorta vivipara (L.) DОХКrЛrО – R. (Norrlin 1871: *Fqq.) a Fallopia convolvulus (L.) Á. LöЯО – Fq. (Norrlin 1871: *Fq.) a Fallopia dumetorum (L.) HШХЮЛ – OЧХв ШХН rОМШrНs: V. GЮЛК (FКРОrsЭröЦ & LЮЭСОr 1946). Persicaria amphibia (L.) GrКв – Fq. (Norrlin 1871: Fqq.) Persicaria hydropiper (L.) SЩКМС – Stfq. (Norrlin 1871: Fq.) Persicaria lapathifolia (L.) GrКв – Str. (Norrlin 1871: Fq.) Persicaria minor (HЮНs.) OЩТг – Fq. (Norrlin 1871: Fq; Кs Polygonum mitis Schrank.). a Persicaria tomentosa (Schrank) Bicknell (Persicaria lapathifolia sЮЛsЩ. pallida (АТЭС.) S. EФЦКЧ & T. KЧЮЭssШЧ) – Fq. (Norrlin 1871: Shunga.) a Polygonum arenastrum Boreau (P. aviculare sЮЛsЩ. microspermum (JШrН. Об BШrОКЮ) BОСОr) – R. a Polygonum aviculare L. – Fq. (Norrlin 1871: *Fqq.) a Rheum rhabarbarum L. – Rr: KТгСТ IsХ. (1998 Kravchenko; KrКЯМСОЧФШ 2007). Rumex acetosa L. – Fq. (Norrlin 1871: *Fqq.) Rumex acetosella L. – Fq. (Norrlin 1871: *Fqq.) Rumex maritimus L. – Rr: ШЧХв ШХН rОМШrНs: V. GЮЛК. – RDB EF: 3 Rumex aquaticus L. – Stfq. (Norrlin 1871: *P.) Rumex crispus L. – R. Rumex fontanopaludosus Kalela (R. acetosa var. fontanopaludosus (KКХОХК) HвХ.) – Rr: Shunga (1942 Kalela). Rumex longifolius DC. – Fq. (Norrlin 1871: *Fqq.) a Rumex obtusifolius L. – Rr: KТгСТ IsХ. (2007 Kravchenko). Rumex pseudonatronatus BШrЛпs – Str. Rumex rossicus MЮrЛ. (Rumex maritimus L. sЮЛsЩ. rossicus (MЮrЛ.) KrвХ.) – Rr: аТЭСШЮЭ ОбКМЭ ХШМКХТЭв (BШrШНТЧК 1977: ЦКЩ; ЧШ ЯШЮМСОr ТЧ LE). Rumex tСyrsТlorus FТЧРОrС. – Stfq. Hypericum maculatum CrКЧЭг – Fq. (Norrlin 1871: *Fq.) *Hypericum perforatum L. – R: ШЧХв ТЧ KТгСТ SФОrrТОs, аСОrО ПШr ЭСО irsЭ ЭТЦО rОМШrНОН КЭ B. KХТЦ., GКrЧТЭsв (FКРОrsЭröЦ & LЮЭСОr 1946); ХКЭОr КХsШ Grвг IsХ. (1988 Kuznetsov; KЮгЧОЭsШЯ 1993; 1999 Kravchenko & Kashtanov); BЮФШХ′ЧТФШЯsФТв IsХ. (1999 Kashtanov); B. LОХТФ IsХ. (2004 Kravchenko H); OrШгС IsХ. (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); ВКЦ IsХ. (1998 Kashtanov). ДErrШЧОШЮsХв ПrШЦ RКНФШХвО IsХ. (KrКЯМСОЧФШ ОЭ КХ. 2000 К).Ж – RDB EF: 3, RDB RK: 3 (LC→NT) Elatine hydropiper L. – Str: V. GЮЛК (1870 Norrlin; NШrrХТЧ 1871; 2000 Timofeeva & Rudkovskaya; 2010 Kravchenko); KКЧОЯ IsХ. (1999 Kashtanov); B. KХТЦ., GКrЧТЭsв BКв (1999 Kravchenko & Kashtanov), KЮrРОЧТЭsв КЧН VШrШЛ’Т (ЛШЭС 2007 Kravchenko); BШХЧТМСЧвТ (2010 Kravchenko); KКгЦК (2012 Kravchenko). *Elatine triandra SМСФЮСr. – Rr: AгСОЩЧКЯШХШФ (SЩКrrО 1945); V. GЮЛК (1870 Norrlin; NШrrХТЧ 1871; 2010 Kravchenko); VОРШrЮФsК КrОК (HЮХЭцЧ 1971). – RDB EF: 3, RDB RK: 3 (VU) a Viola arvensis MЮrrКв – Str. (Norrlin 1871: *Fq.) Viola canina L. – Rr: Mikkovo (1999 Timofeeva, Rudkovskaya & Kryshen); V. GЮЛК (2010 Kravchenko). ДNШrrХТЧ (1871) НТН ЧШЭ sОЩКrКЭО V. canina from V. nemoralis, sОО ЛОХШаЖ. *,**Viola collina BОssОr – Rr: Padmozero (1986 Kuznetsov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3, RDB RK: 3 (LC→NT) Viola epipsila LОНОЛ. – Fq. (Norrlin 1871: *Fq–fqq.) Viola mirabilis L. – Stfq. (Norrlin 1871: *Stfq.) Viola nemoralis Kütz. (V. montana КЮМЭ. ЧШЧ L.) – Fq. (Norrlin 1871: *Fq, as V. lavТcornТs (SЦ.) NШrrХТЧ (1871), Кs аОХХ Кs sОЯОrКХ rОМОЧЭ КЮЭСШrs (О.Р., MКrМЮssОЧ 2010) НШ ЧШЭ sОЩКrКЭО V. nemoralis from V. canina. Viola palustris L. – Fq. (Norrlin 1871: *Fq–fqq.) a a 170 Reports of the Finnish Environment Institute 40 | 2014 Viola rupestris F. А. SМСЦТНЭ – Str. (Norrlin 1871: Fq ТЧ SСЮЧРК КЧН TШХЯЮвК). Viola riviniana RМСЛ. – Fq. (Norrlin 1871: *Fq.) Viola selkirkii PЮrsС Об GШХНТО – Str. (Norrlin 1871: P.) Viola tricolor L. – Fq. (Norrlin 1871: Fq.) *Helianthemum nummularium (L.) Mill. – Rr: B. Lelik., Radkol’e Cape (1988 Kuznetsov; KЮгЧОЭsШЯ 1993, 1997; ЧЮЦОrШЮs rОМОЧЭ sЩОМТЦОЧs ТЧ H КЧН PTГ). OЧХв ШЧО ЦШrО ХШМКХТЭв ТЧ KКrОХТК, КЭ LКФО ВКЧТsвКrЯТ ТЧ Karelia ladogensis. – RDB EF: 2, RDB RK: 2 (EN) Arabidopsis thaliana (L.) HОвЧС. – Stfq. (NШrrХТЧ 1871: SОЧЧКвК GЮЛК (SТЦЦТЧР).) a Armoracia rusticana G. GКОrЭЧ., B. MОв. & SМСОrЛ. – Rr. a Barbarea arcuata (OЩТг Об J. PrОsХ & C. PrОsХ) RМСЛ. (Barbarea vulgaris R. Br. var. arcuata OЩТг Об J. PrОsХ & C. PrОsХ) Fr. – Fq. Barbarea stricta AЧНrг. – Stfq. (Norrlin 1871: *Stfq.) a Brassica campestris L. (B. rapa L. sЮЛsЩ. campestris (L.) A. R. CХКЩСКЦ) – Str. a Bunias orientalis L. – R. a Camelina alyssum (MТХХ.) TСОХХ. – OЧХв ШХН rОМШrНs: stfq in Shunga (Norrlin 1871). a Capsella bursa-pastorТs (L.) MОНТФ. – Fq. (Norrlin 1871: *Fqq.) **Cardamine amara L. – R, ЛЮЭ stfq in Kizhi Skerries. Cardamine dentata Schult. (C. pratensis L. sЮЛsЩ. paludosa (KЧКП) ČОХКФ.) – Fq. (Norrlin 1871: R; SСЮЧРК, V. GЮЛК.) Descurainia sophia (L.) АОЛЛ. Об PrКЧЭХ – R. Draba nemorosa L. – Rr: KЮгКrКЧНК, VТЭsТЧШ (1998 Kravchenko); B. KХТЦ., LШЧРКsв (1987 Kuznetsov); MОРШsЭrШЯ IsХ. (2004 Kravchenko). – RDB EF: 4 a Erophila verna (L.) CСОЯКХХ. – Rr. AгСОЩЧКЯШХШФ (SЩКrrО 1945); KТгСТ КrОК (HЮХЭцЧ 1971). – RDB EF: 3 a Erysimum cheiranthoides L. – Fq. (Norrlin 1871: *Fq.) Erysimum strictum G. GКОrЭЧ., B. MОв. & SМСОrЛ. – Rr: only old records: Shunga (Norrlin 1871); KЮгКrКЧНК (GüЧЭСОr 1880). a Hesperis matronalis L. – Rr. a Lepidium ruderale L. – Rr. a Neslia paniculata (L.) DОsЯ. – OЧХв ШХН rОМШrНs: SСЮЧРК (NШrrХТЧ 1871; GüЧЭСОr 1880). a Raphanus raphanistrum L. – Str. (Norrlin 1871: *Fq.) Rorippa palustris (L.) BОssОr – Fq. (Norrlin 1871: *Fq.) a Sinapis arvensis L. – Rr. Subularia aquatica L. – Str. (Norrlin 1871: Fq ТЧ V. GЮЛК). a Thlaspi arvense L. – Fq. (Norrlin 1871: *Fqq.) a Thlaspi caerulescens J. PrОsХ & C. PrОsХ – Rr: VШХФШsЭrШЯ (1996 Kuznetsov; KЮгЧОЭsШЯ 1997). Turritis glabra L. – P. (Norrlin 1871: P.) a Populus balsamifera L. – Rr: Rechka (2012 Kravchenko). Populus tremula L. – Fq. (Norrlin 1871: *Fqq; МШЩТШsО ТЧ V. GЮЛК – VОРШrЮФsК.) Salix aurita L. – Stfq. (Norrlin 1871: *Stfq–fq.) Salix caprea L. – Fq. (Norrlin 1871: *Fq.) Salix cinerea L. – Fq. (Norrlin 1871: *Fq.) Salix lapponum L. – Str. (NШrrХТЧ 1871: V. GЮЛК – VОРШrЮФsК.) Salix myrsinifolia SКХТsЛ. – Fq. (Norrlin 1871: Fq ТЧ V. GЮЛК.) Salix myrtilloides L. – R. Salix pentandra L. – Fq. (Norrlin 1871: *Fq.) Salix phylicifolia L. – Fq. (Norrlin 1871: *Fq.) Salix rosmarinifolia L. (S. repens L. sЮЛsЩ. rosmarinifolia (L.) AЧНОrssШЧ) – R. (Norrlin 1871: Shunga.) Salix starkeana АТХХН. (S. livida АКСХОЧЛ.) – Str. (Norrlin 1871: *Fq–fqq.) a Salix viminalis L. – Rr. ErЧТЭsФТв IsХ. (1999 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 4 Andromeda polifolia L. – Str. (Norrlin 1871: Fq.) Reports of the Finnish Environment Institute 40 | 2014 171 ArctostapСylos uva-ursТ (L.) SЩrОЧР. – Str. (Norrlin 1871: *Fq.) Calluna vulgaris (L.) HЮХХ. – Fq. (Norrlin 1871: *Fq.) Chamaedaphne calyculata (L.) MШОЧМС. – Fq. (Norrlin 1871: *Fqq.) Ledum palustre L. (Rhododendron tomentosum HКrЦКУК) – Stfq. (Norrlin 1871: Fq ТЧ V. GЮЛК – VОРШrЮФsК.) Oxycoccus microcarpus TЮrМг. Об RЮЩr. (Vaccinium microcarpum (TЮrМг. Об RЮЩr.) SМСЦКХС.) – Rr: ШЧХв iОХН ЧШЭОs, О.Р. LКФО VКЧМСШгОrШ (2012 KrКЯМСОЧФШ, ШЛs.). Oxycoccus palustris Pers. (V. oxycoccos L.) – Stfq. (Norrlin 1871: *Fq– fqq.) Vaccinium myrtillus L. – Fq. (Norrlin 1871: Fqq.) Vaccinium uliginosum L. – Stfq. (Norrlin 1871: Fq ТЧ SА ЩКrЭ.) VaccТnТum vТtТs-Тdaea L. – Fq. (Norrlin 1871: *Fqq.) Moneses unТlora (L.) A. GrКв. – Str. (Norrlin 1871: Str– p.) Orthilia secunda (L.) HШЮsО. – Fq. (Norrlin 1871: *Fq.) Pyrola chlorantha Sа. – R. (Norrlin 1871: *P.) Pyrola minor L. – Stfq. (Norrlin 1871: *Fq.) Pyrola media Sа. – R. Pyrola rotundifolia L. – Fq. (Norrlin 1871: *Fq–fqq.) P. rotundifolia var. chloranthoides NШrrХТЧ (1871:160) аКs НОsМrТЛОН ПrШЦ V. GЮЛК. *Hypopitys monotropa (L.) CrКЧЭг sЮЛsЩ. hypopitys (Monotropa hypopitys L.) – R, mainly in KТгСТ SФОrrТОs: KТгСТ IsХ. (1899 Cajander & Lindroth; CКУКЧНОr & LТЧНrШЭС 1900); KШsЦШгОrШ, GШrsФКвК (1979 RШЧФШЧОЧ, ШЛs.); RКНФШХвО, LвМСФШЯ КЧН EРХШЯ IsХОs (КХХ 1998 Kashtanov); BЮФШХЧТФШЯsФТв КЧН KКХРШЯ IsХОs (ЛШЭС ТЧ 1999 Kashtanov); B. KХТЦ., ErЧТЭsФТв КЧН MвКХ IsХОs (all 1999 Kravchenko & Kashtanov); VОrЭТХШЯШ (1999 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); B. Klim. (2000 Polevoy PTГ); VКЧМСШгОrШ (2004 Talbonen PTГ; KrКЯМСОЧФШ & TТЦШПООЯК 2013); ВЮгСЧвТ OХОЧТв IsХ. (2004 Kravchenko); LТЩШЯТЭsв (2013 Polevoy PTГ); TТЩТЧТЭsв, VКrЧКЯШХШФ (2004 Piirainen). – RDB EF: 3, RDB RK: 3 (LC→NT) Empetrum nigrum L. – R. (Norrlin 1871: *Fq.) PОrСКЩs ШЧХв sЮЛsЩ. hermaphroditum (HКРОrЮЩ) BöМСОr (E. hermaphroditum HКРОrЮЩ) ШММЮrs ТЧ ЭСО КrОК. a Androsace ilТformТs Retz. – R: ПОа rОМШrНs sТЧМО 2010. Lysimachia vulgaris L. – Fq. (Norrlin 1871: *Stfq.) NaumburgТa tСyrsТlora (L.) RМСЛ. (LysТmacСТa tСyrsТlora L.) – Fq. (Norrlin 1871: *Stfq.) Trientalis europaea L. – Fq. (Norrlin 1871: *Fq–fqq.) **Tilia cordata MТХХ. – R, ЛЮЭ fq ТЧ KТгСТ SФОrrТОs. SШЦОЭТЦОs ПШrЦs ЩЮrО sОМШЧНКrв СОrЛ rТМС ПШrОsЭs ШЧ sШЦО ТsХКЧНs ХТФО BОrОгШЯОЭs, DШХРТв, Grвг, KКХРШЯ, UТЦв, ОЭМ. (rОХОЯцs ЩrШЯТНОН Лв KЮгЧОЭsШЯ 1997). AММШrНТЧР ЭШ GüЧЭСОr (1880: 19) ШММЮЩТОs «…КХЦШsЭ КХХ ТsХКЧНs ТЧ LКФО OЧОРК». (NШrrХТЧ 1871: SСЮЧРК.) a Abutilon theophrasti MОНТФ. – Rr: V. GЮЛК (2010 Kravchenko). a Lavatera thuringiaca L. – Rr: V. GЮЛК (2010 Kravchenko); TШХЯЮвК (2011 Timofeeva); Kazhma (2012 Timofeeva). a Malva pusilla SЦ. – OЧХв ШХН rОМШrНs: ЦКТЧХв НЮrТЧР АШrХН АКr II (FКРОrsЭöЦ & LЮЭСОr 1945; HЮХЭцЧ 1971). a Euphorbia helioscopia L. – OЧХв ШХН rОМШrНs: TШХЯЮвК (GüЧЭСОr 1880; KШrШХОЯК 1927–1928). a Euphorbia virgata АКХНsЭ. & KТЭ. (E. esula L. sЮЛsЩ. tommassiniana (BОrЭШХ.) KЮгЦКЧШЯ) – R. **Daphne mezereum L. – Fq. (Norrlin 1871: P.) **Chrysosplenium alternifolium L. – R. (Norrlin 1871: *P.) Saxifraga hirculus L. – Rr: TКЦЛТЭsв – KКsФШsОХРК (2013 Syrjänen). (Norrlin 1871: P.) – RDB EF: 3 Saxifraga nivalis L. – Rr: AгСОЩЧКЯШХШФ (SЩКrrО 1945; 1996 Kashtanov); TОХЩШгОrШ (1952 Ramenskaya & Zaykova; KrКЯМСОЧФШ ОЭ КХ. 2000 К); VОРШrЮФsК, TШХЯЮвК & FОНШЭШЯШ (HЮХЭцЧ 1971, ЛЮЭ ЧШ ЯШЮМСОrs ТЧ H). (NШrrХТЧ 1871: AгСОЩЧКЯШХШФ.) – RDB EF: 3 a Hylotelephium triphyllum (HКа.) HШХЮЛ (Hylotelephium telephium (L.) H. OСЛК, МШХХ.) – Rr: KТгСТ IsХ. (Kravchenko 2007). Sedum acre L. – R. (Norrlin 1871: Fq in Shunga.) 172 Reports of the Finnish Environment Institute 40 | 2014 GrossularТa uva-crТspa (L.) Mill. (RТbes uva-crТspa L.) – Rr: V. GЮЛК (2012 Kravchenko); LКЦЛКsrЮМСОТ (2013 Timofeeva). Ribes nigrum L. – Stfq. (Norrlin 1871: Stfq ТЧ V. GЮЛК.) **Ribes spicatum E. RШЛsШЧ – Fq. (Norrlin 1871: Stfq, as R. rubrum L.) Parnassia palustris L. – Str. (Norrlin 1871: *Fqq.) Drosera anglica HЮНs. – Str. (NШrrХТЧ 1871: ЛОЭаООЧ V. GЮЛК КЧН VОРШrЮФsК.) Drosera rotundifolia L. – Stfq. (Norrlin 1871: *Fq.) a Alchemilla acutiloba OЩТг – Fq. (Norrlin 1871: *Fqq; Кs Alchemilla vulgaris L.) a Alchemilla baltica SКЦ. Об JЮг. – R. a Alchemilla conglobata H. LТЧНЛ. – Rr: Oyatevstchina (2012 Kravchenko). a Alchemilla cymatophylla JЮг. – Rr: Oyatevstchina (2012 Kravchenko). a Alchemilla glaucescens АКХХr. – Stfq. a Alchemilla hirsuticaulis H. LТЧНЛ. – R. a Alchemilla micans BЮsОr – Str. a Alchemilla monticola OЩТг – Fq. a Alchemilla propinqua H. LТЧНЛ. Об JЮг. – Str. a Alchemilla sarmatica JЮг. – R. a Alchemilla subcrenata BЮsОr – Fq. a Cerasus vulgaris Mill. (Prunus cerasus L.) – Rr: ГЮЛШЯШ (2012 Kravchenko); KТгСТ IsХ. (2014 Timofeeva). Comarum palustre L. – Fq. (Norrlin 1871: *Fqq.) Cotoneaster antoninae JЮг. – Str: Kizhi Skerries (1986 Khokhlova; 1988 Kuznetsov; 1999 Kravchenko & Kashtanov) and Kosmozero (1999 Timofeeva et al.; KrКЯМСОЧФШ 2010). – RDB EF: 4 Cotoneaster laxТlorus JКМq. Об LТЧНХ. (C. melanocarpus (BЮЧРО) LШЮНШЧ; C. vulgaris auct. ЧШЧ LТЧНХ.) – P. (NШrrХТЧ 1871: AгСОЩЧКЯШХШФ, SСЮЧРК; МШХХОМЭТЯОХв Кs C. vulgaris). a Crataegus monogyna JКМq. – Rr: Shunga (2012 Kravchenko). Filipendula ulmaria (L.) MКбТЦ. – Fq. (Norrlin 1871: *Fqq.) a Fragaria × ananassa (АОsЭШЧ) DЮМСОsЧО Об RШгТОr – Rr: B. Klim., Klimenitsy (2004 Kravchenko). Fragaria vesca L. – Fq. (Norrlin 1871: *Fqq.) Geum rivale L. – Fq. (Norrlin 1871: Fqq ТЧ SСЮЧРК КЧН V. GЮЛК.) Geum urbanum L. – Stfq. (Norrlin 1871: Shunga.) a Malus domestica BШrФС. – Rr: KТгСТ IsХ. (2014 Timofeeva). Padus avium Mill. (Prunus padus L.) – Fq. (Norrlin 1871: *Fqq.) Potentilla anserina L. – Fq. (Norrlin 1871: Fq.) Potentilla argentea L. – Fq. (NШrrХТЧ 1871: V. GЮЛК, fq in Shunga.) Potentilla erecta (L.) RКОЮsМС. – Fq. (Norrlin 1871: *Fqq.) Potentilla goldbachii (Rupr.) Rupr. (P. thuringiaca sЮЛsЩ. goldbachii (RЮЩr.) TС. АШХП) – Rr: KТгСТ IsХ. (1896 Poppius); TШХЯЮвК (1993 Kravchenko). Potentilla heidenreichii Zimmeter (P. intermedia sЮЛsЩ. heidenreichii (ГТЦЦОЭОr) TгЯОХОЯ) – Rr, only old records: Shunga (Norrlin 1871). Potentilla “impolita” КЮМЭ., ЧШЧ АКСХОЧЛ. – Str. Potentilla intermedia L. – Stfq. (Norrlin 1871: Shunga.) Potentilla norvegica L. – Stfq. (NШrrХТЧ 1871: V. GЮЛК.) **Rosa acicularis LТЧНХ. – Fq. (Norrlin 1871: Fq.) Rosa majalis HОrrЦ. – Fq. (NШrrХТЧ 1871: V. GЮЛК, SСЮЧРК.) Rubus arcticus L. – Str. (NШrrХТЧ 1871: SСЮЧРК, V. GЮЛК.) Rubus chamaemorus L. – Str. (NШrrХТЧ 1871: SШsХКЧШЯЧКЯШХШФ, V. GЮЛК.) **Rubus humulifolius C. A. MОв. – Rr: TШХЯЮвК КЧН KХТЦ NШs (HЮХЭцЧ 1971); UЧТЭsК (1896 Poppius); V. GЮЛК (1896 Poppius); KКsФШsОХРК (2013 SвrУтЧОЧ, ШЛs.); LТЩШЯТЭsв (2013 Kravchenko); PШХвК (2013 SвrУтЧОЧ, ШЛs.); TКЦЛТЭsв (2013 SвrУтЧОЧ, ШЛs.); TТЩТЧТЧТЭsв (2013 SвrУтЧОЧ, ШЛs.); UгФТв SКХЦв (2013 SвrУтЧОЧ, ШЛs.). – RDB EF: 3 Rubus idaeus L. – Fq. (Norrlin 1871: Fqq.) a Reports of the Finnish Environment Institute 40 | 2014 173 Rubus saxatilis L. – Fq. (Norrlin 1871: Fqq.) SanguТsorba oficТnalТs L. – Rr: B. Klim. (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ 2007); TТЩТЧТЭsв (2013 Syrjänen). Sorbus aucuparia L. – Fq. (Norrlin 1871: Fq.) Amoria hybrida (L.) C. Presl (Trifolium hybridum L.) – P. Amoria repens (L.) C. Presl (T. repens L.) – Fq. (Norrlin 1871: Fqq.) Chrysaspis aurea (Pollich) Greene (T. aureum PШХХТМС) – Str. (NШrrХТЧ 1871: V. GЮЛК.) Chrysaspis spadicea (L.) Greene (T. spadiceum L.) – R. (Norrlin 1871: Fq in Shunga.) a Galega orientalis LКЦ. – Rr: V. NТЯК (2011 Timofeeva). Lathyrus aleuticus (GrООЧО) PШЛОН. (L. japonicus АТХХН. ЯКr. aleuticus (HКrЭЦ.) KКrХssШЧ) – Rr: MОРШsЭrШЯ IsХ. (2004 Kravchenko); RОМСЧШТ IsХ. (2004 Piirainen). Lathyrus palustris L. – Stfq. (Norrlin 1871: Shunga.) a Lathyrus pisiformis L. – Rr: KТгСТ IsХ. (2007 Znamenskiy PTГ; KrКЯМСОЧФШ 2007). Lathyrus pratensis L. – Fq. (Norrlin 1871: *Fq.) Lathyrus sylvestris L. – R: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.; HЮХЭцЧ 1971); ЛЮЭ stfq in Kizhi SФОrrТОs: KТгСТ IsХ. (1994 Kuznetsov; KЮгЧОЭsШЯ 1997); KКХРШЯ IsХ. (1999 Kashtanov); BЮФШХ’ЧТФШЯsФТв IsХ. (1999 Kashtanov); ОЭМ. Lathyrus vernus (L.) BОrЧС. – Fq. (Norrlin 1871: *Stfq.) a Lupinus polyphyllus LТЧНХ. – Rr: Pod’elniki (2012 Kravchenko). a Melilotus albus MОНТФ. – Rr: KТгСТ IsХ. (1996 Kuznetsov; KЮгЧОЭsШЯ 1997). a MelТlotus oficТnalТs (L.) LКЦ. – Rr: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1945); KКгСЦК (2012 Kravchenko). a Pisum sativum L. – Rr: Kazhma (2012 Kravchenko & Fadeeva). Trifolium medium L. – Fq. (NШrrХТЧ 1871: V. GЮЛК.) Trifolium pratense L. – Fq. (Norrlin 1871: Fq.) Vicia cracca L. – Fq. (Norrlin 1871: Fqq.) a Vicia hirsuta (L.) GrКв – R. (Norrlin 1871: Fq in Shunga.) a Vicia sativa L. – Rr: Kosmozero (1999 Timofeeva & Rudkovskaya). (Norrlin 1871: Shunga.) Vicia sepium L. – Fq. (Norrlin 1871: *Fq.) Vicia sylvatica L. – Str. (Norrlin 1871: *P.) Vicia tetrasperma (L.) SМСrОЛ. – R. Lythrum salicaria L. – Fq. (Norrlin 1871: Fq.) Peplis portula L. Str. – R: several recent records from B. Klim. (Norrlin 1871: Fq ТЧ V. GЮЛК.) NШЭ rОМШrНОН ПrШЦ V. GЮЛК ТЧ 1999–2013. Chamaenerion angustifolium (L.) Scop. (Epilobium angustifolium L.) – Fq. (Norrlin 1871: *Fqq.) **Circaea alpina L. – Str. (Norrlin 1871: B. Klim.) a Epilobium adenocaulon HКЮssФЧ. – Fq. Epilobium collinum C. C. Gmel. – R. Epilobium montanum L. – Str. (Norrlin 1871: *Stfq–fq.) Epilobium palustre L. – Fq. (Norrlin 1871: Stfq.) a Epilobium pseudorubescens A. Skvorts. (E. ciliatum RКП.) – Rr: V. GЮЛК (2010 Kravchenko); Kazhma (2012 Kravchenko). MyrТopСyllum alternТlorum DC. – Fq. (Norrlin 1871: R in Shunga.) Myriophyllum sibiricum KШЦ. – Str. (Norrlin 1871: Fq; Кs M. spicatum L.) *Myriophyllum verticillatum L. – R: ЛОЭаООЧ TКrШЯsФКвК КЧН BШРШЦШХШЯsФКвК КЧН TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1945); ГСКrЧТФШЯШ (1986 Stoikina PTГ); V. GЮЛК (1999 Butskih, Kryshen & Timofeeva); VШХФШsЭrШЯ (1986 & 1992 Kuznetsov); B. KХТЦ., GКrЧТЭsФКвК BКв (1999 Kravchenko & Kashtanov); OrШгС IsХ. (1999 Kravchenko & Kashtanov); VШгСЦКrТСК RТЯОr (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB RK: 3 (DD) a Acer platanoides L. – Rr: V. GЮЛК (2010 Kravchenko). Linum catharticum L. – Str. (NШrrХТЧ 1871: SСЮЧРК – PКНЦШгОrШ; V. GЮЛК.) Oxalis acetosella L. – Fq. (Norrlin 1871: *Fqq.) 174 Reports of the Finnish Environment Institute 40 | 2014 Erodium cicutarium (L.) L’HОr. – R. (NШrrХТЧ 1871: V. GЮЛК.) Geranium palustre L. – Rr: B. KХТЦ. КrОК (HЮХЭцЧ 1971); RОМСФК (2012 Kravchenko). a Geranium pratense L. – OЧХв ШХН rОМШrНs: SСЮЧРК (NШrrХТЧ 1871). Geranium sylvaticum L. – Fq. (Norrlin 1871: Fqq.) a Impatiens glandulifera Royle – R: ПОа rОМШrНs sТЧМО 2010. Impatiens nolТ-tangere L. – Rr: Putkozerka River (1999 Butskih, Kryshen & Timofeeva); Unitsa (2012 Rudkovskaya). Polygala amarella Crantz – R. a *Polygala comosa SМСФЮСr. – Rr. TШХЯЮвК (1993 Kauhanen PTГ; IЯКЧЭОr & KЮгЧОЭsШЯ 1995). – RDB EF: 1, RDB RK: 3 (VU) Chamaepericlymenum suecicum (L.) AsМС. & GrКОЛЧ. (Cornus suecica L.) – Rr: Lelikozero (1995 Kuznetsov). Aegopodium podagraria L. – Fq. (Norrlin 1871: Fq in Shunga.) a Anethum graveolens L. – Rr: V. GЮЛК (2010 Kravchenko); TШХЯЮвК (2011 Timofeeva); PШХвК (2013 Kravchenko). Angelica sylvestris L. – Fq. (Norrlin 1871: Fq.) Anthriscus sylvestris (L.) HШППЦ. – Fq. (Norrlin 1871: Fq ТЧ V. GЮЛК.) a Carum carvi L. – Fq. (Norrlin 1871: Fqq.) a Chaerophyllum aromaticum L. – Fq КЧН КЛЮЧНКЧЭ ТЧ KТгСТ SФОrrТОs (ШПЭОЧ НШЦТЧКЭОs ТЧ КЛКЧНШЧОН iОХНs): V. NТЯК – CСОХШгОrШ (1999 Butskih, Kryshen & Timofeeva); TШХЯЮвК (HЮХЭцЧ 1971); KЮгКrКЧНК (1988 Kravchenko; KrКЯМСОЧФШ ОЭ КХ. 2000 К); V. GЮЛК (2010 Kravchenko). – RDB EF: 3 a Chaerophyllum prescottii DC. – OЧХв ШХН rОМШrНs: KТгСТ IsХ. (HЮХЭцЧ 1971). Cicuta virosa L. – Fq. (Norrlin 1871: Fq.) Conioselinum tataricum HШППЦ. – Rr, only old records: Unitsa (Norrlin 1871: Rr SТЦЦТЧР); Shunga (1952 Ramenskaya & Zaikova). a Conium maculatum L. – Rr: TШХЯЮвК (2011 Timofeeva); SСЮЧРК КЧН LКФСЧШЯШ (ЛШЭС 2012 Kravchenko). a Eryngium planum L. – OЧХв ШХН rОМШrНs: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946). Heracleum sibiricum L. – Fq. (Norrlin 1871: *Fq–fqq.) a Heracleum sosnowskyi MКЧНОЧ. – Str, ЦКТЧХв ТЧ ЧШrЭСОrЧ ЩКrЭ, КХsШ V. GЮЛК. a Pastinaca sativa L. – Rr: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); SСЮЧРК (2012 Timofeeva). Pimpinella saxifraga L. – Fq. (Norrlin 1871: *Fq.) Sium latifolium L. – R: FОНШЭШЯШ КЧН OвКЭШЯsЭМСТЧК (BОгКТs 1911); V. GЮЛК (2010 Kravchenko). (Norrlin 1871: Fq ТЧ V. GЮЛК.) Thyselium palustre (L.) Raf. (Peucedanum palustre (L.) MШОЧМС). – Fq. (Norrlin 1871: *Fq.) a HТppopСaё rСamnoТdes L. – Rr: TШХЯЮвК (2011 Timofeeva). Frangula alnus Mill. (Rhamnus frangula L.) – Fq. (Norrlin 1871: *Fq.) Galium album Mill. – Fq. (Norrlin 1871: *Fqq, as Galium mollugo L.) Galium boreale L. – Fq. (Norrlin 1871: Fq in Shunga.) Galium elongatum C. Presl (G. palustre L. sЮЛsЩ. elongatum (C. Presl) Lange) – Rr: Lipovitsy КЧН PШХвК (ЛШЭС 2013 Kravchenko). *,** Galium odoratum (L.) SМШЩ. – Rr: B. Klim. (1996 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); B. Lelik. (2004 Kravchenko, Piirainen, Uotila; KrКЯМСОЧФШ 2007); TКЦЛТЭsв (2013 Polevoy PTГ; 2013 Syrjänen). OЮЭsТНО ГКШЧОгСвО ЭСО sЩОМТОs Тs ФЧШаЧ ПrШЦ KКrОХТК, аОsЭ ШП LКФО OЧОРК, ПrШЦ ХОss ЭСКЧ ЭОЧ ХШМКХТЭТОs. – RDB EF: 3, RDB RK: 3 (NT) Galium palustre L. – Fq. (Norrlin 1871: *Fq–fqq.) a Galium ruthenicum АТХХН. – OЧХв ШХН rОМШrНs: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946). Galium trТidum L. – Str. (Norrlin 1871: Fq ТЧ V. GЮЛК.) – RDB EF: 4 **Galium trТlorum Michaux – Str. Galium uliginosum L. – Fq. (Norrlin 1871: *Fqq.) a Galium vaillantii DC. – Str. (Norrlin 1871: *Fq.) a a Reports of the Finnish Environment Institute 40 | 2014 175 Gentianella amarella (L.) BörЧОr – Rr: TШХЯЮвК (1888 KТСХЦКЧ); V. GЮЛК, TКЦЛТЭsв – Kaskoselga (2013 Syrjänen). (NШrrХТЧ 1871: sОО ЛОХШа.) – RDB EF: 4 Gentianella lingulata (C. Agardh) N. M. Pritch. (G. amarella var. lingulata (C. Agardh) KКrХssШЧ) – Stfq. ДNШrrХТЧ (1871) ЭrОКЭОН G. amarella collectively and included f. lingulata; ЭСО ПrОqЮОЧМв ПШr МШХХОМЭТЯО G. amarella is fqЖ. – RDB EF: 3 Menyanthes trifoliata L. – Fq. (Norrlin 1871: Fq). a Sambucus racemosa L. – Rr: VОРШrЮФsК (2013 Kravchenko); LКЦЛКsrЮМСОТ (2013 Timofeeva). **Viburnum opulus L. – Fq. (Norrlin 1871: Fq.) Linnaea borealis L. – Fq. Lonicera pallasii LОНОЛ. (L. caerulea L.) – Stfq. (Norrlin 1871: Fq.) **Lonicera xylosteum L. – Fq. (Norrlin 1871: Soslanovnavolok, Shunga.) Adoxa moschatellina L. – Str. Knautia arvensis (L.) CШЮХЭ. – Fq. (Norrlin 1871: *Fqq). a Calystegia sepium (L.) R. Br. – Rr: V. GЮЛК (2010 Kravchenko); KКгСЦК (2012 Kravchenko). a Calystegia spectabilis (BrЮЦЦТЭЭ) TгЯОХОЯ (C. sepium sЮЛsЩ. spectabilis BrЮЦЦТЭЭ) – Rr: V. GЮЛК (2010 Kravchenko). a Convolvulus arvensis L. – R: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); VОРШrЮФsК (1989 Kravchenko); B. KХТЦ., PОЭrв (1998 Kashtanov), Longasy (1999 Kravchenko & Kashtanov) КЧН VШrШЛ’Т (2007 Kravchenko); V. GЮЛК (2010 Kravchenko). Cuscuta europaea L. – Str. (NШrrХТЧ 1871: V. GЮЛК.) *Polemonium boreale AНКЦs. – Rr: Azhepnavolok (1870 Norrlin; NШrrХТЧ 1871; 1888 KТСlman; 1888 Günther LE; 1896 Poppius; 1907 Bezays & Verdi LE; 1942 Sparre H; SЩКrrО 1945; 1997 Kashtanov; 2001 Kuznetsova PTГ); SСЮЧРК (1979 RШЧФШЧОЧ, ШЛs.; KrКЯМСОЧФШ ОЭ КХ. 2000 К); PКНЦШгОrШ (1870 Norrlin; NШrrХТЧ 1871; 1875 Günther H; 1942 Kalela H; 1999 Kuznetsov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). Polemonium onegense KХШФ. аКs НОsМrТЛОН ШЧ ЭСО ЛКsТs ШП ЭСО ЦКЭОrТКХ МШХХОМЭОН ПrШЦ AгСОЩЧКЯШХШФ Лв BОгКвs КЧН VОrНТ ТЧ 1907 (KХШФШЯ 1955). – RDB EF: 3, RDB RK: 3 (VU) Polemonium caeruleum L. – Stfq. a Buglossoides arvensis (L.) I. M. JШСЧsЭ. (Lithospermum arvense L.) – OЧХв ШХН rОМШrНs: ОЯОrваСОrО (KШrШХОЯК 1927–1928); TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946). (NШrrХТЧ 1871: *Fq). a Cynoglossum oficТnale L. – OЧХв ШХН rОМШrНs: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946), SСЮЧРК (HЮХЭцЧ 1971). a Echium vulgare L. – Rr: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); B. KХТЦ. (1999 Kravchenko & Kashtanov). a Lappula squarrosa (RОЭг.) DЮЦШrЭ – OЧХв ШХН rОМШrНs: TШХЯЮвК (KШrШХОЯК 1927–1928). a Lycopsis arvensis L. (Anchusa arvensis (L.) M. BТОЛ.) – Rr: TШХЯЮвК КЧН KХТЦ NШs, SСТЭТФТ (FКРОrsЭröЦ & LЮЭСОr 1946); VОРШrЮФsК (1989 Kravchenko); B. KХТЦ., LШЧРКsв КЧН PОЭrв (1999 Kravchenko & Kashtanov). a Myosotis arvensis (L.) HТХХ – Fq. (Norrlin 1871: *Stfq–fq.) Myosotis caespitosa Schultz (M. laxa sЮЛsЩ. caespitosa (SМСЮХЭг) NШrНС.) – Str. (Norrlin 1871: *Fq). Myosotis palustris (L.) L. (M. scorpioides L.) – Fq. (Norrlin 1871: *Fq.) a Myosotis sparsТlora J. G. MТФКЧ Об PШСХ – Rr: Ladmozero (2012 Kravchenko). Myosotis stricta Link ex Roem. & Schult. – R. a Nonea rossica Steven (Nonea pulla DC.) – OЧХв ШХН rОМШrНs: AгСОЩЧКЯШХШФ (SЩКrrО 1945). Pulmonaria obscura DЮЦШrЭ. – Rr: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.; HЮХЭцЧ 1971). a Symphytum caucasicum M. BТОЛ. – Rr: KТгСТ IsХ. (2011 Timofeeva); RОМСФК (2012 Kravchenko); LКЦЛКsrЮМСОТ (2013 Timofeeva). a Symphytum asperum L. – Rr: FШТЦШРЮЛК (2013 Timofeeva). Acinos arvensis (Schur) Dandy (Satureja acinos (L.) SМСООХО) – Str. (Norrlin 1871: Padmozero.) Clinopodium vulgare L. – Fq. *Dracocephalum ruyschiana L. – R, mainly in Kizhi Skerries: Kosmozero (1896 Poppius); B. KХТЦ., SОЧЧКвК GЮЛК (1898 Cajander & Lindroth), Pervye Garnitsy (1998 Kashtanov; 176 Reports of the Finnish Environment Institute 40 | 2014 1998 Potakhin PTГ) КЧН GrвгЧКЯШХШФ CКЩО (1999 Kravchenko & Kashtanov); TШХЯЮвК КЧН SСЮЧРК (HЮХЭцЧ 1971); FШЦТЧШ (1988 KrКЯМСОЧФШ, ШЛs.); RКНФШХвО КЧН RОМСЧШТ IsХОs (1988 Kuznetsov; KЮгЧОЭsШЯ 1993); Grвг IsХ. (1992 Kuznetsov; KЮгЧОЭsШЯ 1993; 1999 Kravchenko & Kashtanov); OrШгС КЧН ВКЦ IsХОs (1998 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); LКЦЛКгЧТФ IsХ. (1999 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); PКХОШsЭrШЯ IsХ. (1999 Kravchenko & Kashtanov, 2004 Kravchenko); B. LОХТФ., RКНФШХ’О CКЩО (2004 Kravchenko, Kuznetsov & Gnatyuk, Piirainen). – RDB RK: 3 (LC→NT) a Dracocephalum tСymТlorum L. – Rr: KТгСТ КrОК (HЮХЭцЧ 1971); MОРШsЭrШЯ IsХ. (2004 Kravchenko). Galeopsis bТida BШОЧЧ. – Fq. a Galeopsis ladanum L. – Rr, the only recent record: Paleostrov (2001 Kuznetsova PTГ). (Norrlin 1871: *Fq.) a Galeopsis speciosa MТХХ. – Fq. (Norrlin 1871: *Fq.) a Galeopsis tetrahit L. – Fq. (Norrlin 1871: *Fq; G. bТida included.) Glechoma hederacea L. – Str, mainly in Kizhi Skerries. (Norrlin 1871: Svyatoinos (Simming, KЮХХСОЦ) КЧН KТгСТ “МШЩТШsО” (GüЧЭСОr).) a Lamium amplexicaule L. – OЧХв ШХН rОМШrНs: SСЮЧРК КЧН PКНЦШгОrШ (NШrrХТЧ 1871). a Lamium confertum Fr. – Rr: Kuzaranda (1888 Kihlman; MОЧЧОЦК 1989; 2004 Kravchenko & Kuznetsov). a Lamium dissectum АТЭС. (L. hybridum VТХХ.) – Str. a Lamium purpureum L. (L. purpureum var. incisum (АТХХН.) PОrs.) – Stfq. (Norrlin 1871: Fq.) a Leonurus villosus Desf. ex d’Urv. (L. cardiaca L. sЮЛsЩ. villosus (DОsП. Об Н’UrЯ.) HвХ.) – Rr: TШХЯЮвК (2011 Timofeeva); TТЩТЧТЭsв (2013 Timofeeva). Lycopus europaeus L. – Fq. (Norrlin 1871: Shunga.) Mentha arvensis L. – Fq. (Norrlin 1871: *Fq.) a Mentha × dalmatica TКЮsМС – Rr: V. GЮЛК (2010 Kravchenko); SСЮЧРК (2012 Kravchenko). a Mentha longifolia (L.) HЮНs. – Rr: V. GЮЛК (2010 Kravchenko). *Origanum vulgare L. – R, ЦКТЧХв ТЧ KТгСТ SФОrrТОs: B. KХТЦ., SОЧЧКвК GЮЛК (1898 Cajander & Lindroth; CКУКЧНОr & LТЧНrШЭС 1900), GrвгЧКЯШХШФ CКЩО, KШsОХРК КЧН PОЭrв (КХХ 1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); RКНФШХвО IsХ. (1898 Cajander & Lindroth; 1988 Kuznetsov; KЮгЧОЭsШЯ 1993; 1998 Kashtanov); PКХОШsЭrШЯ IsХ. (1979 Ronkonen PTГ; 1999 Kravchenko& Kashtanov); RОМСЧШТ IsХ. (1988 Khokhlova PTГ); OrШгС IsХ. (1998 Kashtanov; 1999 Kravchenko & Kashtanov); Grвг IsХ. (1999 Kravchenko & Kashtanov); KКХРШЯ, KШЧОЯ, LКЦЛКгЧТФ, RШРШsЭrШЯ КЧН BЮФШХЧТФШЯsФТв IsХОs (КХХ ТЧ 1999 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); ВЮгСЧвТ OХОЧТв IsХ. (1988 Kuznetsov; 1999 Kravchenko & Kashtanov; 2004 Gnatyuk & Kryshen). – RDB EF: 3, RDB RK: 3 (LC→NT) Prunella vulgaris L. – Fq. (Norrlin 1871: *Fq.) Scutellaria galericulata L. – Fq. (Norrlin 1871: *Fq.) Stachys palustris L. – Fq. (Norrlin 1871: Fq, Unitsa.) Stachys sylvatica L. – R. Thymus serpyllum L. – Str. (Norrlin 1871: Fq in Shunga.) *Thymus subarcticus KХШФ. ОЭ SСШsЭ. – Rr: B. Lelik., Radkol’e Cape (1988 Kuznetsov; Kuznetsov 1993, 1997). – RDB EF: 2, RDB RK: 3 (LC→NT) Callitriche cophocarpa Sendtn. – Rr: B. Klim., Petry (1999 Kravchenko & Kashtanov); SСТХЭвК – PЮЭФШгОrФК RТЯОr (1999 Timofeeva & Rudkovskaya); LКНЦШгОrШ (2012 Kravchenko). Callitriche hermaphroditica L. – Rr: UЧТЭsК (HЮХЭцЧ 1971); SСЮЧРК – PЮЭФШгОrШ (HЮХЭцЧ 1971; 1952 Ramenskaya & Zaikova PГV & PTГ; 2012 Kravchenko); B. KХТЦ., GКrЧТЭsФКвК GЮЛК Bay and Longasy (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); V. GЮЛК (1999 Timofeeva & Rudkovskaya; 2010 Kravchenko); KКгСЦК (2012 Kravchenko). – RDB EF: 3 Callitriche palustris L. – Fq. (Norrlin 1871: *Fq?) a Hyoscyamus niger L. – OЧХв ШХН rОМШrНs: PКХОШsЭrШЯ (GüЧЭСОr 1880; KШrШХОЯК 1927–1928); TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946). a Lycopersicon esculentum Mill. – Rr: V. GЮЛК (2010 Kravchenko); KТгСТ IsХ. (2011 Timofeeva). Reports of the Finnish Environment Institute 40 | 2014 177 Solanum dulcamara L. – Str: mainly Kizhi Skerries. a Solanum tuberosum L. – Rr: V. GЮЛК (2010 Kravchenko). Euphrasia brevipila Burn. & Gremli (E. sricta J. F. LОСЦ. ЯКr. stricta) – Fq. Euphrasia hirtella auct. (E. rostkoviana HКвЧО sЮЛsЩ. fennica (KТСХЦ.) KКrХssШЧ) – Str. EupСrasТa oficТnalТs L. s. ХКЭ. – Rr: V. NТЯК (1999 Timofeeva & Rudkovskaya). (Norrlin 1871: *Fq–fqq.) Euphrasia onegensis A. CКУКЧНОr – ?Rr: TШХЯЮвК (sвЧЭвЩЮs ТЧ H). EupСrasТa parvТlora JЮг. (E. nemorosa (PОrs.) АКХХr.) – Stfq. Euphrasia vernalis List (E. stricta J. P. АШХПП Об J. F. LОСЦ. ЯКr. tenuis (BrОЧЧОr) JКХКs) – Str. Limosella aquatica L. –R: V. NТЯК (HЮХЭцЧ 1971); KТгСТ КrОК (HЮХЭцЧ 1971); KКгСЦК (2012 Kravchenko). (NШrrХТЧ 1871: V. GЮЛК.) – RDB EF: 4 Linaria vulgaris Mill. – Fq. (Norrlin 1871: Stfq.) * Melampyrum cristatum L. – OЧХв ШХН rОМШrНs: ЛОЭаООЧ KЮгКrКЧНК КЧН PКНЦШгОrШ (1874 Günther H; HЮХЭцЧ 1971). – RDB EF: 3, RDB RK: 2 (EN) Melampyrum nemorosum L. – Str. Melampyrum pratense L. – Fq. (Norrlin 1871: Fq.) Melampyrum sylvaticum L. – Fq. (Norrlin 1871: *Fqq.) a Odontites vulgaris Moench – Str. (Norrlin 1871: Fq in Shunga.) Pedicularis palustris L. – Fq. (Norrlin 1871: *Fqq.) Pseudolysimachion longifolium (L.) Opiz (Veronica longifolia L.) – Fq. (Norrlin 1871: Fq.) Pseudolysimachion maritimum (L.) Á. LöЯО &. D. LöЯО (Veronica longifolia var. maritima (L.) HКrЭЦ. – Rr: B. Klim. and Paleostrov (Kravchenko 2007). *Pseudolysimachion spicatum (L.) Opiz (Veronica spicata L.) – R: Kosmozero (1896 Poppius); B. KХТЦ., SОЧЧКвК GЮЛК (1898 Cajander & Lindroth; CКУКЧНОr & LТЧНrШЭС 1900); B. ГКrОЯШ КЧН PШвКХТЭsТЧsФКвК (ЛШЭС 1943 Fagerström H; FКРОrsЭröЦ & LЮЭСОr 1946); TОХЩШгОro (1952 Ramenskaya & Zaykova); FШЦТЧШ (1988 KrКЯМСОЧФШ, ШЛs.); ГТЦЧвКв MЭ. (1988 Kravchenko); SЯвКЭЮСК BКв (1999 Butskih, Kryshen & Timofeeva; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3, RDB RK: 3 (NT) Rhinanthus minor L. – Fq. (Norrlin 1871: *Fqq.) Rhinanthus serotinus (SМСöЧС.) OЛШrЧý – Fq. (Norrlin 1871: Fqq.) Scrophularia nodosa L. – Str. (NШrrХТЧ 1871: SСЮЧРК, V. GЮЛК.) a Verbascum nigrum L. – Str. (NШrrХТЧ 1871: ЛОЭаООЧ V. GЮЛК КЧН KШsЦШгОrШ, fq ТЧ V. GЮЛК.) Verbascum thapsus L. – Str. Veronica arvensis L. – Str. Veronica chamaedrys L. – Fq. (Norrlin 1871: *Fqq.) VeronТca oficТnalТs L. – Fq. (Norrlin 1871: *Fq.) a Veronica persica Poir. – Rr: V. GЮЛК (2010 Kravchenko). Veronica scutellata L. – Str. (NШrrХТЧ 1871: V. GЮЛК; SСЮЧРК (Кs ЯКr. villosa L.) Veronica serpyllifolia L. – Fq. (Norrlin 1871: *Fqq.) Veronica verna L. – Str. (Norrlin 1871: Fq.) *LТttorella unТlora (L.) Asch. – Rr: VОРШrЮФsК (2013 Kravchenko). – RDB RF: 2, RDB EF: 2, RDB RK: 2 (EN) Plantago lanceolata L. – Stfq: ОsЩОМТКХХв ТЧ KТгСТ SФОrrТОs. (NШrrХТЧ 1871: KТгСТ IsХ. (GüЧЭСОr).) Plantago major L. – Fq. (Norrlin 1871: *Fqq.) Plantago media L. – Str. (NШrrХТЧ 1871: TШХЯЮвК.) Pinguicula vulgaris L. – Str. (Norrlin 1871: Fq in the north.) Utricularia intermedia HКвЧО – Str. (Norrlin 1871: Fq.) Utricularia minor L. – R. Utricularia vulgaris L. – Stfq (Norrlin 1871: Stfq.) Hippuris vulgaris L. – Str. (Norrlin 1871: Shunga.) Campanula cervicaria L. – R: B. KХТЦ., KЮгЧОЭsв; KКХРШsЭrШЯ IsХ.; KЮгКrКЧНК КЧН TОХвКЭЧТФШЯШ (КХХ BОгКвs 1911); V. GЮЛК (1942/1943 KЮУКХК, ШЛs.); PОrРЮЛК КrОК КЧН V. GЮЛК (HЮХЭцЧ 1971); B. KХТЦ., MОНЯОгСТК GШrК (1997 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); ВЮгСЧвТ OХОЧТв 178 Reports of the Finnish Environment Institute 40 | 2014 (2004 PТТrКТЧОЧ, ШЛs.); LТsТЭsТЧШ (2004 PТТrКТЧОЧ, ШЛs.). (NШrrХТЧ 1871: DТКЧШЯК GШrК.) – RDB EF: 3, RDB RK: 3 (LC→NT) Campanula glomerata L. – Fq. (Norrlin 1871: Fq.) *,**Campanula latifolia L. – R: TТЩТЧТЭsв, VКrЧКЯШХШФ (2004 Kravchenko); OвКЭОЯsЭМСТЧК (2011 escaped Timofeeva & Nikolaeva PTГ; TТЦШПООЯК & NТФШХКОЯК 2012); LТЩШЯТЭsв, TКЦЛТЭsв КЧН TТЩТЧТЭsв (2013 SвrУтЧОЧ, ШЛs.). – RDB EF: 4, RDB RK: 3 (LC→NT) Campanula patula L. – Fq. (Norrlin 1871: *Fq–fqq.) Campanula persicifolia L. – Stfq. (Norrlin 1871: Fq.) Campanula rapunculoides L. – Stfq. (Norrlin 1871: Fq.) Campanula rotundifolia L. – Fq. (Norrlin 1871: Fq.) *Lobelia dortmanna L. – Stfq, ОsЩОМТКХХв ТЧ KТгСТ SФОrrТОs. SЩОМТОs Тs ФЧШаЧ ПrШЦ МК 25 localities. (Norrlin 1871: P.) – RDB RF: 3, RDB RK: 3 (LC→NT) Achillea millefolium L. – Fq. (Norrlin 1871: *Fqq.) a Achillea nobilis L. – Rr: PrвКХТМСТЧsФКвК (FКРОrsЭröЦ & LЮЭСОr 1946); V. GЮЛК (RКЦОЧsФКвК 1983, ЧШ ЯШЮМСОrs КЯКТХКЛХО) Antennaria dioica (L.) GКОrЭЧ. – Fq. (Norrlin 1871: *Fqq.) a Anthemis arvensis L. – R. (NШrrХТЧ 1871: V. GЮЛК.) a Anthemis tinctoria L. – OЧХв ШХН rОМШrНs: V. GЮЛК (NШrrХТЧ 1871); OвКЭОЯsЭМСТЧК (BОгКТs 1911); KТгС IsХ., TШХЯЮвК КЧН V. GЮЛК (FКРОrsЭröЦ & LЮЭСОr 1946). a Arctium minus (HТХХ) BОrЧС. – Rr: V. GЮЛК (2010 Kravchenko). (Norrlin 1871: Shunga, stfq ТЧ V. GЮЛК.) a Arctium tomentosum MТХХ. – Stfq. (Norrlin 1871: Stfq in Shunga.) a Artemisia absinthium L. – Rr: TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); V. GЮЛК (2010 Kravchenko). a Artemisia rupestris L. – OЧХв ШХН rОМШrНs: SСЮЧРК (FКРОrsЭröЦ & LЮЭСОr 1946). a Artemisia vulgaris L. – Stfq. (NШrrХТЧ 1871: V. GЮЛК КЧН fq ТЧ TШХЯЮвК.) a Aster novТ-belgТТ L. – Rr: V. GЮЛК (2010 Kravchenko). a Aster salignus АТХХН. – Rr: V. GЮЛК (2010 Kravchenko). Bidens cernua L. – Str: mainly in Kizhi Skerries. (Norrlin 1871: Fq ТЧ V. GЮЛК.) Bidens radiata TСЮТХХ. – R. Bidens tripartita L. – Fq. (Norrlin 1871: Fq.) a Calendula oficТnalТs L. – Rr: Kazhma (2012 Kravchenko). a Carduus crispus L. – Str. (Norrlin 1871: Fq.) Centaurea jacea L. – Fq. (Norrlin 1871: Fqq in Shunga.) Centaurea phrygia L. – Fq. (Norrlin 1871: Fq–fqq.) Centaurea scabiosa L. – Stfq. (Norrlin 1871: Fq.) a Cichorium intybus L. – OЧХв ШХН rОМШrНs: SСЮЧРК КЧН V. GЮЛК (FКРОrsЭröЦ & LЮЭСОr 1946). a Cirsium arvense L. (C. arvense var. arvense) – Rr: V. GЮЛК (2010 Kravchenko). Cirsium heterophyllum (L.) HТХХ. – Fq. (Norrlin 1871: *Fq.) Cirsium oleraceum (L.) SМШЩ. – Str. Cirsium palustre (L.) SМШЩ.– Stfq. (Norrlin 1871: *Fq.) a Cirsium setosum (АТХХН.) BОssОr (C. arvense var. mite (АТЦЦ. & GrКЛ.) LКЧРО) – Fq. (Norrlin 1871: *Fqq; Кs Cirsium arvense L. s. lat.) a Cirsium vulgare (SКЯТ) TОЧ. – P. (Norrlin 1871: Shunga and fq ТЧ V. GЮЛК.) a Conyza canadensis (L.) CrШЧq. (Erigeron canadensis L.) – Rr: V. GЮЛК (2010 Kravchenko); Kazhma (2012 Kravchenko). Crepis biennis L. – Str: irsЭ rОМШrНОН ПrШЦ TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); rОМОЧЭ rОМШrНs ПrШЦ МК. 15 ЩХКМОs ТЧ ЦОКНШаs, rШКНsТНОs, iОХНs КЧН sСШrОs. – RDB EF: 4 Crepis paludosa (L.) MШОЧМС – P. (NШrrХТЧ 1871: V. GЮЛК.) Crepis tectorum L. – R. (Norrlin 1871: *Fq.) a Cyanus segetum (L.) HТХХ (Centaurea cyanus L.) – R. (Norrlin 1871: *Fq.) Erigeron acris L. – Fq. (Norrlin 1871: *Fq.) Erigeron uralensis Less. (E. acris sЮЛsЩ. brachycephalus (H. LТЧНЛ.) HТТЭШЧОЧ) – Str. Reports of the Finnish Environment Institute 40 | 2014 179 *Eupatorium cannabinum L. – Str: KТгСТ IsХ. КЧН SОЧЧКвК GЮЛК (ЛШЭС ТЧ 1898 Cajander & Lindroth; CКУКЧНОr & LТЧНrШЭС 1900) КЧН МК. 25 rОМОЧЭ rОМШrНs, ЦКТЧХв ПrШЦ KТгСТ SФОrrТОs. – RDB EF: 3, RDB RK: 3 (LC→NT) Gnaphalium uliginosum L. – Fq. (Norrlin 1871: *Fq.) a Helianthus tuberosus L. – Rr: V. NТЯК (2011 Timofeeva); SСЮЧРК (2012 Kravchenko). HТeracТum caesТТlorum AХЦq. Об NШrrХ. (H. subcaesium КЮМЭ.) – PКХОШsЭrШЯ (2004 Uotila); Kizhi (1898 Liro & Cajander). Hieracium chlorelliceps NШrrХ. Об оФsТЩ – SОЧЧКвК GЮЛК (1898 Liro & Cajander). Hieracium coronarium Brenner (H. adunans NШrrХ.) – KТгСТ (1898 Liro & Cajander). Hieracium diaphanoides LТЧНОЛ. – B. LОХТФ., RКНФШХ’О (2004 Uotila). Hieracium distendens Brenner (H. fenno-orbТcans NШrrХ.) – SОЧЧКвК GЮЛК (1898 Liro & Cajander). Hieracium incurrens NШrrХ. – B. LОХТФ., RКНФШХ’О (2004 Uotila). Hieracium karelorum (Norrl.) Norrl. (H. multiglandulosum оФsТЩ; H. prenanthoides auct.) – Str. VКrЧКЯШХШФ (2004 Kravchenko & Piirainen); B. KХТЦ., OЛШгОrШ (1999 Kravchenko & Kashtanov); ЩrШЛКЛХв КХsШ ПrШЦ UгФКвК SКХЦК (2013 Kravchenko), Uimy isles (1986 Khokhlova), ЦКТЧХКЧН Лв KКХРШЯ IsХ. (1986 Kuznetsov), Klimenitsy (2004 Kravchenko), VШrШЛ’Т (2007 Kravchenko). TСОrО КrО ЦШrО, вОЭ ЮЧНОsМrТЛОН ЭКбК ШП H. sect. Prenanthoidea KШМС, аСТМС are found in Azhepnavolok (1870 Norrlin) and Shunga (Norrlin 1871, as H. prenanthoides) and Nizhnee Myagrozero (2002 Kravchenko). Hieracium laeticolor (AХЦq.) LöЧЧr. (H. prolixiforme NШrrХ.) – KТгСТ (1898 Liro & Cajander); SОЧЧКвК GЮЛК (1898 Liro & Cajander); PКХОШsЭrШЯ (2004 Uotila). Hieracium oistophyllum Pugsl. (H. sagittatum (LТЧНОЛ.) NШrrХ.) – LКФО KШsЦШгОrШ (1996 Poppius). Hieracium pruiniferum (NШrrХ.) NШrrХ. – B. KХТЦ. (1997 Kashtanov). Hieracium ravidum Brenner (H. galbanum (DКСХsЭ.) BrОЧЧОr) – KТгСТ (1898 Liro & Cajander); SОЧЧКвК GЮЛК (1898 Liro & Cajander); PКХОШsЭrШЯ (2004 Uotila). Hieracium sagittipotens NШrrХ. – SОЧЧКвК GЮЛК (1898 Liro & Cajander). Hieracium tenuiglandulosum NШrrХ. – B. LОХТФ. (2001 Kuznetsova PTГ). Hieracium umbellatum L. – Fqq. (Norrlin 1871: *Fqq.) a Inula britannica L. – OЧХв ШХН rОМШrНs: PrвКХТМСТЧsФКвК (FКРОrsЭröЦ & LЮЭСОr 1946). Inula salicina L. – Rr: Ladmozero (2012 Kravchenko). – RDB EF: 3 a Lapsana communis L. – R. (Norrlin 1871: *Stfq–fq.) Leontodon autumnalis L. – Fq. (Norrlin 1871: *Fq–fqq.) Leontodon hispidus L. – Str. (NШrrХТЧ 1871: BОЭаООЧ TШХЯЮвК КЧН V. GЮЛК.) a Lepidotheca suaveolens (Pursh) Nutt. (Matricaria discoidea DC., M. matricarioides КЮМЭ.) – Fq. Leucanthemum ircutianum TЮrМг. Об DC. (L. vulgare L.) – Fq. (Norrlin 1871: *Fqq.) Ligularia sibirica (L.) CКss. – R. (Norrlin 1871: Unitsa (Simming).) a Logia arvensТs (L.) HШХЮЛ (Filago arvensis L.) – Rr: V. GЮЛК (2010 Kravchenko). a Matricaria recutita L. (M. chamomilla L.) – Rr: V. GЮЛК (2010 Kravchenko). Mulgedium sibirum (L.) Cass. ex Less. (Lactuca sibirica (L.) MКбТЦ.) – Str. (Norrlin 1871: Str ТЧ V. GЮЛК.) Omalotheca sylvatica (L.) SМС. BТЩ. & F. А. SМСЮХЭг (Gnaphalium sylvaticum L.) – Fq. (Norrlin 1871: * Fq–fqq.) **Petasites frigidus (L.) Fr. – R: KЮгКrКЧНК (HЮХЭцЧ 1971); LКФО KШЩКЧОЭг (1999 Kravchenko & Kashtanov); RвКЛШЯШ (2010 Kravchenko); VОrФСЧОО MвКРrШгОrШ (2012 Kravchenko); Lipovitsy and Uzkie Salmy (2013 Kravchenko); TТЩТЧТЭsв (2013 SвrУтЧОЧ, ШЛs.). (NШrrХТЧ 1871: SСЮЧРК – TШХЯЮвК.) Picris hieracioides L. – Str. (Norrlin 1871: Str.) Pilosella × cymТlora (NтРОХТ & PОЭОr) S.BrтЮЭ. & GrОЮЭОr (HТeracТum cymТlorum NтРОХТ & PОЭОr; H. conferciens NШrrХ.; P. oficТnarum < P. pubescens) – KТгСТ (1898 Liro & Cajander); SОЧЧКвК GЮЛК (1898 Liro & Cajander). Hieracium conferciens NШrrХ. (1904) аКs НОsМrТЛОН ШЧ ЭСО ЛКsТs ШП ЭСО МТЭОН МШХХОМЭТШЧs ПrШЦ KТгСТ КЧН SОЧЧКвК GЮЛК. 180 Reports of the Finnish Environment Institute 40 | 2014 Pilosella × fallacina (F.А.SМСЮХЭг) F.А.SМСЮХЭг (Hieracium fallacinum F.А.SМСЮХЭг; Pilosella oficТnarum × Pilosella praealta × Pilosella pubescens) – SОЧЧКвК GЮЛК (1898 Liro & Cajander). Pilosella × lagellarТs (АТХХН.) ArЯ.-TШЮЯ. (HТeracТum lagellare АТХХН.; PТlosella oficТnarum > Pilosella onegensis) – SОЧЧКвК GЮЛК (1898 Liro & Cajander); ЩrШЛКЛХв КХsШ KКХРШЯ IsХ. (1986 Kuznetsov). PТlosella lorТbunda (АТЦЦ. & GrКЛ.) Fr. (P. suecica (Fr.) F. SМСЮХЭг & SМС. BТЩ., P. fennica (Norrl.) Norrl., Hieracium lorТbundum АТЦЦ. & GrКЛ., H. suecicum Fr., H. fennicum (NШrrХ.) MОХК) – Stfq: SОЧЧКвК GЮЛК (1898 Liro & Cajander), VШХФШsЭrШЯ IsХ. (1986 Kuznetsov). (Norrlin 1871: *Stfq–fq.) Pilosella × glomerata (FrШОХ.) Fr. (Hieracium glomeratum FrШОХ.; P. pubescens × P. onegensis) – B. KХТЦ. (1997 Kashtanov; 2004 Piirainen); SОЧЧКвК GЮЛК (1898 Liro & Cajander). PТlosella oficТnarum F. SМСЮХЭг & SМС. BТЩ. (Hieracium pilosella L.) – Stfq: Kizhi (1898 Liro & Cajander); SОЧЧКвК GЮЛК (1898 Liro & Cajander); RКНФШХвО IsХ. (1988 Kuznetsov); Pod’elniki (2012 Kravchenko). (Norrlin 1871: *Fq–fqq.) Pilosella onegensis Norrl. (Hieracium onegense (NШrrХ.) NШrrХ.; H. caespitosum КЮМЭ.) – Stfq. NШЭ НШМЮЦОЧЭОН Лв sЩОМТЦОЧs. TСТs sЩОМТОs Тs rКЭСОr МШЦЦШЧ ТЧ Kon (Norrlin 1871: *Stfq; Кs H. caespitosum) ТЧ sЩТЭО ШП ЭСО КЛsОЧМО ШП ЩrОsОrЯОН sЩОМТЦОЧs ПrШЦ ГКШЧОгСТО. Pilosella peleteriana (Mцr.) F. SМСЮХЭг & SМС. BТЩ. (Hieracium peleterianum Mцr.) – Rr: SОЧЧКвК GЮЛК (1898 Liro & Cajander). Pilosella pubescens Norrl. (Hieracium pubescens HОХХsЭr.; H. cymosum auct., H. vaillantii КЮМЭ.) – Stfq: SОЧЧКвК GЮЛК (1898 Liro & Cajander); VШХФШsЭrШЯ (1986 Kuznetsov); KТгСТ (1986 Kuznetsov). (Norrlin 1871: *Fq.) Ptarmica cartilaginea (LОНОЛ. Об RМСЛ.) LОНОЛ. (Achillea salicifolia BОssОr) – Rr: Shunga (Putkozero) (Norrlin 1871, 1979 Ronkonen, 2012 Kravchenko); КХХ rОМШrНs ПrШЦ sСШrОs ШП the same lake. Ptarmica vulgaris HТХХ (Achillea ptarmica L.) – Rr: V. NТЯК (1999 Timofeeva & Rudkovskaya); V. GЮЛК (2010 Kravchenko). Saussurea alpina L. – Rr: FОНШЭШЯШ (BОгКТs 1911); TШХЯЮвК (FКРОrsЭröЦ & LЮЭСОr 1946); Karasozero (1999 Kuznetsov); TТЩТЧТЭsв – KКsФШsОХРК (2013 Syrjänen). a Senecio vulgaris L. – Str. Solidago virgaurea L. – Fq. (Norrlin 1871: Fq ЛОЭаООЧ V. GЮЛК КЧН VОРШrЮФsК.) a Sonchus arvensis L. – Str. (Norrlin 1871: *Fqq.) a Sonchus asper (L.) HТХХ – R. (NШrrХТЧ 1871: SСЮЧРК КЧН V. GЮЛК.) a Sonchus oleraceus L. – R. (NШrrХТЧ 1871: ТЧ ЭСО аСШХО ГКШЧОгСвО PОЧТЧsЮХК.) Tanacetum vulgare L. – Fq. (Norrlin 1871: Str, ЛЮЭ fq ТЧ V. GЮЛК; UЧТЭsК (KЮХХСОЦ).) Taraxacum oficТnale АТРР. МШХХ. – Fq. (Norrlin 1871: *Fq.) Tripleurospermum inodorum (L.) SМС. BТЩ. – Fq. (Norrlin 1871: *Fqq.) Trommsdorfia maculata (L.) Bernh. (Hypochaeris maculata L.) – Stfq. (NШrrХТЧ 1871: V. GЮЛК.) Tussilago farfara L. – Fq. (Norrlin 1871: *P.) Paris quadrifolia L. – Fq. (Norrlin 1871: Fq ТЧ V. GЮЛК.) Convallaria majalis L. – Fq. (Norrlin 1871: Fq.) Maianthemum bifolium (L.) F. А. SМСЦТНЭ – Fq. (Norrlin 1871: *Fqq.) Polygonatum odoratum (MТХХ.) DrЮМО – Str. (Norrlin 1871: Azhepnavolok and near Shunga.) Allium oleraceum L. – Str: ШЧХв ТЧ KТгСТ SФОrrТОs, irsЭ rОМШrН КЭ KТгСТ IsХ. (1995 Heikkilä PTГ; KЮгЧОЭsШЯ 1997); КХsШ OrШгС IsХ. (1998 Kashtanov); KКХРШЯ IsХ. (1999 Kashtanov); МК. 10 localities after 1997 at B. Klim. Allium schoenoprasum L. – Rr: MвsС’Т IsХОs (1986 Khokhlova PTГ); IгЛЮsСОМСЧвТ IsХ. (1988 Kravchenko); SОЯОrЧвТ MвsСТв IsХ. (1988 Kuznetsov); B. KХТЦ., IХКТЧКЯШХШФ (1997 Kashtanov), Pervye Garnitsy (1998 Kashtanov) and Lukova Bay (2004 Kravchenko, Piirainen, Uotila); B. Lelik. (2001 Kuznetsova). a Asparagus oficТnalТs L. – Rr: Rechka (2012 Kravchenko). Reports of the Finnish Environment Institute 40 | 2014 181 Gagea minima (L.) KОr GКаХ. – Rr: KТгСТ IsХ. (HЮХЭцЧ 1971; 1986 Drozdova; KЮгЧОЭsШЯ 1993; 1998 Kravchenko, 1999 Znamenskiy, 2003 Kravchenko & Kuznetsov); ЛОЭаООЧ TОХТКЭЧТФШЯШ and Zharnikovo (1986 Drozdova; KЮгЧОЭsШЯ 1993); KХТЦ NШs (2001 Shelekhov). Iris pseudacorus L. – Stfq. (NШrrХТЧ 1871: V. GЮЛК.) Coeloglossum viride (L.) HКrЭЦ. – Str: mainly in Kizhi Skerries. (Norrlin 1871: *P–stfq.) CorallorСТza trТida CСсЭОХ. – R. (Norrlin 1871: *Fq.) *,**Cypripedium calceolus L. – R: KЮгКrКЧНК (GüЧЭСОr 1880); ВЮгСЧвТ OХОЧТв IsХ. (1896 Poppius); LКЦЛКsrЮМСОв (HЮХЭцЧ 1971); ГКРШrsФШО LКФО (1952 Ramenskaya & Zaykova). VКЛХШФ IsХ. (1988 Kuznetsov; KЮгЧОЭsШЯ 1993); KКТЧШs IsХ. (KЮгЧОЭsШЯ & KСШФСХШЯК 1994); B. KХТЦ., IХКТЧКЯШХШФ CКЩО (1997 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К) КЧН KЮrРОЧТЭsв (MКrФШЯsФКвК ОЭ КХ. 2007); RОМСЧШТ IsХ. (2004 PТТrКТЧОЧ, ШЛs.); MОРШsЭrШЯ (2004 Kravchenko H, PTГ); TТЩТЧТЭsв (2004 PТТrКТЧОЧ & UШЭТХК, ШЛs., 2013 SвrУтЧОЧ, ШЛs.); KКsФШsОХРК (2013 TТФФКЧОЧ, ШЛs.); TЮrКsЭКЦШгОrШ (2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013). – RDB EF 4, RDB RF 3, RDB RK 3 (LC→NT). *Dactylorhiza cruenta (O. F. MЮОХХ.) SШя (Dactylorhiza incarnata sЮЛsЩ. cruenta (O. F. MüХХ.) Nyman) – Rr, ШЧХв ШХН rОМШrНs: AгСОЩЧКЯШХШФ (SЩКrrО 1945); TШХЯЮвК (HЮХЭцЧ 1971). – RDB EF 3, RDB RK 3 (NT) Dactylorhiza fuchsii (DrЮМО) SШя – Stfq. Dactylorhiza incarnata (L.) SШя – Str. (Norrlin 1871: *Stfq–fq.) Dactylorhiza maculata (L.) SШя – Fq. (Norrlin 1871: *Fq; ТЧМХ. D. fuchsii.) *Dactylorhiza traunsteineri (SКЮЭ. Об RМСЛ.) SШя s. ХКЭ. – R: V. GЮЛК (1896 Poppius, 2013 Kravchenko); LКЦЛКsrЮМСОв (1907 Bezays & Verdi; BОгКвs 1911); UЧТЭsК (HЮХЭцЧ 1971); PЮЭФШгОrШ (1952 RКЦОЧsФКвК, ШЛs.); PКХЭОРК (1999 Butskih, Kryshen & Timofeeva); OвКЭОЯsЭМСТЧК (KЮгЧОЭsШЯ 1993; KЮгЧОЭsШЯ ОЭ КХ. 1999; 2012 Kravchenko); KЮгКrКЧНК, TТЩТЧТЭsв (2004 Kravchenko); B. KХТЦ., SЭМСЮМСТК BКв (MКrФШЯsФКвК ОЭ. КХ. 2007); TЮrКsЭКЦШгОrШ (2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013); PШХвК (2013 Kravchenko). (Norrlin 1871: *Stfq, as var. curvifolia NвХ.) – RDB RF: 3, RDB RK: 3 (LC→NT) Epipactis helleborine (L.) CrКЧЭг – Str. (Norrlin 1871: Unitsa.) *Epipactis palustris (L.) CrКЧЭг – R: AгСОЩЧКЯШХШФ (SЩКrrО 1945; 1997 Kashtanov); TОХpozero (1952 Ramenskaya & Zaykova; 1979 Ronkonen); LКФО ГКРШrsФШО (1952 Ramenskaya & Zaykova); SСЮЧРК (HЮХЭцЧ 1971); PТРЦК MТrО (1980 Elina, Antipin & Kuzmina PTГ; KЮгЧОЭsШЯ ОЭ КХ. 2013); LКФО PКНЦШгОrШ (1986 Kuznetsov); LКЦЛКsrЮМСОв, KКХОРЮЛsФШО Mire (1991 Dyachkova PTГ); LКФО KКrКsШгОrШ (1999 Kuznetsov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); KЮгКrКЧНК (2004 Kravchenko & Kuznetsov, 2004 Piirainen, 2004 Uotila); GТгСШгОrШ (MКrФШЯsФКвК ОЭ КХ. 2007; 2012 Timofeeva; KrКЯМСОЧФШ & TТЦШПООЯК 2013). – RDB EF: 3, RDB RK: 3 (LC→NT) Goodyera repens (L.) R. Br. – R. (Norrlin 1871: Unitsa (Kullhem).) Gymnadenia conopsea (L.) R. Br. – Stfq. (Norrlin 1871: *Fqq.) Hammarbya paludosa (L.) O. KЮЧЭгО – Str. **Listera cordata (L.) R. Br. – Str. (Norrlin 1871: *Fq.) Listera ovata (L.) R. Br. – Stfq. (Norrlin 1871: *Fq–fqq.) *Malaxis monophyllos (L.) Sа. – Str: ЛОЭаООЧ TКrШЯsФКвК КЧН BШРШЦШХШЯsФКвК (FКРОrsЭröЦ & LЮЭСОr 1946); FОНШЭШЯШ (HЮХЭцЧ 1971); TОХвКЭЧТФШЯШ (1987 Stoykina); LТМСФШЯ IsХ. (1998 Kashtanov); PКХОШsЭrШЯ IsХ. (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); SЯвatukha Bay (1999 Butskih, Kryshen & Timofeeva; KrКЯМСОЧФШ ОЭ КХ. 2000 К); KЮгКrКЧНК (2004 Kravchenko & Kuznetsov, Piirainen); SСЮЧОЯsФТв IsХ. (MКrФШЯsФКвК ОЭ. КХ. 2007); V. GЮЛК (2010 Kravchenko); TЮrКsЭКЦШгОrШ (2012 Kravchenko; KrКЯМСОЧФШ & TТЦШПООЯК 2013); ЛОЭаООЧ PШН’ОХЧТФТ КЧН ГЮЛШЯШ (2012 Kravchenko); PШХвК (2013 Kravchenko). (Norrlin 1871: *P.) – RDB EF: 2, RDB RK: 3 (LC→NT) *,**NeottТa nТdus-avТs (L.) RТМС. – Str, only in Kizhi Skerries: Boyarstchina and Zharnikovo (ЛШЭС 1986 Drozdova PГV); TОХвКЭЧТФШЯШ, KЮsСЧКЯШХШФ (KЮгЧОЭsШЯ & KСШФСХШЯК 1994); B. Klim., Klimenitsy (1997 Kashtanov), Pervye Garnitsy (1998 Kashtanov), Gryznavolok Cape (1999 Kravchenko & Kashtanov), Koselga (1999 Kravchenko & Kashtanov) КЧН VШrШЛ’Т 182 Reports of the Finnish Environment Institute 40 | 2014 (2007 Kravchenko); Grвг IsХ. (1999 Kravchenko & Kashtanov); MвКХ’ IsХ. (1999 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); ВЮгСЧвТ OХОЧТв IsХ. (2004 Kravchenko); B. LОХТФ., Radkol’e Cape (2004 Kravchenko & Kuznetsov); DШХРТв IsХ. (MКrФШЯsФКвК ОЭ КХ. 2007); TКЦЛТЭsв (2013 Syrjänen); TТЩТЧТЭвs (2013 SвrУтЧОЧ, ШЛs.). – RDB EF: 3, RDB RK: 3 (LC→NT) Platanthera bifolia (L.) RТМС. – Stfq. (Norrlin 1871: *Fq.) Calla palustris L. – Stfq. (Norrlin 1871: Fq.) Lemna minor L. – Stfq. (Norrlin 1871: Shunga and fq ТЧ V. GЮЛК.) Lemna trisulca L. – Str. (NШrrХТЧ 1871: V. GЮЛК КЧН fq in Shunga.) Spirodela polyrhiza (L.) SМСХОТН. – Rr: MОХШТРЮЛК (2013 Timofeeva). Butomus umbellatus L. – Str. AlТsma plantago-aquatТca L. – Fq. (Norrlin 1871: Fq.) Sagittaria × lunata C. D. Preston & Uotila (S. natans × sagittifolia) – Rr: B. Klim., Pervye Garnitsy (1998 Kashtanov) and KЮЦЮsС GЮЛК (1999 Kravchenko & Kashtanov). Sagittaria natans PКХХ. – Rr: Shunga (1896 Poppius); KШsЦШгОrШ, PКНЦШгОrШ КЧН PЮЭФШгОrШ (Shunga) (Klyukina 1965, no vouchers). Sagittaria sagittifolia L. – Str. (Norrlin 1871: Fqq ТЧ V. GЮЛК.) ᵃElodea canadensТs MТМСб. – Str. HydrocСarТs morsus-ranae L. – Str. (NШrrХТЧ 1871: DТКЧШЯК GШrК (SТЦЦТЧР); UЧТЭгК (KЮХХСОЦ); sООЧ ТЧ sОЯОrКХ ХШМКХТЭТОs ТЧ ЭСО аСШХО ГКЧШЧОгСвО PОЧТЧsЮХК.) Stratiotes aloides L. – Str. (Norrlin 1871: Fq ТЧ ЭСО ЧШrЭСОrЧ ЩКrЭ; V. GЮЛК.) Scheuchzeria palustris L. – R. (Norrlin 1871: *Stfq.) Triglochin palustris L. – R. (Norrlin 1871: Fq.) Potamogeton alpinus BКХЛ. – Fq. (Norrlin 1871: *Many localities.) Potamogeton × angustifolius J. PrОsХ (P. gramineus × lucens) – Rr: Regimatka (2012 Kravchenko). Potamogeton berchtoldii FТОЛОr – Str. (Norrlin 1871: *Stfq; Кs P. pusillus L.) Potamogeton compressus L. – R. (Norrlin 1871: Fq in Shunga.) Potamogeton ilТformТs Pers. (StuckenТa ilТformТs (PОrs.) BörЧОr) – Rr: Putkozero (Klyukina 1965); B. KХТЦ., GКrЧТЭsФКвК GЮЛК BКв (1998 Kashtanov; Kravchenko et al. 2000 a). (Norrlin 1871: SСЮЧРК.) – RDB EF: 4 *Potamogeton friesii RЮЩr. – Rr, only old records, all from Lake Putkozero (Shunga) (1888 Kihlman; Kihlman 1888, 1890; 1896 Poppius; KХвЮФТЧК 1965). – RDB EF: 4, RDB RK: 3 (NT) Potamogeton gramineus L. – Fq. (Norrlin 1871: *Fq.) Potamogeton lucens L. – Fq. (Norrlin 1871: Fqq.) Potamogeton natans L. – Fq. (Norrlin 1871: *Fq.) Potamogeton obtusifolius MОrЭ. & А. D. J. KШМС – R. (NШrrХТЧ 1871: SЮsХШЧШЯ NКЯШХШФ КЧН V. GЮЛК.) Potamogeton perfoliatus L. – Fq. (Norrlin 1871: *Fq.) Potamogeton praelongus АЮХПОЧ – Rr: VКХРШЦШгОrШ, LКФОs KШsЦШгОrШ КЧН PЮЭФШгОrШ (KХвЮФТЧК 1965; ЧШ ЯШЮМСОrs); KШЧНШгОrШ (2012 Timofeeva). *Potamogeton rutilus АШХПР. – Rr: only old records, all from Lake Putkozero (Shunga) (1870 Norrlin; NШrrХТЧ 1871 (fq ТЧ SСЮЧРК); 1888 Kihlman; Kihlman 1888, 1890; 1896 Poppius). – RDB EF: 3, RDB RK: 3 (NT) *CaulТnТa lexТlТs АТХХН. (Najas lexТlТs (АТХХН.) RШsЭФ. & А. L. E. SМСЦТНЭ) – Rr: V. GЮЛК (1870 Norrlin; NШrrХТЧ 1871; GüЧЭСОr 1880; 1943 Luther; LЮЭСОr 1945; FКРОrsЭröЦ & LЮЭСОr 1946); KТгСТ IsХ., НrТПЭОН (KЮгЧОЭsШЯ 1993). TСО sОМШЧН rОМШrН ШП Caulinia from Karelia is also from Kon, ПrШЦ LКФО PвКХШгОrШ (LЮЭСОr 1945). – RDB EF: 1. RDB RF: 2, RDB RK: 1 (CR) Sparganium angustifolium MТМСб. – Str. (Norrlin 1871: Shunga.) Sparganium emersum RОСЦКЧЧ – Str. (NШrrХТЧ 1871: V. GЮЛК КЧН fq in Shunga.) Sparganium glomeratum BОЮrХ. – Rr: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.); TШХЯЮвК КЧН V. NТЯК (HЮХЭцЧ 1971); AгСОЩЧКЯШХШФ (1996 Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3 Sparganium gramineum GОШrРТ – Rr, ШЧХв ШХН rОМШrНs: KТгСТ КrОК КЧН B. KХТЦ. (HЮХЭцЧ 1971). Reports of the Finnish Environment Institute 40 | 2014 183 Sparganium microcarpum (NОЮЦ.) ČОХКФ. – Rr: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.); KЮгКrКЧНК (HЮХЭцЧ 1971); TШХЯЮвК (1993 Kravchenko); MвКХ’ IsХ. (1999 Kravchenko & Kashtanov). (Norrlin 1871: Shunga, as S. ramosum HЮНs., ЧШЦ. ТХХОР. = S. erectum L., s. lat.) Sparganium natans L. (S. minimum АКХХr.) – Stfq. (Norrlin 1871: Fq.) Typha angustifolia L. – Rr: SСЮЧРК (GüЧЭСОr 1880); V. GЮЛК (GüЧЭСОr 1880; 1999 Timofeeva & Rudkovskaya; 2010 Kravchenko); VОРШrЮФsК (2013 Kravchenko). (Norrlin 1871: Shunga.) Typha latifolia L. – Str: irsЭ rОМШrНs ПrШЦ GКЯШsЭrШЯ IsХ. ТЧ UЧТЭsК BКв (1988 KrКЯМСОЧФШ, ШЛs.) КЧН AгСОЩЧКЯШХШФ (1996 Kashtanov). Juncus alpinoarticulatus CСКТб – Fq. (Norrlin 1871: *Stfq–fq, as J. nodulosus = J. alpinoarticulatus s.lat.) Juncus articulatus L. – Stfq. (Norrlin 1871: *Fq.) Juncus bufonius L. – Str. (Norrlin 1871: *Fq.) Juncus bulbosus L. – Rr: Rechka (2012). Juncus compressus JКМq. – Stfq. (NШrrХТЧ 1871: V. GЮЛК КЧН fq in Shunga.) Juncus conglomeratus L. – R. Juncus effusus L. – Str. Juncus ilТformТs L. – Fq. (Norrlin 1871: *Fqq.) Juncus iscСerТanus TЮrМг. Об V. I. KrОМг. (J. alpinoarticulatus sЮЛsЩ. iscСerТanus TЮrМг. Об V. I. KrОМг.) HтЦОЭ-AСЭТ) – Rr: VШrШЛ’Т (2007 Kravchenko). Juncus minutulus (AХЛОrЭ & JКСКЧН.) PrКТЧ (J. bufonius sЮЛsЩ. minutulus (AХЛОrЭ & JКСКЧН.) SяШ, ЧШЦ. ТХХОР.) – Rr: VКЧМСШгОrШ (2012 Kravchenko). Juncus nodulosus АКСХОЧЛ. (J. alpinoarticulatus sЮЛsЩ. rarТlorus (HКrЭЦ.) HШХЮЛ) – Str. (Norrlin 1871, see under J. alpinoarticulatus.) Juncus ranarius SШЧРОШЧ & E. P. PОrrТОr – Rr: SОЧЧКвК GЮЛК (1898 Liro & Cajander). Juncus stygius L. – Rr. (Norrlin 1871: Unitsa.) Luzula multТlora (EСrС.) LОУ. – Fq. (Norrlin 1871: *Fq.) Luzula pallescens Sа. – Fq. (Norrlin 1871: *Fqq.) Luzula pilosa (L.) АТХХН. – Fq. (Norrlin 1871: *Fqq.) Carex acuta L. – Fq. (Norrlin 1871: *Fq.) Carex appropinquata Schumach. – Rr: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.); B. KХТЦ., KШsОХРК (1999 Kravchenko & Kashtanov); RОМСЧШв IsХ. (2004 Piirainen H, PTГ); LТЩШЯТЭsв, TКЦЛТЭsв КЧН TТЩТЧТЭsв (2013 SвrУтЧОЧ, ШЛs.). Carex aquatilis АКСХОЧЛ. – R: V. GЮЛК КЧН UsЭ’-ВКЧНШЦК (1942/1943 KЮУКХК, ШЛs.); ШЛsОrЯКЭТШЧs ПrШЦ sОЯОrКХ ЩШТЧЭs, ЛЮЭ ЧШ ЯШЮМСОrs. Carex atherodes Spreng. – Rr: Kosmozero (1896 Poppius; HЮХЭцЧ 1971); ОrrШЧОШЮsХв rОЩШrЭОН ПШr KТгСТ IsХ. (KЮгЧОЭsШЯ 1993; sОО KrКЯМСОЧФШ ОЭ КХ. 2000 К). – RDB EF: 3 Carex brunnescens (PОrs.) PШТr. – Str. Carex buxbaumii АКСХОЧЛ. – Str. (Norrlin 1871: Shunga.) Carex canescens L. – Fq. (Norrlin 1871: *Fqq.) Carex capillaris L. – R. (Norrlin 1871: B. Klim. (Simming).) Carex cespitosa L. – Fq. (Norrlin 1871: *Fqq.) Carex chordorrhiza L. П. – Stfq. (Norrlin 1871: *Fqq.) Carex diandra SМСrКЧФ – Stfq. (Norrlin 1871: *Fqq.) Carex digitata L. – Stfq. (NШrrХТЧ 1871: V. GЮЛК.) Carex dioica L. – Stfq. (Norrlin 1871: Fqq.) **Carex disperma DОаОв – Str. (Norrlin 1871: *P.) Carex echinata MЮrrКв – Str. (Norrlin 1871: *Fq.) Carex elongata L. – Fq. (Norrlin 1871: *Fq.) Carex ericetorum PШХХТМС – Rr, ШЧХв ШХН rОМШrНs: SСЮЧРК КЧН VОРШrЮФsК (HЮХЭцЧ 1971). Carex lava L. – Fq. (Norrlin 1871: Fqq.) Carex globularis L. – Str. (Norrlin 1871: Fq.) Carex heleonastes L. f. – Rr: Karasozero (1995 Kuznetsov); ЛОЭаООЧ ГСКrЧТФШЯШ КЧН PШН’ОХniki (1996 Kuznetsov; KЮгЧОЭsШЯ 1997; KЮгЧОЭsШЯ ОЭ КХ. 1999); B. KХТЦ., KШsОХРК (1999 184 Reports of the Finnish Environment Institute 40 | 2014 Kravchenko & Kashtanov; KrКЯМСОЧФШ ОЭ КХ. 2000 К); TЮrКsЭКЦШгОrШ (2012 Kravchenko). – RDB EF: 4 Carex juncella (Fr.) TС. Fr. (C. nigra sЮЛsЩ. juncella Fr.) – Stfq. (Norrlin 1871: *Fq.) Carex lasiocarpa EСrС. – Fq. (Norrlin 1871: *Fq.) Carex leporina L. – Fq. (Norrlin 1871: *Fq.) Carex limosa L. – Stfq. (Norrlin 1871: *Fqq.) Carex livida (АКСХОЧЛ.) АТХХН. – Rr: Unitsa (1870 Norrlin: NШrrХТЧ 1871); BШвКrsЭМСТЧК (1986 Stoykina; KЮгЧОЭsШЯ 1993; KЮгЧОЭsШЯ ОЭ КХ. 1999); UгФТО (2005 Antipin); OвКЭОЯsЭМСТЧК КЧН TЮrКsЭКЦШгОrШ (ЛШЭС 2012 Kravchenko). **Carex loliacea L. – Str. (Norrlin 1871: *P–stfq.) *Carex muricata L. – Str: V. GЮЛК, UsЭУКЧЧШУО (1943 KЮУКХК, ШЛs.; HЮХЭцЧ 1971; 2012 Kravchenko); ЧЮЦОrШЮs rОМОЧЭ rОМШrНs ПrШЦ KТгСТ SФОrrТОs (KЮгЧОЭsШЯ 1997; ВЮНТЧК 1999; KrКЯМСОЧФШ ОЭ КХ. 2000 К; MШrШгШЯК ОЭ КХ. 2010), КХsШ TТЩТЧТЭsв (2004 Kravchenko & Piirainen H, PTГ). – RDB EF: 3, RDB RK: 3 (LC→NT) Carex nigra (L.) RОТМСКrН. – Fq. (Norrlin 1871: *Fqq.) Carex omskiana Meinsh. (C. elata AХХ. sЮЛsЩ. omskiana (MОТЧsС.) JКХКs) – Str. (Norrlin 1871: V. GЮЛК КЧН fq in Shunga.) Carex pallescens L. – Fq. (Norrlin 1871: *Fq.) Carex panicea L. – Str. (Norrlin 1871: *Fq.) Carex paucТlora LТРСЭП. – Str. (Norrlin 1871: *Fq.) Carex paupercula Michx. (C. magellanica LКЦ. sЮЛsЩ. irrigua (АКСХОЧЛ.) HТТЭШЧОЧ) – Fq. (Norrlin 1871: *Fqq.) Carex pseudocyperus L. – Rr: SСЮЧОЯsФТв IsХ. (2010 DОЦОЧЭТОЯК, ШЛs.: MШrШгШЯК ОЭ КХ. 2010). – RDB RK: 3 (LC→NT) Carex rhynchophysa FТsМС., C. A. MОв. & AЯц-LКХХ. – Str. (Norrlin 1871: *P.) *Carex riparia CЮrЭТs – Rr: TКЦЛТЭsв (2013 SвrУтЧОЧ, ШЛs.); ЯОrв rКrО sЩОМТОs ТЧ KКrОХТК, аСОrО ФЧШаЧ ШЧХв ТЧ 3 ШЭСОr ХШМКХТЭТОs. – RDB EF: 2, RDB RK: 3 (VU) Carex rostrata SЭШФОs – Fq. (Norrlin 1871: *Fqq.) Carex scandinavica E. А. DКЯТОs (C. viridula Michx. var. pulchella (LöЧЧr.) B. SМСЦТН) – Str. – RDB EF: 3 Carex serotina MцrКЭ (C. viridula var. viridula) – P. (Norrlin 1871: Fq ТЧ SСЮЧРК; ТЧМХ. C. scandinavica.) **Carex tenuТlora АКСХОЧЛ. – Rr: VОФСФШгОrШ (2012 Kravchenko). – RDB EF: 3 Carex vaginata TКЮsМС – Stfq. (Norrlin 1871: Stfq–fq.) Carex vesicaria L. – Fq. (Norrlin 1871: *Fq.) Eleocharis acicularis (L.) RШОЦ. & SМСЮХЭ. – P. (Norrlin 1871: *Fq.) Eleocharis mamillata (H. LТЧНЛ.) H. LТЧНЛ. – Rr: TШХЯЮвК КЧН KХТЦ NШs – OФСТsОЯsФКвК (FКРОrsЭröЦ & LЮЭСОr 1946); VШrШЛ’Т (2007 Kravchenko). Eleocharis palustris (L.) R. Br. – Stfq. (Norrlin 1871: *Fq.) EleocСarТs quТnquelora (HКrЭЦКЧЧ) O. SМСаКrг – Str. (Norrlin 1871: Fq in Shunga.) Eleocharis uniglumis (LТЧФ.) SМСЮХЭ. – Rr: SСЮЧРК (HЮХЭцЧ 1971). TСТs Тs ЭСО ШЧХв rОМШrН ПrШЦ LКФО OЧОРК, ЛЮЭ ЭСО sЩОМТОs Тs ФЧШаЧ ПrШЦ LКФО VШНХШгОrШ, ОКsЭ ШП LКФО OЧОРК. Eriophorum angustifolium HШЧМФ. (E. polystachyon L. ЧШЦ. rОУ.) – Stfq. (Norrlin 1871: *Fqq.) Eriophorum gracile А. D. J. KШМС Об RШЭС – Str. (Norrlin 1871: Shunga.) Eriophorum latifolium HШЩЩО – Str. (Norrlin 1871: Shunga, fq ЛОЭаООЧ TШХЯЮвК КЧН V. GЮЛК.) Eriophorum vaginatum L. – Stfq. (Norrlin 1871: *Fqq.) Rhynchospora alba (L.) VКСХ – Str. (NШrrХТЧ 1871: ЛОЭаООЧ KШsЦШгОrШ КЧН V. GЮЛК.) Schoenoplectus lacustris (L.) Palla (Scirpus lacustris L.) – Fq. (Norrlin 1871: Fqq.) Scirpus sylvaticus L. – Fq. (Norrlin 1871: *Stfq–fq.) Trichophorum alpinum (L.) PОrs. – Str. (Norrlin 1871: *Fqq.) Trichophorum cespitosum (L.) HКrЭЦ. – R. Agrostis canina L. – Fq. (Norrlin 1871: *Fqq.) Agrostis capillaris L. (A. tenuis SТЛЭС.). – Fq. (Norrlin 1871: *Fqq.) Reports of the Finnish Environment Institute 40 | 2014 185 Agrostis gigantea Roth – Rr: КММШrНТЧР ЭШ KЮгЧОЭsШЯ (1993) ОЯОrваСОrО ТЧ KТгСТ SФОrrТОs, ЭСО ПrОqЮОЧМв ШЛЯТШЮsХв ШЯОrОsЭТЦКЭОН; V. GЮЛК (2012 Kravchenko). Agrostis stolonifera L. – P. (Norrlin 1871: shores of Lake Onega.) Alopecurus aequalis SШЛШХ. – Fq. (Norrlin 1871: *Fq.) Alopecurus geniculatus L. – Fq. (Norrlin 1871: *Stfq.) a Alopecurus pratensis L. – Fq. Anthoxanthum odoratum L. – Fq. (Norrlin 1871: *Fqq.) a Apera spТca-ventТ (L.) P. BОКЮЯ. – OЧХв ШХН rОМШrНs: *fqq Лв NШrrХТЧ (1871), fq Лв KШrШХОЯК (1927–1928), fqq Лв KЮУКХК (1942/1943, Цs.), stfq–fq Лв FКРОrsЭröЦ & LЮЭСОr (1946). a Avena fatua L. – Rr: V. GЮЛК (1999 Timofeeva & Rudkovskaya). Avenella lexuosa (L.) DrОУОr (DescСampsТa lexuosa (L.) TrТЧ., LercСenfeldТa lexuosa (L.) SМСЮr, ЧШЦ. ТХХОР.) – Fq. (Norrlin 1871: *Fqq.) a Briza media L. – Str. a Bromopsis inermis (LОвss.) HШХЮЛ (Bromus inermis LОвss.) – Str. a Bromus arvensis L. – OЧХв ШХН rОМШrНs: LКЦЦКsЩЮrШ (1943 KЮУКХК, ШЛs.); TШХЯЮвК (FКРОrsЭröЦ & Luther 1946). a Bromus secalinus L. – OЧХв ШХН rОМШrНs: SОЧЧКвК GЮЛК (BОгКТs 1911); TШХЯЮвК КЧН KХТЦ NШs (FКРОrsЭröЦ & LЮЭСОr 1946). Calamagrostis arundinacea (L.) Roth – Fq. (NШrrХТЧ 1871: V. GЮЛК.) Calamagrostis canescens (АОЛОr) RШЭС – Fq. (Norrlin 1871: *Fq–fqq.) Calamagrostis epigeios (L.) RШЭС – Fq. (Norrlin 1871: Fqq.) Calamagrostis meinshausenii (TгЯОХОЯ) VТХУКsШШ (C. ОЩТРОТШs sЮЛsЩ. meinshausenii TгЯОХОЯ) – Rr: Megostrov (2004 Kravchenko); V. GЮЛК (2010 Kravchenko). Calamagrostis neglecta (EСrС.) G. GКОrЭЧ., B. MОв. & SМСОrЛ. – Fq. (Norrlin 1871: Fqq.) Calamagrostis phragmitoides HКrЭЦ. (C. purpurea (TrТЧ.) TrТЧ. sЮЛsЩ. phragmitoides (C. HКrЭЦ.) TгЯОХ.) – Fq. (NШrrХТЧ 1871: V. GЮЛК.) a Dactylis glomerata L. – Fq. (Norrlin 1871: Fq ТЧ SСЮЧРК КЧН V. GЮЛК.) Deschampsia cespitosa (L.) P. BОКЮЯ. – Fq. (Norrlin 1871: Fqq.) Elymus caninus (L.) L. (Agropyron caninum (L.) P. BОКЮЯ.) – Fq. (Norrlin 1871: Fq in Shunga КЧН V. GЮЛК.) Elytrigia repens (L.) Nevski (Agropyron repens (L.) P. BОКЮЯ.) – Fq. (Norrlin 1871: *Fq.) Festuca arenaria OsЛОМФ – Rr: Megostrov (2004 Kravchenko). Festuca ovina L. – Fq. (Norrlin 1871: *Fq.) Festuca rubra L. – Fq. (Norrlin 1871: *Fqq.) GlycerТa luТtans (L.) R. Br. – P. (Norrlin 1871: *Fq.) **Glyceria lithuanica (GяrsФТ) GяrsФТ – R: V. GЮЛК (1943 KЮУКХК, ШЛs.); TЮrКsЭКЦШгОrШ (1989 Kravchenko); SСТХЭвК (1999 Timofeeva & Rudkovskaya); LТЩШЯТЭsв КЧН UгФКвК SКХЦК (2013 Kravchenko); OвКЭОЯТЭsК, PШХвК, TКЦЛТЭsв, TТЩТЧТЭsв – KКsФШsОХРК КЧН UгФТв SКХЦв (КХХ 2013 SвrУтЧОЧ, ШЛs.). Glyceria maxima (C. HКrЭЦ.) HШХЦЛ. – Rr: UsЭ’-ВКЧНШЦК (1943 KЮУКХК, ШЛs.); SСЮЧРК (HЮХЭцЧ 1971); KЮгКrКЧНК (HЮХЭцЧ 1971); OrШгС IsХ. (1999 KrКЯМСОЧФШ & Kashtanov); V. GЮЛК (2012 Kravchenko). (Norrlin 1871: Unitsa.) Glyceria notata CСОЯКХХ. – P. a Helictotrichon pubescens (HЮНs.) PТХР. (Avenula pubescens (HЮНs.) DЮЦШrЭ.) – Rr: B. Klim., Kurgenitzy (2007 Kravchenko); VОrФСЧОО MвКРrШгОrШ (2012 ГЧКЦОЧsФТв, ШЛs.). Hierochloë arctica C. Presl (H. hirta (SМСrКЧФ) BШrЛ. sЮЛsЩ. arctica (C. PrОsХ) G. АОТЦ.) – Fq. (Norrlin 1871: *P; Кs H. odorata (L.) P. Beauv.) a Hordeum distichon L. – Rr: Pod’elniki (2012 Kravchenko). Leymus arenarius (L.) HШМСsЭ. – Rr: SСЮЧРК КЧН TШХЯЮвК (HЮХЭцЧ 1971). RКЭСОr МШЦЦШЧ ТЧ ОКsЭОrЧ КЧН sШЮЭСОrЧ ЩКrЭ ШП ЭСО ХКФО КЧН ШЧ HОНШsЭrШЯ IsХКЧН ОКsЭ ШП KЮгКrКЧНК, ЛЮЭ ЯОrв rКrО ТЧ ГКШЧОгСвО, ЦКв ЛО ЛОМКЮsО ШП ХКМФ ШП sЮТЭКЛХО sКЧНв sСШrОs. 186 Reports of the Finnish Environment Institute 40 | 2014 Lolium perenne L. – OЧХв ШХН rОМШrНs: KЮгКrКЧНК (GüЧЭСОr 1880); V. GЮЛК, LКЦЦКsЩЮrШ КЧН UsЭ’-ВКЧНШЦК, КЛЮЧНКЧЭ ТЧ iОХНs, ЩrШЛКЛХв МЮХЭТЯКЭОН (1942/1943 KЮУКХК, ШЛs.); TШХЯЮвК КЧН KХТЦ NШs (FКРОrsЭröЦ & LЮЭСОr 1946). Melica nutans L. – Fq. (Norrlin 1871: *Fqq.) Milium effusum L. – Fq. (NШrrХТЧ 1871: V. GЮЛК.) Molinia caerulea (L.) MШОЧМС – P. (Norrlin 1871: Fq in Shunga.) Nardus stricta L. – P. (Norrlin 1871: *Fqq.) Phalaroides arundinacea (L.) Rauschert (Phalaris arundinacea L.) – Fq. (Norrlin 1871: *Stfq–fq.) Phleum pratense L. – Fq. (Norrlin 1871: *Fq.) Phragmites australis (CКЯ.) TrТЧ. Об SЭОЮН. – Fq. (Norrlin 1871: Fqq.) Poa alpina L. – R. (Norrlin 1871: Azhepnavolok and Shunga.) Poa angustifolia L. – Str. a Poa annua L. – Fq. (Norrlin 1871: *Fqq.) Poa compressa L. – Str. Poa humilis HШППЦ. (P. pratensis sЮЛsЩ. irrigata (LТЧНЦ.) H. LТЧНЛ., P. subcaerulea Smith, P. pratensis sЮЛsЩ. subcaerulea (SЦ.) HТТЭШЧОЧ) – R. Poa nemoralis L. – P. Poa palustris L. – Fq. (Norrlin 1871: *Stfq; ТЧМХ. P. nemoralis.) Poa pratensis L. – Fq. (Norrlin 1871: *Fqq; ЩrШЛКЛХв ТЧМХ. P. angustifolia.) **Poa remota FШrsОХ. – Rr: V. GЮЛК (1942/1943 KЮУКХК, ШЛs.); TКЦЛТЭsв, VКrЧКЯШХШФ (2004 Kravchenko). Poa trivialis L. – Stfq. (Norrlin 1871: *Fq.) a Puccinellia distans (JКМq.) PКrХ. – Rr: Kosmozero (1999 Timofeeva & Rudkovskaya); KЮzaranda (2004 Kravchenko & Kuznetsov, 2004 Uotila); PКХОШsЭrШЯ (2004 Uotila); V. GЮЛК (2010 Kravchenko); KКгСЦК (2012 Kravchenko) ; B. KХТЦ., KШЧНК (2004 Uotila). a Schedonorus arundinaceus (SМСrОЛ.) DЮЦШrЭ. (Festuca arundinacea SМСrОЛ.) – Str. a Schedonorus pratensis (HЮНs.) P. BОКЮЯ. (Festuca pratensis HЮНs.) – Fq. (Norrlin 1871: SСЮЧРК; Кs Festuca elatior L.) Scolochloa festucacea (АТХХН.) LТЧФ – Rr: V. GЮЛК (LЮЭСОr 1945; FКРОrsЭröЦ & LЮЭСОr 1946); B. KХТЦ. КrОК (HЮХЭцЧ 1971); KТгСТ IsХ. (1994 Kuznetsov). a Secale cereale L. – OЧХв ШХН rОМШrНs: KХТЦ NШs (FКРОrsЭröЦ & LЮЭСОr 1946). a Dubious or erroneously recorded species Nymphaea tetragona Georgi (Klyukina 1965) Rumex confertus АТХХН. (BОгКТs 1911) Gentiana pneumonanthe L. (Bezais 1911) Carduus nutans L. (Bezais (1911) Lactuca tatarica (L.) C. A. Mey. (Bezais 1911) Phleum alpinum L. 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Reports of the Finnish Environment Institute 40 | 2014 191 Margarita Fadeeva and Alexei Kravchenko in moist herb-rich forest (spruce swamp) near Lipovitsy village (Photo Jevgeni Jakovlev). 192 Reports of the Finnish Environment Institute 40 | 2014 3.2 Bryophyte lora of Zaonezhye Peninsula Anatoly Maksimov* and Kimmo Syrjänen** *Institute of Biology of Karelian Research Center of Russian Academy of Sciences, Petrozavodsk. 50 Alexandra Nevskogo St., 185003 Petrozavodsk, Karelia, Russia ** The Finnish Environment Institute (SYKE) Corresponding author Kimmo Syrjänen E-mail: kimmo.syrjanen@ymparisto.i Abstract The bryophyte lora of Zaonezhye Peninsula consists of 235 species of mosses and 64 hepatics. The proportion of red listed and indicator species is very high in the area. The establishment of nature monuments and a strictly protected area on Zaonezhye Peninsula will contribute to the conservation of a number of rare Red Data Book species and valuable forest indicator species, growing on forests with pristine and old-growth characteristics, swamp forests and black alder forests, nutrient-rich mesotrophic and eutrophic mires, as well as calcicolous cliffs and rock outcrops. Introduction Floristically, Zaonezhye Peninsula is of great interest. Its distinctive lora and vegetation are due to a distinctive microclimate, different bedrocks and nutrient-rich, sodden lithogenic shungite soils. Shungite (name is according to village Shunga) is black carboniferous rock type which is typical for Zaonezhye. Due to favourable growth conditions, species of southern taiga forests occur here in a middle taiga landscape. According to the biogeographic zonation of Eastern Fennoscandia (Mela & Cajander 1906), the study area is located in the eastern part of the province of Karelia onegensis, or the Zaonezhye loristic province (Ramenskaya 1960). The Zaonezhye loristic province is the second most diverse province in Karelia for mosses after the Priladozhye loristic province. Despite the proximity of Zaonezhye Peninsula to Petrozavodsk and a well-developed road network, the peninsula, especially its western and northeastern parts, has been poorly studied bryoloristically until recently. For a long time the irst moss samples, collected by A.K. Cajander and J.I. Lindroth in the vicinity of Sennaya Guba and on Kizhi Island in 1898, were stored in the cryptogamous plant herbarium at the Reports of the Finnish Environment Institute 40 | 2014 193 Museum of Botany, Helsinki University. These samples have been published only recently (Ahti & Boychuk 2006). In 1921, L.I. Savich-Lyubitskaya collected mosses near the village of Shunga. Between 1987 and 1996, moss samples from Kizhi Island were collected by Oleg Kuznetsov, Anatoly Maksimov, Tatyana Brazovskaya and Natalya Stoikina who studied mire lora and vegetation; by V.A.Bakalin (Bakalin et al. 1999) who undertook a special study of moss species from Kizhi Islands and a part of Bolshoi Klimenetsky Isl.; and by Margarita Boychuk and Jevgenia Markovskaya who studied mosses on the islands of Kizhi Nature Reserve (Boychuk & Markovskaya 2005). The moss lora of Zaonezhye Peninsula (villages Shunga, Tolvuya, Lisitsino and Kosmozero) and the planned Zaonezhye Nature Reserve was studied by Anatoly Maksimov and Tatyana Maksimova in 2000 and by Anatoly Maksimov in 2001 and 2012. Moss samples, collected by Oleg Kuznetsov in 1999 and by Stanislav Kutenkov in 2012 from mires in the study area, have been used for compiling a list of moss species growing in the nature reserve. A list of moss species from Zaonezhye Nature Reserve has been published recently (Maksimov, 2013). This publication contains a list of new mosses from Zaonezhye Peninsula based for the most part on the results of our studies. By 2013, 221 moss species had been reported from Zaonezhye Peninsula (Bakalin et al. 1999; Kuznetsov et al. 2000; Boychuk & Markovskaya 2005; Ahti & Boychuk 2006; Maksimov 2013), although a consolidated list of moss species from the peninsula has not yet been published. In 2013, the Finnish scientists Kimmo Syrjänen and Olli Manninen continued the study of bryophytes from southern and southwestern Zaonezhye Peninsula. They collected and analyzed approximately 200 bryophyte samples, which are stored in the Turku University herbarium (TUR). Anatoly Maksimov re-analyzed the moss samples from Zaonezhye Peninsula, which are stored in the Karelian Research Centre herbarium (PTZ). In 2013, observations of certain indicator species of bryophytes like Neckera pennata were also collected by Jyri Mikkola, Olli-Pekka Tikkanen and Timo Kuuluvainen. As a result, four new moss species, namely Eurhynchium angustirete, Plagiomnium afine, Schistidium platyphyllum and Tayloria lingulata, and one liverwort, Anastrophyllum michauxii, have been reported from the Zaonezhye loristic province. Eurhynchium angustirete, Plagiomnium afine and Tayloria lingulata have been included in the Red Data Book of the Republic of Karelia (2007). Thirteen moss species (Dicranum fragilifolium, Herzogiella seligeri, Mnium lycopodioides, Myurella julacea, Neckera pennata, Plagiomnium drummondii, Plagiothecium latebricola, Polytrichastrum pallidisetum, Rhizomnium magnifolium, Schistidium platyphyllum, Sphagnum quinquefarium, S. rubellum and Tayloria lingulata) have been found for the irst time on Zaonezhye Peninsula. Thus, 235 moss species, making up 65% of the moss lora in the Zaonezhye loristic province (363 species), are now known from Zaonezhye Peninsula (see List of species). A preliminary list of hepatics includes 64 species. Rare and valuable species. Interesting Bryophyte species include Brachythecium rutabulum, Calypogeia suecica, Encalypta brevicolla, Eurhynchium angustirete, Hamatocaulis vernicosus, Harpanthus scutatus, Homomallium incurvatum, Hylocomiastrum pyrenaicum, Isothecium alopecuroides, Jamesomiella autumnalis, Leucodon sciuroides, Liochlaena lanceolata, Lophozia ascendens, Neckera besseri, N. pennata, Orthotrichum gymnostomum, Oxystegus tenuirostris, Plagiomnium afine, P. drummondii, Plagiothecium latebricola, Platygyrium repens, Pylaisia selwynii, Scapania apiculata, Schistidium pulchrum, Sphagnum auriculatum, S. pulchrum, S. lindbergii and Trichocolea tomentella. Fourteen of them, namely Calypogeia suecica, Eurhynchium angustirete, Harpanthus scutatus, Jamesomiella autumnalis, Lophozia ascendens, Neckera besseri, N. pennata, Orthotrichum gymnostomum, Plagiomnium afine, P. drummondii, Scapania apiculata, Sphagnum auriculatum, Tayloria 194 Reports of the Finnish Environment Institute 40 | 2014 lingulata and Trichocolea tomentella, are listed as very rare species in the Red Data Book of Karelia (2007). Some species from Zaonezhye Peninsula, e.g. Pylaisia selwynii and Hamatocaulis vernicosus, are included in the Red Data Book of European Bryophytes (Red.., 1995). Hamatocaulis vernicosus, Herzogiella turfacea and Plagiomnium drummondii are also listed in the EU Habitats Directive. Indicator species. Overall 47 bryophyte species, which according to Andersson et al. (2009) are considered indicator species of valuable forest habitats, are found from Zaonezhye Peninsula. This is a remarkably high number of indicator bryophytes. The list of indicator species includes many of the above-mentioned red-listed species: Anastrophyllum michauxii, Anomodon attenuatus, A. longifolius, Barbilophozia lycopodioides, Calypogeia suecica, Crossocalyx hellerianus, Dicranum drummondii, D. lagellare, D. fragilifolium, Eurhynchium angustirete, Harpanthus scutatus, Herzogiella seligeri, Homalia trichomanoides, Hylocomiastrum pyrenaicum, H. umbratum, Jamesoniella autumnalis, Leucodon sciuroides, Liochlaena lanceolata, Lophozia ascendens, Lophozia longilora, Mnium stellare, Neckera complanata, N. pennata, Orthocaulis attenuatus, Orthotrichum gymnostomum, O. obtusifolium, Oxyrrhynchium hians, Philonotis spp., Plagiochila asplenioides, Plagiomnium afine, P. drummondii, Plagiothecium latebricola, Platygyrium repens, Pseudobryum cinclidioides, Pterigynandrum iliforme, Pylaisia selwynii , Riccardia latifrons, R. palmata, Scapania apiculata, Schistostega pennata, Sphagnum quinquefarium, Sphagnum wulianum, Sphenolobus saxicola, Tayloria lingulata, Trichocolea tomentella and Tritomaria quinquedentata. The most valuable and interesting habitats and sites from the perspective of bryophyte species diversity include old-growth forests, alder swamps, mesotrophic and eutrophic mires and rich-fens as well as carboniferous rock outcrops. Old-growth spruce and mixed forests. Mesic, herb-rich forests with pristine and old-growth characteristics are very important for bryophyte biodiversity on Zaonezhye Peninsula. Often these forests create a long continuum of coarse woody debris and moist microclimates. Windfallen logs include mainly spruce but also aspen and sometimes pine. These forests are mainly located on heatland sites, remote from old villages, although they are sometimes found also on mire margins and along brooks and rivulets. Epixylic liverworts favour logs where the bark has fallen off and the surface is slightly softened. The diversity of epixylic liverworts typical for pristine forests is high in the forests of Zaonezhye. The frequency of indicator species such as Crossocalyx hellerianus, Lophozia longilora and Riccardia spp. as well as red-listed Calypogeia suecica varies from common to very common in these forests. For example, there are 160 observations of indicator species Crossocalyx hellerianus (syn. Anastrophyllum hellerianum) and red-listed Calypogeia suecica were collected from 21 sites in 2013. The early epixylic colonizer, Lophozia ciliata is common in Zaonezhye. More demanding epixylics such as red-listed Lophozia ascendens and Jamesoniella autumnalis are found in several stands, whereas both Scapania apiculata and Anastrophyllum michauxii seem to be rather rare. In the Zaonezhye population, female plants of Jamesoniella autumnalis also bear perianths, which indicates optimal conditions for growth. According to Damsholt (2002), perianths of Jamesoniella autumnalis are rare in Fennoscandia. Reports of the Finnish Environment Institute 40 | 2014 195 Fig. 1. Spruce logs host diverse lora of rare epixylic liverworts in Zaonetshye. Lipovitsy (Photo Kimmo Syrjänen). Swamp forests and other wet forests. The red-listed Harpanthus scutatus and the indicator species Liochlaena lanceolata grow in more moist and wet forests with the presence of black alder (Alnus glutinosa). Also, Plagiothecium latebricola is found on the stumps and at the bases of old alder trees in swamp forests and moist forests along streams. Trichocolea tomentella occurs where the forest bottom is moist and affected by groundwater. It seems to grow occasionally in herb-rich swamp forests affected by springs. On the forest loor of moist spruce and swamp forests, Rhytidiadelphus subpinnatus is commonly found, sometimes together with Hylocomiastrum umbratum and more rarely with Hylocomiastrum pyrenaicum. The last two species are considered indicator species of valuable forest habitats. Fig. 2. Herb-rich swamp forest near Polya (Photo Kimmo Syrjänen). 196 Reports of the Finnish Environment Institute 40 | 2014 Forests with large aspen trees. In addition to old-growth mixed forests, large aspen individuals are also present in the late successional stages of secondary deciduous forests. These forests are common on rich soils close to abandoned villages of southern Zanonezhye Peninsula. Indicator species Neckera pennata is relatively common and a typical epiphyte of large aspens. In sheltered conditions it forms large mats along trunks. In 2013, Neckera pennata was observed in 120 locations. Also Orthotrichum obtusifolium is a common indicator species, growing on Zaonezhye aspens. Orthotrichum gymnostomum is mainly found on aspen trunks in old-growth forests, although it also grows in secondary forests. It is easily overlooked as it typically grows relatively high up on the trunk and is therefore mainly found on recently fallen trees (either by wind or beavers). The same is true of Pylaisia selwynii, which is more rare than the closely related Pylaisia polyantha that is common on aspen trunks. Fig. 3. Base of aspen with Neckera pennata, etc. (Photo Kimmo Syrjänen). Deciduous and mixed herb-rich forests have a diverse bryophyte lora at the bases of aspens and on the forest loor. Both Eurhynchium angustirete and Plagiomnium drummondii grow in these habitats. Also indicator species Homalia trichomanoides and Isothecium alopecuroides can be found at the base of aspen trunks. Plagiomnium medium and Sciuro-hypnum curtum are very common on the forest loor. In addition to many rare liverworts, mosses Herzogiella seligeri and Herzogiella turfacea grow on decaying aspen trunks. The latter is common also in swamp forests. Rare Plagiomnium afine has been found at the base of old Ulmus glabra trunk in one deciduous stand. Bedrock exposures with carbonate rich rocks occur in various places in the area. These outcrops host a rich lora of bryophytes that prefer calcareous substrata. Species include Tortella tortuosa, Distichium capillaceum and Ditrichum lexicaule, which are typical indicators of limestone rocks. Especially worth mentioning are the southern and southeastern slopes of Mount Sypun, where there are rare species such as Encalypta brevicolla, Leucodon sciuroides, Neckera besseri, N. complanata and Oxystegus tenuirostris. Also the bedrock exposures on the south- and southwest-facing slopes of the southern end of Svyatukha Bay are important. The Red Data Book species Orthotrichum gymnostomum and rare nemoral species, including Anomodon attenuatus, Brachythecium rutabulum, Homalia trichomanoides, Isothecium alopecuroides, I. myosuroides, Platygyrium repens and Pseudoleskeella papillosa have been encountered here. Reports of the Finnish Environment Institute 40 | 2014 197 Fig. 4. Spring rich fen close to Kaskoselga with Carex appropinquata, Saxifraga hirculus and Hamatocaulis vernicosus etc. (Photo Kimmo Syrjänen). Valuable mires and fens. Certain mires near the lakes Karasozero and Koibozero, as well as Kalegubskoe Mire in the vicinity of Lambasruchei, are of great scientiic interest. The mosses Sphagnum pulchrum, S. aongstroemii and S. lindbergii, which are uncommon to Zaonezhye, have been found here. These mires also host a number of calciphilous mosses that rely on diverse ground nutrients (Dyachkova et al. 1993; Kuznetsov et al. 2000). In the southern part of the peninsula, there are also several fens that are valuable for conservation, including the fens southwest and northwest of the village of Tambitsy. These fens have a rich lora of bryophytes and vascular plants, including Hamatocaulis vernicosus. Conclusions The moss lora of the Zaonezhye Peninsula generally comprises the basic species that grow in Zaonezhye, where impoverished south-taiga forests occur in mid-taiga landscapes. The moss lora consists of 235 species that account for about 65% of the lora in the Zaonezhye loristic province. Altogether 14 bryophyte species of Karelian Red List have been found, but the amount of indicator species of valuable forest habitat is much higher: 47 mosses and liverworts. The establishment of a strictly protected area on the Zaonezhye Peninsula will contribute to the conservation of the rare Red Data Book species, such as Calypogeia suecica, Eurhynchium angustirete, Harpanthus scutatus, Jamesomiella autumnalis, Lophozia ascendens, Neckera besseri, N. pennata, Orthotrichum gymnostomum, Plagiomnium afine, P. drummondii, Scapania apiculata, Sphagnum auriculatum, Tayloria lingulata and Trichocolea tomentella, and the nemoral moss species Anomodon attenuatus, Brachythecium rutabulum, Leucodon sciuroides, Neckera complanata, Platygyrium repense and Pylaisia selwynii, most bryophytes, which grow on nutrient-rich eutrophic mires, and bryophyte indicators of old-growth forests. 198 Reports of the Finnish Environment Institute 40 | 2014 Zaonezhye has long history of traditional land use and selective cutting of forests, and also recently some forests are used in intensive forestry. However, large pristine-like stands with continuity of dead wood (both windfalls and standing trees) and large deciduous trees e.g. aspen are available in many places. Diverse bryolora of natural forests and mires is present in the peninsula. In addition to coniferous forests Zaonezhye has also many other valuable forest habitat types and mires with intact hydrology those support diverse bryophyte species composition. For example, swamp forests with black alder are such sites as well as deciduous late successional herb-rich stands. Larger pristine-like coniferous and herb rich mixed forest stands can be connected to each other by careful planning of conservation areas. Forests can also be connected to villages with shoreline forests, mires, swamp forests and waterways. Zaonezhye provides unique possibility to make connected network of conservation areas. 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MТrОsЖ. − IЧ: IЧЯОЧЭШrв КЧН ЛТШНТЯОrsТЭв sЭЮНТОs ШП ГКШЧОгСвО PОЧТЧsЮХК КЧН NШrЭСОrЧ sСШrО ШП ЭСО LКНШРК LКФО (ШЩОrКЭТЯЧШ-ТЧПШrЦКМТШЧЧвО ЦКЭОrТКХв). KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 71–83. (IЧ RЮssТКЧ). MКФsТЦШЯ, A.I. 2012. . . « » ДBrвШЭСвЭОs ШП ЭСО KТЯКМС NКЭЮrО RОsОrЯОЖ. – IЧ: PrТrШНЧвО ЩrШМОssв Т вКЯХОЧТвК Я ЮЧТФКХ’ЧвС ЮsХШЯТвКС srОНЧОЭКОгСЧШРШ гКЩШЯОЧНЧТФК. MКЭОrТКХв ЧКЮМСЧШ-ЩrКФЭТМСОsФШТ ФШЧПОrОЧМТТ, ЩШsЯвКsСОЧЧШТ 80-ХОЭТвЮ FGBU «GШsЮНКrsЭЯОЧЧвТ ЩrТrШНЧвТ гКЩШЯОНЧТФ “KТЯКМС”. PОЭrШгКЯШНsФ. Щ. 122–125. (IЧ RЮssТКЧ). MКФsТЦШЯ, A.I. 2013. . . 4.3. Д 4.3. MШssОsЖ. − IЧ: GrШЦЭsОЯ, A.N. (ОН.), SОХФК LКЧНsМКЩОs ШП the Zaonezhskii Peninsula: Natural Characteristics, Land Use, Conservation. Petrozavodsk: Karelian Research CОЧЭrО ШП RAS, Щ. 132–136. (IЧ RЮssТКЧ). MОХК, A.J. & CКУКЧНОr, A.K. 1906. SЮШЦОЧ ФКsЯТШ. – HОХsТЧФТ, Б+68+764 Щ. RКЦОЧsФКвК, M. L. 1960. . . ДHКЧНЛШШФ VКsМЮХКr PХКЧЭs ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ. 400 Щ. (IЧ RЮssТКЧ). RОН DКЭК BШШФ ШП EЮrШЩОКЧ BrвШЩСвЭОs. 1995. – TrШЧНСОТЦ. 291 Щ. RОН DКЭК BШШФ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТК. 2007. IЯКЧЭОr, E. V. & KЮгЧОЭsШЯ, O. L. (ОНs.), . . ., . . ( .). – PОЭrШгКЯШНsФ, 368 Щ. (IЧ RЮssТКЧ). Reports of the Finnish Environment Institute 40 | 2014 199 Appendix List of mosses from Zaonezhye Peninsula Nomenclature according to Ignatov et al. (2006), with some changes. Fam. Sphagnaceae Sphagnum angustifolium (C. E. O.Jensen ex Russow) C. E. O. Jensen S. aongstroemii C. Hartm. S. auriculatum Schimp. S. balticum (Russow) C. E. O.Jensen S. capillifolium (Ehrh.) Hedw. S. centrale C. E. O. Jensen S. compactum Lam. & DC. S. contortum Schultz S. cuspidatum Ehrh. ex Hoffm. S. fallax (H. Klinggr.) H. Klinggr. S. imbriatum Wilson S. lexuosum Dozy & Molk. S. fuscum (Schimp.) H. Klinggr. S. girgensohnii Russow S. inundatum Russow S. jensenii H. Lindb. S. lindbergii Schimp. S. magellanicum Brid. S. majus (Russow) C. E. O. Jensen S. obtusum Warnst. S. papillosum Lindb. S. platyphyllum (Lindb. ex Braithw.) Warnst. S. pulchrum (Lindb. ex Braithw.) Warnst. S. quinquefarium (Lindb. ex Braithw.) Warnst. S. riparium Ångstr. S. rubellum Wilson S. russowii Warnst. S. squarrosum Crome S. subfulvum Sjörs S. subsecundum Nees S. teres (Schimp.) Ångstr. S. warnstorii Russow S. wulianum Girg. Fam. Andreaeaceae Andreaea rupestris Hedw. Fam. Polytrichaceae Atrichum tenellum (Röhl.) Bruch et al. A. undulatum (Hedw.) P. Beauv. Pogonatum urnigerum (Hedw.) P. Beauv. Polytrichastrum longisetum (Sw. ex Brid.) G. L. Smith P. pallidisetum (Funck) G. L. Smith Polytrichum commune Hedw. P. juniperinum Hedw. P. piliferum Hedw. 200 Reports of the Finnish Environment Institute 40 | 2014 P. strictum Brid. Fam. Tetraphidaceae Tetraphis pellucida Hedw. Fam. Funariaceae Funaria hygrometrica Hedw. Fam. Encalyptaceae Encalypta brevicolla (Bruch et al.) Ångstr. E. ciliata Hedw. E. rhaptocarpa Schwägr. E. vulgaris Hedw. Fam. Grimmiaceae Bucklandiella microcarpa (Hedw.) Bednarek-Ochyra & Ochyra Grimmia longirostris Hook. G. muehlenbeckii Schimp. Niphotrichum canescens (Hedw.) Bednarek-Ochyra & Ochyra Schistidium apocarpum (Hedw.) Bruch et al. S. dupretii (Thér.) W. A. Weber S. papillosum Culm. S. platyphyllum (Mitt.) H.Perss. S. pulchrum H. H. Blom S. rivulare (Brid.) Podp. Fam. Dicranaceae Dicranella cerviculata (Hedw.) Schimp. D. heteromalla (Hedw.) Schimp. D. schreberiana (Hedw.) Dixon Dicranum bonjeanii De Not. D. brevifolium (Lindb.) Lindb. D. drummondii Müll. Hal. D. lagellare Hedw. D. lexicaule Brid. D. fragilifolium Lindb. D. fuscescens Turner D. majus Turner D. montanum Hedw. D. polysetum Sw. D. scoparium Hedw. D. undulatum Schrad. ex Brid. Paraleucobryum longifolium (Hedw.) Loeske Fam. Rhabdoweisiaceae Amphidium lapponicum (Hedw.) Schimp. Cnestrum schisti (F. Weber & D. Mohr) I. Hagen Cynodontium strumiferum (Hedw.) Lindb. C. tenellum (Schimp.) Limpr. Hymenoloma crispulum (Hedw.) Ochyra Fam. Ditrichaceae Ceratodon purpureus (Hedw.) Brid. Distichium capillaceum (Hedw.) Bruch et al. Ditrichum lexicaule (Schwägr.) Hampe Saelania glaucescens (Hedw.) Broth. Fam. Pottiaceae Barbula convoluta Hedw. Bryoerythrophyllum recurvirostrum (Hedw.) P.C. Chen Reports of the Finnish Environment Institute 40 | 2014 201 Didymodon ferrugineus (Schimp. ex Besch.) M.O. Hill D. rigidulus Hedw. Oxystegus tenuirostris (Hook. & Tayl.) A. J. E. Smith Syntrichia ruralis (Hedw.) F. Weber & D. Mohr Tortella fragilis (Hook. & Wilson) Limpr. T. tortuosa (Hedw.) Schimp. Fam. Fissidentaceae Fissidens adianthoides Hedw. F. osmundoides Hedw. Fam. Schistostegaceae Schistostega pennata (Hedw.) F. Weber & D. Mohr Fam. Meesiaceae Leptobryum pyriforme (Hedw.) Wilson Meesia triquetra (Jolycl.) Ångstr. Paludella squarrosa (Hedw.) Brid. Fam. Splachnaceae Splachnum luteum Hedw. S. rubrum Hedw. Tayloria lingulata (Dicks.) Lindb. Tetraplodon angustatus (Hedw.) Bruch et al. Fam. Orthotrichaceae Orthotrichum gymnostomum Bruch ex Brid. O. obtusifolium Brid. O. rupestre Schleich. ex Schwägr. O. speciosum Nees Fam. Hedwigiaceae Hedwigia ciliata (Hedw.) P. Beauv. Fam. Bryaceae Bryum argenteum Hedw. B. bimum (Schreb.) Turner B. caespiticium Hedw. B. capillare Hedw. B. creberrimum Tayl. B. lonchocaulon Müll. Hal. B. moravicum Podp. B. pallescens Schleich. ex Schwägr. B. pseudotriquetrum (Hedw.) P. Gaertn., B. Mey. & Schreb. B. weigelii Spreng. Rhodobryum roseum (Hedw.) Limpr. Fam. Mielichhoferiaceae Pohlia bulbifera (Warnst.) Warnst. P. cruda (Hedw.) Lindb. P. nutans (Hedw.) Lindb. Fam. Mniaceae Cinclidium stygium Sw. Mnium lycopodioides Schwägr. M. stellare Hedw. Plagiomnium afine (Bland.) T. J. Kop. P. cuspidatum (Hedw.) T. J. Kop. P. drummondii (Bruch & Schimp.) T.J. Kop. Plagiomnium elatum (B.S.G.) T.J. Kop. P. ellipticum (Brid.) T. J. Kop. 202 Reports of the Finnish Environment Institute 40 | 2014 P. medium (Bruch et al.) T. J. Kop. Pseudobryum cinclidioides (Huebener) T. J. Kop. Rhizomnium magnifolium (Horik.) T.J.Kop. R. pseudopunctatum (Bruch & Schimp.) T. J. Kop. R. punctatum (Hedw.) T. J. Kop. Rhodobryum roseum (Hedw.) Limpr. Fam. Bartramiaceae Bartramia pomiformis Hedw. Philonotis fontana (Hedw.) Brid. Fam. Aulacomniaceae Aulacomnium palustre (Hedw.) Schwägr. Fam. Fontinalaceae Dichelyma falcatum (Hedw.) Myrin Fontinalis antipyretica Hedw. Fam. Plagiotheciaceae Herzogiella seligeri (Brid.) Z. Iwats. Herzogiella turfacea (Lindb.) Z. Iwats. Isopterygiopsis pulchella (Hedw.) Z. Iwats. Myurella julacea (Schwägr.) Schimp. Plagiothecium cavifolium (Brid.) Z. Iwats. P. denticulatum (Hedw.) Bruch et al. P. laetum Bruch et al. P. latebricola Bruch et al. P. piliferum (Sw.) Bruch et al. Fam. Pterigynandraceae Pterigynandrum iliforme Hedw. Fam. Leucodontaceae Leucodon sciuroides (Hedw.) Schwägr. Fam. Hypnaceae Hypnum cupressiforme Hedw. Fam. Pylaisiadelphaceae Platygyrium repens (Brid.) Bruch et al. Fam. Pseudoleskeaceae Lescuraea incurvata (Hedw.) Lawt. Fam. Anomodontaceae Anomodon attenuatus (Hedw.) Huebener A. longifolius (Brid.) Hartm. Fam. Heterocladiaceae Heterocladium dimorphum (Brid.) Bruch et al. Fam. Neckeraceae Homalia trichomanoides (Hedw.) Bruch et al. Neckera besseri (Lobarz.) Jur. N. complanata (Hedw.) Huebener N. oligocarpa Bruch N. pennata Hedw. Fam. Climaciaceae Climacium dendroides (Hedw.) F. Weber & D. Mohr Fam. Hylocomiaceae Hylocomiastrum pyrenaicum (Spruce) M. Fleisch. H. umbratum (Hedw.) M. Fleisch. Hylocomium splendens (Hedw.) Bruch et al. Pleurozium schreberi (Brid.) Mitt. Reports of the Finnish Environment Institute 40 | 2014 203 Rhytidiadelphus squarrosus (Hedw.) Warnst. R. subpinnatus (Lindb.) T. J. Kop. R. triquetrus (Hedw.) Warnst. Fam. Lembophyllaceae Isothecium alopecuroides (Lam. ex Dubois) Isov. I. myosuroides Brid. Fam. Brachytheciaceae Brachytheciastrum velutinum (Hedw.) Ignatov & Huttunen Brachythecium albicans (Hedw.) Bruch et al. B. erythrorrhizon Bruch et al. B. mildeanum (Schimp.) Schimp. B. rivulare Bruch et al. B. rutabulum (Hedw.) Bruch et al. B. salebrosum (F. Weber & D. Mohr) Bruch et al. Cirriphyllum piliferum (Hedw.) Grout Eurhynchiastrum pulchellum (Hedw.) Ignatov & Huttunen Eurhynchium angustirete (Broth.) T.J. Kop. Oxyrrhynchium hians (Hedw.) Loeske Sciuro-hypnum curtum (Lindb.) Ignatov S. populeum (Hedw.) Ignatov & Huttunen S. relexum (Starke) Ignatov & Huttunen S. starkei (Brid.) Ignatov & Huttunen Fam. Calliergonaceae Calliergon cordifolium (Hedw.) Kindb. C. giganteum (Schimp.) Kindb. C. megalophyllum Mikut. C. richardsonii (Mitt.) Kindb. Loeskypnum badium (Hartm.) H. K. G. Paul Straminergon stramineum (Dicks. ex Brid.) Hedenäs Warnstoria exannulata (Bruch et al.) Loeske W. luitans (Hedw.) Loeske W. procera (Renauld & Arnell) Tuom. W. tundrae (Arnell) Loeske Fam. Scorpidiaceae Hamatocaulis vernicosus (Mitt.) Hedenäs Hygrohypnella ochracea (Turner ex Wilson) Ignatov & Ignatova Sanionia uncinata (Hedw.) Loeske Scorpidium cossonii (Schimp.) Hdenäs S. revolvens (Sw. ex anon.) Rubers S. scorpioides (Hedw.) Limpr. Fam. Pylaisiaceae Breidleria pratensis (W. D. J. Koch ex Spruce) Loeske Calliergonella cuspidata (Hedw.) Loeske C. lindbergii (Mitt.) Hedenäs Homomallium incurvatum (Schrad. ex Brid.) Loeske Ptilium crista-castrensis (Hedw.) De Not. Pylaisia polyantha (Hedw.) Bruch et al. P. selwynii Kindb. Stereodon pallescens (Hedw.) Mitt. Fam. Rhytidiaceae Rhytidium rugosum (Hedw.) Kindb. Fam. Pseudoleskeellaceae 204 Reports of the Finnish Environment Institute 40 | 2014 Pseudoleskeella nervosa (Brid.) Nyh. P. papillosa (Lindb.) Kindb. P. tectorum (Funck ex Brid.) Kindb. Fam. Thuidiaceae Abietinella abietina (Hedw.) M. Fleisch. Helodium blandowii (F. Weber & D. Mohr) Warnst. Thuidium assimile (Mitt.) A. Jaeger T. recognitum (Hedw.) Lindb. Fam. Amblystegiaceae Amblystegium serpens (Hedw.) Bruch et al. Campyliadelphus chrysophyllus (Brid.) Kanda C. elodes (Lindb.) Kanda Campylidium sommerfeltii (Myrin) Ochyra Campylium protensum (Brid.) Kindb. Campylium stellatum (Hedw.) C. E. O. Jensen Cratoneuron ilicinum (Hedw.) Spruce Drepanocladus aduncus (Hedw.) Warnst. D. polygamus (Bruch et al.) Hedenäs Drepanocladus sendtneri (Schimp. ex H. Müll.) Warnst. Hygroamblystegium luviatile (Hedw.) Loeske Leptodictyum riparium (Hedw.) Warnst. Palustriella falcata (Brid.) Hedenäs Pseudocalliergon trifarium (F. Weber & D. Mohr) Loeske Serpoleskea subtilis (Hedw.) Loeske Tomentypnum nitens (Hedw.) Loeske Fig. 5. Neckera pennata (Photo: Kimmo Syrjänen). Reports of the Finnish Environment Institute 40 | 2014 205 Fig. 6. Rhytidiadelphus subpinnatus (Photo: Kimmo Syrjänen). Fig. 7. Trichocolea tomentella (Photo: Kimmo Syrjänen). 206 Reports of the Finnish Environment Institute 40 | 2014 3.3 List of lichens and allied fungi collected on Zaonezhye Peninsula Margarita A. Fadeeva*, Olli Manninen** and Kimmo Syrjänen*** *Forest Research Institute of Karelian Research Center of Russian Academy of Sciences, 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia Corresponding author Margarita Fadeeva E-mail: fadeeva@krc.karelia.ru ** Luonto-Liitto, Annankatu 26 A, 00100 Helsinki, Finland *** The Finnish Environment Institute (SYKE), P.O.Box 140, 00251 Helsinki, Finland. History of the studies of lichens in Zaonezhye Peninsula and adjacent islands The pioneer study of the lichen lora on Zaonezhye Peninsula was undertaken in 1863 by two Finnish naturalists: student Th. Simming and lecturer A. Kullhem. They collected a large number of lichen specimens, which are now in the herbarium of the Botanical Museum of the Finnish Museum of Natural History, University of Helsinki (H). The collection was analyzed and partly published by W. Nylander (1866 a, c), the greatest lichen classiier at that time. In the same time (1863) Alexander K. Günther was travelling, presumably together with Th. Simming and A. Kullhem, on Zaonezhye Peninsula. A. K. Günther, an Alexander Plant staff healer in the Olonets Province, who later collected lichens actively near Petrozavodsk, visited the northeastern part of the territory and Kizhi Island. The results of his trip are reported in his work “On lora of the Obonega Region Province» (Günther 1880), where lichens are not mentioned. In 1870, Finnish botanist and phytogeographer J.P. Norrlin visited the biogeographic province Karelia onegensis (Kon) (it is Norrlin was the irst scientist who recognized Kon province he interpreted it in a broader sense than modern authors do). Norrlin described many of the samples he collected near the villages of Velikaya Guba, Tolvuja and Shunga, together with the samples collected by Th. Simming and A. Kullhem, in the second part of his classical work «Flora Kareliae Onegensis. II. Lichenes» (Norrlin 1876). The collections of Th. Simming, A. Kullhem and J. P. Norrlin are referred to by E. A. Vainio in his fundamental work «Lichenographia Fennica. I–IV» (Vainio 1921, 1922, 1927, 1934). Norrlin’s collections are stored in H. Reports of the Finnish Environment Institute 40 | 2014 207 In 1898 and 1899, Finnish botanists A.K. Cajander and J. I. Lindroth (subsequently Liro) toured Russian Karelia and the Onega River area. They visited many places such as Kizhi Island, Bolshoi Klimenetsky Island, Bolshoi Lelikovsky Island (Point Radkolye), Yuzhny Oleny Island and other smaller islands. Their routes have been described and lists of the moss species, liverworts and lichens collected by Cajander and Lindroth have been published by T. Ahti and M. Boychuk (Ahti & Boychuk 2006). The list of lichens, which consists of 68 species, does not comprise samples from the Zaonezhye Peninsula. In 1907, Russian agronomist and botanist E.K. Bezais took a 2-month ield trip to Karelia. His goal was to study and describe the coastal and insular vegetation of Lake Onega. While travelling, he collected and described both plants and lichens. He submitted a detailed report on his trip (Bezais 1911), in which he mentioned Cladonia rangiferina (L.) F. H. Wigg. found on Paleostrov Island. The herbarium of Botanical Institute (LE) comprises at least two lichen samples collected by E.K. Bezais and A. Verdi «on north shore of Lake Onega»: Rhizocarpon badioatrum (Flörke ex Spreng.) Th. Fr. and Rhizocarpon distinctum Th. Fr. (Fadeyeva et al. 1997). In 1920–1924, V.P. Savich joined the Olonets Scientiic Expedition led by G.U. Vereshchagin and organized by the State Hydrological Institute together with the Main Botanical Gardens (now the Botanical Institute, RAS) and other scientiic institutions, and collected lichen samples on shores of lakes Sandal, Segozero and Vygozero and near Povenets (west and north shores of Lake Onega). It is well- known that he also visited the Shunga area, because LE has a sample of Ophioparma ventosa (L.) Norman collected by V.P. Savich and L.I. Savich-Lyubitskaya on Gorodok Hill, 9 km southeast of Shunga. Unfortunately, many samples from a huge collection of lichens (several thousand samples) brought by V.P. Savich from Karelia and kept in LE (Vereshchagin 1921, 1924) have not yet been analyzed. In the 1970s, T.P. Sizova and T. Yu. Tolpysheva of Moscow State University studied the species composition of lichens on famous wooden Church of Transiguration on Kizhi Island (Tolpysheva et al. 2001). In 1999–2001 and 2007, M.A. Fadeyeva visited Kizhi Island, Bolshoi Klimenetsky Island, Bolshoi Lelikovsky Island, Severny and Yuzhny Oleny Island, Volkostrov, Krestovy and Belaya Selga village in Zaonezhye. Only a small portion of more than one thousand samples collected chiely in 1999 has been published (Fadeyeva 2000, 2001, 2003, Fadeyeva et al. 2007). In 2004, M.A. Fadeyeva joined a Russian-Finnish expedition to the Zaonezhye Peninsula and Lake Onega islands (3.–8 July, 2004). Russia was represented by E. Gnatjuk, A. Kravchenko, A. Kryshen’ & O. Kuznetsov and Finland by M. Piirainen, T. Lindholm, R. Ruuhijärvi & P. Uotila. She visited Bolshoi Klimenetsky Island (Klimetsky Nos Peninsula and Point Lukovo), Bolshoi Lelikovsky Island (Point Radkolye), Megostrov, Paleostrov, Rechnoi, Shushenevsky and Yuzhny Oleny islands and the continental shore near Kuzaranda and Tipinitsky villages (Point Varnavolok). In 2010, M.A. Fadeyeva, together with A. V. Kravchenko, V.I. Krutov, O.O. Predtechenskaya and A.V. Ruokolainen (Forest Research Institute, KarRC, RAS), studied the area north and south of Velikaya Guba (the environs of the former villages Komlevo, Ryabovo, Lipovitsky and Lakes Palozero and Khmeleozero). In 2012, M.A. Fadeyeva was involved in the integrated study of planned Zaonezhsky Landscape Reserve. The study was conducted by the Forest Research Institute, KarRC, RAS (Fadeyeva 2013). In 2012, A. V. Kravchenko and M.A. Fadeyeva studied the vascular plant and lichen lora of the mainland shores near the Kizhi Skerries from the village of Oyatevshchina to Lake Vekhozero at the request of Kizhi Museum-Reserve (Fadeyeva & Kravchenko 2013). A list of 137 lichens and related fungi was made up, but it was not presented in the above publication. The lichen samples 208 Reports of the Finnish Environment Institute 40 | 2014 collected by A. V. Kravchenko and M.A. Fadeyeva are in the Karelian Research Centre herbarium (PTZ). Finally, in 2013, Olli Manninen, Kimmo Syrjänen and Margarita Fadeeva joined a Finnish-Russian Zaonezhye expedition in the framework of the BPAN project and collected lichen samples on southeastern part of Zaonezhye Peninsula (see Syrjänen et al. 2014, p. 212). Acknowledgements The author Margarita Fadeeva is thankful for professor Soili Stenroos (Head Curator of Fungi at Botanical Museum/Finnish Museum of Natural History University of Helsinki) for the help during her visits in Helsinki University Herbarium in 2011 and 2012, and for professor Teuvo Ahti for the permanent help in her work. REFERENCES AЧНОrssШЧ, L., AХОбООЯК, N.M., & KЮгЧОЭsШЯК, E. S. (ОНs) 2009. ., . ., . . ДSЮrЯОв ШП ЛТШХШРТМКХХв ЯКХЮКЛХО ПШrОsЭs ТЧ NШrЭС-АОsЭОrЧ EЮrШЩОКЧ RЮssТК. VШХ 2. IНОЧЭТiМКЭТШЧ ЦКЧЮКХ ШП sЩОМТОs ЭШ ЛО ЮsОН НЮrТЧР sЮrЯОв КЭ sЭКЧН ХОЯОХЖ. – SЭ-PОЭОrsЛЮrР. 258 Щ. AСЭТ T., BШвМСЮФ M. 2006. TСО ЛШЭКЧТМКХ УШЮrЧОвs ШП A. K. CКУКЧНОr КЧН J. I. LТЧНrШЭС ЭШ KКrОХТК КЧН OЧОРК RТЯОr ТЧ 1898 КЧН 1899, аТЭС К ХТsЭ ШП ЭСОТr ЛrвШЩСвЭО КЧН ХТМСОЧ МШХХОМЭТШЧs. – NШrrХТЧТК 14: 1–65. BОгКТs, E. K. 1911. . . . ДRОЩШrЭ ШЧ ЛШЭКЧТМКХ sЭЮНв ШП LКФО OЧОРК sСШrОs ПrШЦ PОЭrШгКЯШНsФ ЭШ PШЯОЧОЭsЖ. − IЧ: PrШМООНТЧРs ШП ЭСО SЭ.PОЭОrsЛЮrР NКЭЮrКХТsЭs’ SШМТОЭв. BШЭКЧв SОМЭТШЧ. 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VШХ. 2: 17—60. (IЧ RЮssТКЧ). HОrЭОХ, H. 1970. PКrКsТЭТsМСО ХТМСОЧТsТОrЭО ArЭОЧ НОr SКЦЦОХРКЭЭЮЧР LОМТНОК ТЧ EЮrШЩК. − HОrгШРТК. (1): 405–438. MКРЧЮssШЧ, A. H. 1939. SЭЮНТОs ТЧ sЩОМТОs ШП LОМКЧШrК ЦКТЧХв ЭСО AsЩТМТХТК РТЛЛШsК РrШЮЩ. − KЮЧРХТРК SЯОЧsФК VОЭОЧsФКЩsКФКНОЦТОЧs HКЧНХТЧРКr. SОrТОs 3. 17(5): 1–182. NШrНТЧ, I. 1972. CКХШЩХКМК, sОМЭ. GКsЩКrrТЧТК ТЧ NШrНОЮrШЩК. – TКбШЧШЦТsФК ШМС ОФШХШРТsФК SЭЮНТОr. UЩsКХК, 184 Щ. Reports of the Finnish Environment Institute 40 | 2014 209 NШrНТЧ, A., MШЛОrР, R., TøЧsЛОrР, T., VТЭТФКТЧОЧ, O., DКХsтЭЭ, й., MвrНКХ, M., SЧТЭЭТЧР, D. & EФЦКЧ, S. 2011. SКЧЭОssШЧ’s CСОМФХТsЭ ШП FОЧЧШsМКЧНТКЧ LТМСОЧ-ПШrЦТЧР КЧН LТМСОЧТМШХШЮs FЮЧРТ. VОrsТШЧ AЩrТХ 29, 2011 – СЭЭЩ://130.238.83.220/sКЧЭОssШЧ/СШЦО.ЩСЩ (12 NШЯОЦЛОr 2014). NШrrХТЧ, J. P. 1876: FХШrК KКrОХТКО OЧОРОЧsТs. II. LТМСОЧОs. − MОННОХКЧНОЧ SШМ. FКЮЧК FХШrК FОЧЧТМК 1:1–46. NвХКЧНОr, А. 1866 К. LТМСОЧОs LКЩЩШЧТКО ШrТОЧЭКХТs. − NШЭТsОr SтХХsФ. FКЮЧК FХШrК FОЧЧТМК FörСКЧНХ.8: 101–192 (Preprint). NвХКЧНОr, А. 1866 М. AННОЧНК ЧШЯК КН LТМСОЧШРrКЩСТКЦ ОЮrШЩКОКЦ. CШЧЭТЧЮКЭТШ ЭОrЭТК. − FХШrК 49: 417–421. SвrУтЧОЧ, K., MКЧЧТЧОЧ O, & FКНООЯК, M.A. 2014. RОН-ХТsЭОН КЧН ТЧНТМКЭШr ХТМСОЧs ШП ГКШЧОгСвО PОЧТЧsЮХК. − IЧ: LТЧНСШХЦ, T., JКФШЯХОЯ, J. & KrКЯМСОЧФШ, A. (ОНs.), BТШРОШРrКЩСв, ХКЧНsМКЩОs, ОМШsвsЭОЦs КЧН sЩОМТОs ШП ГКШЧОгСвО PОЧТЧsЮХК, ТЧ OЧОРК LКФО, RЮssТКЧ KКrОХТК. RОЩШrЭs ШП ЭСО FТЧЧТsС EЧЯТrШЧЦОЧЭ IЧsЭТЭЮЭО 2014/40: 223-230. TШХЩвsСОЯК, . ВЮ., LвЮЛТЦШЯК . G., GШrsСТЧК . S., SТгШЯК . P. 2001. . ., . ., Г рш а Е. ., ва . П. . 3. ДLТМСОЧ lШrК ШП КЧМТОЧЭ аШШНОЧ КrМСТЭОМЭЮrКХ ЦШЧЮЦОЧЭs. 3. CСЮrМС ШП TrКЧsiРЮrКЭТШЧ ТЧ KТгСТЖ. − IЧ: VОsЭЧТФ MШsФШЯsФШРШ ЮЧТЯОrsТЭОЭК, SОr. 16. BТШХШРв 1: 24–33. (IЧ RЮssТКЧ). VКТЧТШ, E. A. 1923−1934. LТМСОЧШРrКЩСТК FОЧЧТМК. I–IV. − AМЭК SШМ. FКЮЧК FХШrК FОЧЧТМК 1921. 49(2): 1–274 (1921). 53(1): 1–340 (1922). 57(1): 1–138 (1927). 57(2–3): 1–531 (1927). VОrОsСМСКРТЧ, G. ВЮ. 1921. . . . 1920 ДOХШЧОЭs sМТОЧЭТiМ ОбЩОНТЭТШЧ. PrОХТЦТЧКrв rОЩШrЭ ШЧ 1920 sЭЮНвЖ. 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List of lichens and allied fungi of Zaonezhye Peninsula The list is compiled on basis of published data and from recent collections, as well as from specimens in the herbaria of Karelian Scientiic Center of Russian Academy of Sciences, Petrozavodsk (PTZ), Institute of Botany of Russian Academy of Sciences, St. Petersburg PAH (LE), Botanical Museum of the Finnish Museum of Natural History, University of Helsinki (H), and University of Turku (TUR). Bol. Klim.Isl. − Bolshoi Klimenetsky Island * - lichenicolous fungus, + - saprophytic fungus The nomenclature follows Nordin et al. (2011). The list incorporates 298 species and infraspeciic taxa of lichens, 3 species of lichenicolous fungi, and 3 species of saprotrophic fungi 1. 2. 3. 4. 5. 6. 7. 210 Acarospora fuscata (Schrad.) Th. Fr. – Norrlin 1876; Fadeeva 2013; Podyelniki, on stones in the wall around old chapel, 08.07.2012, M.A. Fadeeva, PTZ. Acarospora glaucocarpa (Ach.) Körb. – Norrlin 1876. Adelolecia kolaёnsis (Nyl.) Hertel & Rambold – Norrlin 1876; Vainio 1934. Alectoria sarmentosa (Ach.) Ach. – Polya village -S, herb-rich spruce mire, on twigs of spruce, 25.08.2013, K. Syrjänen, TUR; Velikaya Guba -SW, Zubovo -N, NE of the Lake Pužej, siliceous east facing cliff, on rock wall, 24.08.2013, K.Syrjänen, TUR. Alyxoria varia (Pers.) Ertz & Tehler – Shunga, 1870, J. P. Norrlin, . Amandinea coniops (Wahlenb.) M.Choisy ex Scheid. & H. Mayrhofer – Norrlin 1876. Amandinea punctata (Hoffm.) Coppins & Scheid. – Fadeeva 2000. Reports of the Finnish Environment Institute 40 | 2014 8. 9. 10. 11. 12. 13. 14. 15. 16. 17. 18. 19. 20. 21. 22. 23. 24. 25. 26. 27. 28. 29. 30. 31. 32. 33. 34. 35. 36. Arctoparmelia centrifuga (L.) Hale – Fadeeva 2013; NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. Arctoparmelia incurva (Pers.) Hale – Fadeeva 2013. Arthonia cinereopruinosa Schaer. – Nylander 1866 a; Norrlin 1876. Arthonia mediella Nyl.– Norrlin 1876. Arthonia radiata (Pers.) Ach. – Norrlin 1876. Arthonia spadicea Leight. – Norrlin 1876. Aspicilia cinerea (L.) Körb. – Norrlin 1876. Aspicilia verrucigera Hue – Bol. Klim.Isl., 1863, A. Kullhem, H: Magnusson 1939. Bacidia bagliettoana (A. Massal. & De Not.) Jatta – Norrlin 1876; Vainio 1922; Fadeeva 2013; Kizhi Island, on Ulmus laevis, 27.05.1999, M.A. Fadeeva, PTZ. Bacidia rubella (Hoffm.) A. Massal. – Norrlin 1876; Vainio 1922. Bacidia subincompta (Nyl.) Arnold – Norrlin 1876; Vainio 1922. Baeomyces carneus Flörke – Fadeeva 2013. Bellemerea cinereorufescens (Ach.) Clauzade & Cl. Roux – Norrlin 1876. Bellemerea diamarta (Ach.) Hafellner & Cl. – Norrlin 1876. Biatora pallens (Kullh.) Printzen – Zubovo village, on Sorbus aucuparia, 03.07.2012, M.A. Fadeeva, PTZ. Biatora vernalis (L.) Fr. – Tolpysheva et al. 2001. Blastenia crenularia (With.) Arup et al. – Norrlin 1876. Botryolepraria lesdainii (Hue) Canals & al. – Fadeeva 2013. Bryoria capillaris (Ach.) Brodo & D. Hawksw. – Fadeeva 2013; NW shore of Lake Vekhkozero, on twigs of spruce 11.07.2012, M.A. Fadeeva, PTZ. Bryoria fremontii (Tuck.) Brodo & D. Hawksw. – Vegoruksy Village, ca. 1.5 km SE, forest-side edge of dry grassland on sandy ground, A.V. Kravchenko, 19.08.2010, PTZ. Bryoria furcellata (Fr.) Brodo & D. Hawksw. – Fadeeva 2000; Tolpysheva et al. 2001; Zubovo village, on trunk and twigs of pine, 03.07.2012, M.A. Fadeeva, PTZ; Podyelniki, on trunk and twigs of pine, 10.07.2012, M.A. Fadeeva, PTZ. Bryoria fuscescens (Gyeln.) Brodo & D. Hawksw. – Surroundings of Zubovo village, on trunks and twigs of pine, 03.07.2012, M.A. Fadeeva, PTZ; Podyelniki, on pine, 10.07.2012, M.A. Fadeeva, PTZ; Zubovo –N, on twigs of spruce, 24.08. 2013, K. Syrjänen, TUR. Bryoria implexa (Hoffm.) Brodo & D.Hawksw. – Fadeeva 2013. Bryoria nadvornikiana (Gyeln.) Brodo & D. Hawksw. – Tolpysheva et al. 2001; Fadeeva 2013; North to Zubovo village, on dry Juniperus communis, 04.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013, Podyelniki, on dry Juniperus communis, 10.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on twigs of spruce, 11.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Polya village, on Betula, 26.06.2013, M.A. Fadeeva, PTZ; Tambitsy village NW, Kaskoselga E, spruce bog at border of a fen, on birch and spruce, 28.08.2014 K. Syrjänen, TUR. Bryoria simplicior (Vain.) Brodo & D. Hawksw. – Tolpysheva et al. 2001. Buellia disciformis (Fr.) Mudd – Fadeeva, 2000; Zubovo village, on bark of Sorbus aucuparia, 03.07.2012, M.A. Fadeeva, PTZ. Calicium salicinum Pers. – Norrlin 1876; Zubovo village, on stump of Salix caprea, 04.07.2012, M.A. Fadeeva, PTZ. Calicium trabinellum (Ach.) Ach. – Podyelniki, on wood of pine, 10.07.2012, M.A. Fadeeva, PTZ. Calicium viride Pers. – On bark of spruce, Podyelniki, 07.07.2012, western shore of Lake Vekhkozero, 11.07.2012, M.A. Fadeeva, PTZ. Reports of the Finnish Environment Institute 40 | 2014 211 37. Caloplaca cerina (Hedw.) Th.Fr. – Tolpysheva et al. 2001; Zubovo village, on Prunus padus, 03.07.2012, M.A. Fadeeva, PTZ. 38. Caloplaca saxicola (Hoffm.) Nordin – Norrlin 1876; Nordin 1972. 39. Candelaria concolor (Dicks.) Stein – Tolpysheva et al. 2001; probably this is Candelaria paciica M. Westb. & Arup, see: Westberg & Arup 2010. 40. Candelariella aurella (Hoffm.) Zahlbr. – Tolpysheva et al. 2001; Kizhi Island, on Ulmus laevis, 28.05.1999, M.A. Fadeeva, PTZ. 41. Candelariella coralliza (Nyl.) H. Magn. – Ersenevo village, abandoned ield, on stones, 05.07.2012, M.A. Fadeeva, PTZ. 42. Candelariella vitellina (Hoffm.) Müll. Arg. – Tolpysheva et al., 2001; Fadeeva 2013; 43. Candelariella xanthostigma (Ach.) Lettau – Fadeeva, 2000, Pustoy Bereg, abandoned village, on Ulmus laevis, 04.07.2012, M.A. Fadeeva, PTZ. 44. Catillaria erysiboides (Nyl.) Th. Fr. – Nylander 1866 a; Norrlin 1876; Vainio 1934; 45. Cetraria aculeata (Schreb.) Fr. – Bol. Klim. Isl., Lukovo Bay, on rock, 05.07.2004, M.A. Fadeeva PTZ. 46. Cetraria ericetorum Opiz – Fadeeva 2000. 47. Cetraria islandica (L.) Ach. subsp. islandica – Fadeeva 2000, 2013; Podyelniki, on ground, 10.07.2012, M.A. Fadeeva, PTZ. 48. Cetraria odontella (Ach.) Ach. – Norrlin 1876; Fadeeva 2013. 49. Cetraria sepincola (Ehrh.) Ach. – Tolpysheva et al. 2001; Fadeeva 2000; Podyelniki, on stones in the wall around old chapel, 08.07.2012, M.A. Fadeeva, PTZ. 50. Cetrelia cetrarioides (Delise & Duby) W. L. Culb. & C. F. Culb. – on rocks, Paleostrov Island, 03.07.2004, M.A. Fadeeva, PTZ; Bolshoi Lelikovsky Island, Radkolye Cape, 06.07.2004, M.A. Fadeeva, PTZ. 51. Chaenotheca brachypoda (Ach.) Tibell – Fadeeva 2013; Fadeeva & Kravchenko 2013; Zubovo village, stump of Salix caprea, 04.07.2012, M.A. Fadeeva, PTZ; Polya village, stump of Salix caprea, 26.06.2013, M.A. Fadeeva, PTZ; surroundings of Lake Rugozero, stump of birch, 27.06.2013, M.A. Fadeeva, PTZ. 52. Chaenotheca brunneola (Ach.) Müll. Arg. – Western shore of Lake Vekhkozero, on bark of spruce, 11.07.2012, M.A. Fadeeva, PTZ. 53. Chaenotheca chlorella (Ach.) Müll. Arg. – Tambitsy-NW towards Kaskoselga, herbrich - grassy swamp forest, on birch snag, 28.08. 2013, K. Syrjänen, TUR; Tambitsy-SW, mires NW of Kurnejnavolok cape, on old Salix pentandra, 27.08. 2013, K. Syrjänen, TUR; Polya village – S, on old birch, 25.08.2013, K. Syrjänen, TUR. 54. Chaenotheca chrysocephala (Turner ex Ach.) Th. Fr. – Vainio 1927; Fadeeva 2013; Podyelniki, on spruce, 07.07.2012, M.A. Fadeeva, PTZ. 55. Chaenotheca ferruginea (Turner ex Sm.) Mig. – Norrlin 1876; Vainio 1927; Fadeeva 2013; western shore of Lake Vekhkozero, on bark of spruce, 11.07.2012, M.A. Fadeeva, PTZ. 56. Chaenotheca furfuracea (L.) Tibell – Vainio 1927; Fadeeva 2000; Fadeeva & Kravchenko 2013; south-eastern shore of Lake Vekhkozero, on spruce along brook, 11.07.2012, M.A. Fadeeva, PTZ. 57. Chaenotheca gracilenta (Ach.) Mattsson & Middelb. – Polya village, on roots of fallen spruce, 26.06.2013, M.A. Fadeeva, PTZ; Polya village -S, decaying stump, 25.08. 2013, K. Syrjänen, TUR. 58. Chaenotheca laevigata Nádv. – Surroundings of Zubovo village, on stump of Salix caprea, 04.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013. 59. Chaenotheca subroscida (Eitner) Zahlbr. – Lipovitsy, along a brook, on stump of birch, 25.06.2013, M.A. Fadeeva, PTZ. 60. Chaenotheca trichialis (Ach.) Th. Fr. – Vainio 1927; surroundings of Zubovo village, on stump of pine, 04.07.2012, M.A. Fadeeva, PTZ. 212 Reports of the Finnish Environment Institute 40 | 2014 61. Chaenotheca xyloxena Nádv. – Surroundings of Zubovo village, on stump of Salix caprea, 04.07.2012, M.A. Fadeeva, PTZ. 62. *Chaenothecopsis hospitans (Th. Fr.) Tibell – “Ad Dianova-gora, saxicola, Simming, 1863”: Norrlin 1876; Vainio 1927; Zhurbenko & Ahti 2005. 63. Chrysothrix chlorina (Ach.) J. R. Laundon – Fadeeva 2013; Podyelniki, on stones in the wall around old chapel, 10.07.2012, M.A. Fadeeva, PTZ. 64. Circinaria caesiocinerea (Nyl. ex Malbr.) A. Nordin et al. – Fadeeva 2000. 65. Cladonia amaurocraea (Flörke) Schaer. – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ; northern shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 66. Cladonia arbuscula (Wallr.) Flot. – Fadeeva 2000; Tolpysheva et al. 2001; Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ; northern shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 67. Cladonia mitis Sandst. – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, northern shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 68. Cladonia bacilliformis (Nyl.) Glück – Podyelniki, on dry Juniperus communis, 10.07.2012, M.A. Fadeeva, PTZ. 69. Cladonia botrytes (K. G. Hagen) Willd. – Tolpysheva et al. 2001; Podyelniki, on roots of fallen spruce, 07.07.2012, M.A. Fadeeva, PTZ. 70. Cladonia cenotea (Ach.) Schaer. – Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ. 71. Cladonia chlorophaea (Flörke ex Sommerf.) Spreng. – Fadeeva 2013; Northern end of Kizhi Island, abandoned ield, on stones, 28.05.1999, M.A. Fadeeva, PTZ; Rechka abandoned village, on ground, 04.07.2012, M.A. Fadeeva, PTZ. 72. Cladonia coccifera (L.) Willd. – Fadeeva 2013; northern shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 73. Cladonia coniocraea (Flörke) Spreng. – Fadeeva 2013; surroundings of Zubovo village, on bark of pine, 03.07.2012, M.A. Fadeeva, PTZ. 74. Cladonia cornuta (L.) Hoffm. s.l. – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, northern shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 75. Cladonia crispata (Ach.) Flot. var. crispata – Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ. 76. Cladonia deformis (L.) Hoffm. – Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ. 77. Cladonia decorticata (Flörke) Spreng. – Fadeeva 2013. 78. Cladonia imbriata (L.) Fr. – Tolpysheva et al. 2001; Fadeeva 2013; Zubovo village, on Salix caprea, 03.10.2012, M.A. Fadeeva, PTZ; Podyelniki, on roots of fallen spruce, 07.07.2012, M.A. Fadeeva, PTZ. 79. Cladonia furcata (Huds.) Schrad. – Fadeeva 2000, 2013; NW shore of Lake Vekhkozero, on moss-covered stones in the rock wall (seismic dislocation), 11. 07.2012, M.A. Fadeeva, PTZ 80. Cladonia gracilis (L.) Willd. ssp. turbinata (Ach.) Ahti – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 08.07.2012, NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11. 07.2012, M.A. Fadeeva, PTZ. 81. Cladonia macilenta Hoffm. – Fadeeva 2013. 82. Cladonia phyllophora Hoffm. – Volkostrov Island, on soil, 31.05.1999, M.A. Fadeeva, PTZ; Podyelniki, abandoned ield, on moss-covered stones, 08.07.2012, M.A. Fadeeva, PTZ. Reports of the Finnish Environment Institute 40 | 2014 213 83. Cladonia pleurota (Flörke) Schaer. – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 08.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11. 07.2012, M.A. Fadeeva, PTZ. 84. Cladonia pocillum (Ach.) Grognot – Fadeeva 2013. 85. Cladonia pyxidata (L.) Hoffm. – Tolpysheva et al. 2001; Northern end of Ersenevo village, stone shore of Lake Onega, on ground, 05.07.2012, M.A. Fadeeva, PTZ. 86. Cladonia rangiferina (L.) F. H. Wigg. – Tolpysheva et al. 2001; Fadeeva 2000, 2013; Podyelniki, abandoned ield, on moss-covered stones, 08.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11. 07.2012, M.A. Fadeeva, PTZ. 87. Cladonia squamosa Hoffm. – Fadeeva 2013; NW shore of Lake Vekhkozero, on moss-covered stones in the rock wall (seismic dislocation), 11.07.2012, M.A. Fadeeva, PTZ. 88. Cladonia stellaris (Opiz) Pouzar & Vězda – Fadeeva 2000, 2013; Podyelniki, abandoned ield, on moss-covered stones, 08.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11. 07.2012, M.A. Fadeeva, PTZ. 89. Cladonia stygia (Fr.) Ruoss – Fadeeva 2013. 90. Cladonia subulata (L.) F. H. Wigg. – Fadeeva 2013; Zubovo village, on stones in abandoned ield, 03.10.2012, M.A. Fadeeva, PTZ. 91. Cladonia sulphurina (Michx.) Fr. – Zubovo village, on stones in abandoned ield, 03.10.2012, M.A. Fadeeva, PTZ. 92. Cladonia symphycarpa (Flörke) Fr. – Yuzhny Oleny Island, on dolomites, 20.07.2000, M.A. Fadeeva, PTZ. 93. Cladonia turgida Hoffm. – Fadeeva 2013; NW shore of Lake Vekhkozero on moss-covered stones in the rock wall (seismic dislocation), 11. 07.2012, M.A. Fadeeva, PTZ. 94. Cladonia uncialis (L.) F. H. Wigg. ssp. uncialis – Fadeeva 2000, 2013; NW shore of Lake Vekhkozero, on moss-covered stones in the rock wall (seismic dislocation), 11. 07.2012, M.A. Fadeeva, PTZ. 95. Cladonia verticillata (Hoffm.) Schaer. – Podyelniki, abandoned ield, on mosscovered stones, 10.07.2012, M.A. Fadeeva, 2012 PTZ. 96. Collema laccidum (Ach.) Ach. – Kuzaranda village, on marble, 04.07.2004, M.A. Fadeeva, PTZ. 97. Collema furfuraceum (Arnold) Du Rietz – Fadeeva 2013. 98. Coenogonium luteum (Dicks.) Kalb & Lücking – Nylander 1866 a; Norrlin 1876. 99. Coenogonium pineti (Ach.) Lücking & Lumbsch – Nylander 1866 a; Norrlin 1876; Tambitsy-NW towards Kaskoselga, swamp forest close to the bog, on birch snag, 28.08.2013, K. Syrjänen, TUR. 100. Cyphelium karelicum (Vain.) Räsänen – Nylander 1866 ; Norrlin 1876; Vainio, 1922. 101. Dendriscocaulon umhausense (Auersw.) Degel. – Norrlin 1876. 102. Dermatocarpon luridum (With.) J.R. Laundon – Norrlin 1876. 103. Dermatocarpon miniatum (L.) W. s.l. – Ashepnavolok Cape, 08.1870, J.P. Norrlin, . 104. Diploschistes scruposus (Schreb.) Norman – Fadeeva 2013; Podyelniki, abandoned ield, on moss-covered stones, 10.07.2012, M.A. Fadeeva, PTZ. 105. Enchylium polycarpon (Hoffm.) Otálora et al. – Fadeeva 2013. 106. Epilichen scabrosus (Ach.) Clem. – Dianova Gora, on Baeomyces rufus, A. Kullhem, H: Norrlin 1876; Zhurbenko & Ahti 2005. 107. Evernia divaricata (L.) Ach. – western shore of Bol. Klim. Isl., [Kishi (Vatnavolok)], on spruce twigs, 1863, A. Kullhem, H: Norrlin 1876; Lipovitsy, along the brook, on spruce twigs, 25.06.2013, M.A. Fadeeva, PTZ; Polya village, on spruce twigs, 26.06.2013, M.A. Fadeeva, PTZ; Uzkaya Salma, on spruce twigs, 28.06.2013, M.A. Fadeeva, PTZ; Tambitsy-SW, mires to the NW of the cape Kurnejnavolok, 214 Reports of the Finnish Environment Institute 40 | 2014 herb-rich – grassy swamp forests at border of a pine bog, on twigs of spruces, 27.08.2013, K. Syrjänen, TUR; Polya village –S, herb-rich swamp forest, on old birch, 25.08. 2013, K. Syrjänen, TUR; Velikaya Guba -SW, Zubovo –N, North east from Lake Pužej, open mire below an east facing cliff, on birch, 24.08.2014, K. Syrjänen, TUR; Tambitsy -N. W-NW from the small cape Tolstyj Navolok, swamp forest, on trunk of Alnus glutinosa, 26.8.2013, K. Syrjänen, TUR. 108. Evernia mesomorpha Nyl. – Fadeeva 2013; Fadeeva & Kravchenko 2013; surroundings of Zubovo village, on bark of pine, Salix caprea, Juniperus, birch, 03.07.2013, M.A. Fadeeva, PTZ; on bark of pine, surroundings of Lake Rugozero Lake, 27.06.2013, M.A. Fadeeva, PTZ; Uzkaya Salma, on bark of pine, Juniperus comminis, 28.06.2013, M.A. Fadeeva, PTZ; Velikaya Guba -SW, Zubovo –N, northeast from Lake Pužej, open oligotropic mire, on trunk of birch, 24.08.2013, K. Syrjänen, TUR. 109. Evernia prunastri (L.) Ach. – Tolpysheva et al. 2001; west of Zubovo village, on Sorbus aucuparia, 03.07.2012, M.A. Fadeeva, PTZ. 110. Fuscidea pusilla Tønsberg – Fadeeva 2013. 111. Fuscopannaria praetermissa (Nyl.) P. M. Jørg. – Fadeeva 2013; NW shore of Lake Vekhkozero, on moss-covered stones in the rock wall (seismic dislocation), 11. 07.2012, M.A. Fadeeva, PTZ. 112. Graphis scripta (L.) Ach. – Bol. Klim. Isl., on bark of Salix, 12.06.1863, Th. Simming, H: Nylander 1866 a; Norrlin 1876; NE end of Bol. Klim. Isl., on dry Sorbus aucuparia, 27.05.1999, M.A. Fadeeva, PTZ. 113. Gyalecta fagicola (Hepp ex Arnold) Kremp. – Fadeeva 2001, 2003, s.n. Gyalecta truncigena (Ach.) Hepp; Fadeeva 2013; eastern shore Kizhi Island, north of Yamka village, on old trees of Ulmus laevis, 27.05.1999, M.A. Fadeeva, PTZ; North to Zubovo village, on aspen, 04.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013. 114. Gyalecta truncigena (Ach.) Hepp – 4 km N to Velikaya Guba village, on trunk of old aspen, 26.06.2013, M.A. Fadeeva, PTZ. 115. Gyalecta ulmi (Sw.) Zahlbr. – Dianova Gora, 1863, Th. Simming, H; Lipovitsy village –SW, to the west of Lake Bezdonnoe, brook-side herb-rich deciduous forest, on old Ulmus, 23.08. 2013, K. Syrjänen, TUR. 116. Gyalolechia lavorubescens (Huds.) Søchting et al. – Tolpysheva et al. 2001. 117. *Homostegia piggotii (Berk. et Broome) P. Karst. – Dianova Gora, on Parmelia saxatilis, 1870, J.P. Norrlin, H: Zhurbenko & Ahti 2005. 118. Hypocenomyce scalaris (Ach.) M.Choisy – Fadeeva 2013; NW shore of Lake Vekhkozero, on bark of pine, M.A. Fadeeva, 11.07.2012, PTZ. 119. Hypogymnia physodes (L.) Nyl. – Tolpysheva et al. 2001; Fadeeva 2000, 2013; Zubovo village, on spruce, pine, 03.07.2012, M.A. Fadeeva, PTZ; Zubovo village, on trunk of Alnus glutinosa, 03.07.2012, M.A. Fadeeva, PTZ. 120. Hypogymnia tubulosa (Schaer.) Hav. – Tolpysheva et al. 2001; Fadeeva 2000, 2013; Pustoy Bereg abandoned village, on birch, 04.07.2012, M.A. Fadeeva, PTZ. 121. Hypogymnia vittata (Ach.) Parrique – Norrlin 1876; Komlevo abandoned village, on moss-covered basement rocks, 17.08.2010, M.A. Fadeeva, PTZ. 122. Icmadophila ericetorum (L.) Zahlbr. – Norrlin 1876. 123. Immersaria cupreoatra (Nyl.) Calat. & Rambold – Norrlin 1876. 124. Imshaugia aleurites (Ach.) S. L. F. Mey. – Podyelniki, on bark of pine, 10.07.2012, M.A. Fadeeva, PTZ. 125. Lathagrium fuscovirens (With.) Otálora et al. – Fadeeva 2013. 126. Lasallia pustulata (L.) Mérat – Fadeeva 2013. 127. Lecania cyrtella (Ach.) Th.Fr. – Tolpysheva et al. 2001. 128. Lecanora allophana Nyl. – Fadeeva 2013; surroundings of Zubovo village, on old aspens, 04.07.2012, M.A. Fadeeva, PTZ. Reports of the Finnish Environment Institute 40 | 2014 215 129. Lecanora argopholis (Ach.) Ach. – Norrlin 1876. 130. Lecanora dispersa (Pers.) Sommerf. s.l. – Norrlin 1876. 131. Lecanora fuscescens (Sommerf.) Nyl. – Norrlin 1876. 132. Lecanora hagenii (Ach.) Ach. – Tolpysheva et al. 2001. 133. Lecanora intricata (Ach.) Ach. – Podyelniki, on stones, 08.07.2012, M.A. Fadeeva, PTZ. 134. Lecanora leptyrodes (Nyl.) G.B.F. Nilsson – Fadeeva 2000; North to Oyatevshina village, on aspen, 05.07.2012, M.A. Fadeeva, PTZ. 135. Lecanora muralis (Schreb.) Rabenh. – Fadeeva 2013; North to Ersenevo village, on stones in the abandoned ield, 05.07.2012, M.A. Fadeeva, PTZ. 136. Lecanora pulicaris (Pers.) Ach. – Tolpysheva et al. 2001. 137. Lecanora rupicola (L.) Zahlbr. – Fadeeva 2001; Zhurbenko & Ahti 2005. 138. Lecanora saligna (Schrad.) Zahlbr. – Tolpysheva et al. 2001. 139. Lecanora symmicta (Ach.) Ach. s.l. – Severnye Oleny Island, on birch, 29.05.1999, M.A. Fadeeva, PTZ; Podyelniki, on dry Juniperus communis, 08.07.2012, M.A. Fadeeva, PTZ. 140. Lecanora varia (Hoffm.) Ach. – Tolpysheva et al. 2001. 141. Lecidea conluens (Weber) Ach. – Vainio 1934. 142. Lecidea erythrophaea Flörke ex Sommerf. – Norrlin 1876; Tolpysheva et al. 2001; Fadeeva 2013; Severnye Oleny Island, on aspen, 29.05.1999, M.A. Fadeeva, PTZ. 143. Lecidea leprarioides Tønsberg – Lipovitsy, along the brook, on bark of spruce, 25.06.2013, M.A. Fadeeva, PTZ. 144. Lecidea lapicida (Ach.) Ach. var. pantherina Ach. – Norrlin 1876; Vainio 1934. 145. Lecidea tessellata Flörke – Norrlin 1876. 146. Lepraria membranacea (Dicks.) Vain. – Fadeeva 2013. 147. Leproplaca obliterans (Nyl.) Arup et al. – Norrlin 1876. 148. Leptogium saturninum (Dicks.) Nyl. – Fadeeva 2000, 2013; Fadeeva & Kravchenko 2013; surroundings of Zubovo village, on bark of aspen, 03.07.2012, M.A. Fadeeva, PTZ; Polya village, on bark of aspen, 26.06.2013, M.A. Fadeeva, PTZ; 149. Lichenomphalia umbellifera (L. : Fr.) Redhead & al. – Fadeeva 2013. 150. Lobaria pulmonaria (L.) Hoffm. – Fadeeva 2000, 2013; surroundings of Zubovo village, on Populus tremula, Sorbus aucuparia and Juniperus communis, 03.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; surroundings of Zubovo village, on Salix caprea, 04.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Podyelniki, on old aspens, 10.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on aspen, 11.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; NW shore of Lake Vekhkozero, on Salix caprea, 11.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko, 2013; Lipovitsy, along the brook, on drying Sorbus aucuparia, 25.06.2013, M.A. Fadeeva, PTZ; Polya village, stump of Salix caprea, 26.06.2013, M.A. Fadeeva, PTZ; Tambitsy N, W-NW from the small cape Tolstyj Navolok, mixed herb-rich forest, fallen on ground from a large aspen, with sporophytes, 26.08. 2013, K. Syrjänen, TUR. 151. Lobaria scrobiculata (Scop.) DC. – Fadeeva 2013; Lipovitsy, along the brook, on drying Sorbus aucuparia, 25.06.2013, M.A. Fadeeva, PTZ. 152. Lobothallia melanaspis (Ach.) Hafellner – Bolshoi Lelikovsky Island, Radkolye Cape, on shore rocks, 06.07.2004, M.A. Fadeeva, PTZ. 153. Lopadium coralloideum (Nyl.) Lynge – Norrlin 1876; Vainio 1922. 154. Lopadium disciforme (Flot.) Kullh. – Lipovitsy, along the brook, on bark of spruce, 25.06.2013, M.A. Fadeeva, PTZ. 155. Loxospora elatina (Ach.) A. Massal. – Podyelniki, on bark of Juniperus communis, 10.07.2012, M.A. Fadeeva, PTZ. 216 Reports of the Finnish Environment Institute 40 | 2014 156. Megaspora verrucosa (Ach.) Hafellner & V. Wirth – surroundings of Zubovo village, on old aspens, 03.07.2012, M.A. Fadeeva, PTZ: Fadeev & Kravchenko 2013; 157. Melanelia hepatizon (Ach.) A. Thell. – Fadeeva 2013; Shunga, 1870, J.P. Norrlin, ; Podyelniki, abandoned iels, on stones, 10.07.2012, M.A. Fadeeva, PTZ. 158. Melanelia stygia (L.) Essl. – Fadeeva 2013. 159. Melanelixia fuliginosa (Fr. ex Duby) O.Blanco et al. – Fadeeva 2013. 160. Melanelixia subaurifera (Nyl.) O. Blanco & al. – Dianova Gora, 1863, A. Kullhem, H; between Tipinitsy village and Varnavolok Cape, on aspen, 04.07.2004, M.A. Fadeeva, PTZ; North to Zubovo village, on Sorbus aucuparia, 03.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013. 161. Melanohalea exasperata (De Not.) O. Blanco & al. – Fadeeva 2000; Tolpysheva et al. 2001; Fadeeva & Kravchenko 2013; Paleostrov Island, on Tilia cordata, 03.07.2004, M.A. Fadeeva, PTZ; North to Zubovo village, on Sorbus aucuparia, Prunus padus, Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ. 162. Melanohalea exasperatula (Nyl.) O. Blanco & al. – The northern end of Kizhi Island, on Ulmus laevis, 30.05.1999, M.A. Fadeeva, PTZ. 163. Melanohalea olivacea (L.) O. Blanco & al. – Fadeeva 2000; Tolpysheva et al. 2000; surroundings of Zubovo village, on Salix caprea, on birch, 03.07.2012, M.A. Fadeeva, PTZ. 164. Melanohalea septentrionalis (Lynge) O. Blanco & al. – Tolpysheva et al. 2001. 165. Micarea denigrata (Fr.) Hedl. – North to Zubovo village, on stump of pine, 03.07.2012, M.A. Fadeeva, PTZ. 166. +Microcalicium arenarium (Hampe ex A. Massal.) Tibell – Lipovitsy, along the brook, on roots of fallen spruce, 25.06.2013, M.A. Fadeeva, PTZ. 167. *Microcalicium disseminatum (Ach.) Vain. – Rybya Bay of Lake Onega, on bark of spruce, 11.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Lipovitsy, along the brook, on bark of spruce, on Chaenotheca sp., 25.06.2013, M.A. Fadeeva, PTZ; Polya village, stump of birch, 26.06. 2013, M.A. Fadeeva, PTZ. 168. Montanelia disjuncta (Erichsen) Divakar et al. – Fadeeva 2013; Podyelniki, on stones, 08.07.2012, M.A. Fadeeva, PTZ. 169. Montanelia panniformis (Nyl.) Divakar et al. – Fadeeva 2013. 170. Montanelia sorediata (Ach.) Divakar et al. – Kizhi Island, on Kizhi church wall, 31.05.1999, M.A. Fadeeva, PTZ. 171. Mycobilimbia carneoalbida (Müll. Arg.) S.Ekman & Printzen – Fadeeva 2000, 2013; Rybya Bay of Lake Onega, on bark of aspen, 11.07.2012, M.A. Fadeeva, PTZ. 172. Mycobilimbia epixanthoides (Nyl.) Vitik. et al. ex Hafellner et Türk – Nylander 1866 a, b; Norrlin 1876; Vainio 1922; Fadeeva 2000, 2003, 2013; Zhurbenko & Ahti 2005; North to Zubovo village, on stump of aspen, 03.07.2012, M.A. Fadeeva, PTZ. 173. Mycobilimbia tetramera (De Not.) Vitik. et al. ex Hafellner & Türk – Vainio 1922. 174. Mycoblastus sanguinarius (L.) Norman – Fadeeva 2000, 2013. 175. +Mycocalicium subtile (Pers.) Szatala – Bol. Klim. Isl., 1863, Th. Simming, H. 176. Myriospora heppii (Nägeli ex Körb.) Hue – Norrlin 1876. 177. Myriospora smaragdula (Wahlenb. ex Ach.) Nägeli ex Uloth – Norrlin 1876. 178. Naetrocymbe punctiformis (Pers.) R. C. Harris – Norrlin 1876. 179. Nephroma bellum (Spreng.) Tuck. – North to Zubovo village, on aspen, Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on bark of aspen, 11.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Lipovitsy, along the brook, on drying Sorbus, 25.06.2013, M.A. Fadeeva, PTZ; Polya village -S, herb-rich swamp forest, on large Salix pentandra, 25.08. 2013, K. Syrjänen, TUR. Reports of the Finnish Environment Institute 40 | 2014 217 180. Nephroma parile (Ach.) Ach. – Fadeeva 2000, 2013; Fadeeva & Kravchenko 2013; North to Zubovo village, on aspen, 03.07.2012, M.A. Fadeeva, PTZ; Rybya Bay of Lake Onega, on bark of aspen, 11.07.2012, M.A. Fadeeva, PTZ. 181. Nephroma resupinatum (L.) Ach. – Fadeeva 2013; Fadeeva & Kravchenko 2013; Dianova Gora, 1863, Th. Simming, H; Rybya Bay of Lake Onega, on bark of aspen, 11.07.2012, M.A. Fadeeva, PTZ; Lipovitsy, along the brook, on drying Sorbus aucuparia, 25.06.2013, M.A. Fadeeva, PTZ. 182. Ochrolechia androgyna (Hoffm.) Arnold – Dianova Gora, 26.08.1863, Th. Simming, H. 183. Ophioparma ventosa (L.) Norman – Norrlin 1876; Fadeeva 2013; Gorodok Hill, on diabase, 27.06.1924, V. P. Savich & L. I. Savich-Lyubitskaya, LE. 184. Parmelia fraudans (Nyl.) Nyl. – Norrlin 1876; Fadeeva 2000, 2013; Podyelniki, on stones, 08.07.2012, M.A. Fadeeva, PTZ. 185. Parmelia saxatilis (L.) Ach. – Fadeeva 2000, 2013; Podyelniki, abandoned iels, on stones, 10.07.2012, M.A. Fadeeva, PTZ, NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 186. Parmelia sulcata Taylor – Tolpysheva et al. 2001; Fadeeva 2000, 2013; North to Zubovo village, on Sorbus aucuparia, Prunus padus, 03.07.2012, M.A. Fadeeva, PTZ. 187. Parmeliella triptophylla (Ach.) Müll. Arg – Norrlin 1876; Fadeeva 2013; Ashepnavolok Cape, 1870, J.P. Norrlin, H. 188. Parmelina tiliacea (Hoffm.) Hale – Fadeeva et al. 2007; Paleostrov Island, on Tilia cordata, 03.07.2004, M.A. Fadeeva, PTZ. 189. Parmeliopsis ambigua (Wulfen) Nyl. – Tolpysheva et al. 2001; Fadeeva 2013; North to Zubovo village, on Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ. 190. Parmeliopsis hyperopta (Ach.) Arnold – Tolpysheva et al. 2001; Podyelniki, on bark of pine, 10.07.2012, M.A. Fadeeva, PTZ. 191. Peltigera aphthosa (L.) Willd. – Fadeeva 2000, 2013; Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on moss-covered basement rocks, 11.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on moss-covered basement rocks, 11.07.2012, M.A. Fadeeva, PTZ. 192. Peltigera canina (L.) Willd. – Fadeeva 2000, 2013; Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on base of old aspen, 11.07.2012, M.A. Fadeeva, PTZ; Lipovitsy, on aspen, 27.06.2013, M.A. Fadeeva, PTZ. 193. Peltigera collina (Ach.) Schrad. – Bol. Klim. Isl., on stony shore among mosses, 25.06.2007, M.A. Fadeeva, PTZ. 194. Peltigera didactyla (With.) J. R. Laundon – Fadeeva 2013. 195. Peltigera latiloba Holt.-Hartw. – Fadeeva 2013. 196. Peltigera lepidophora (Nyl. ex Vain.) Bitter – Fadeeva 2000, 2013. 197. Peltigera leucophlebia (Nyl.) Gyeln. – Fadeeva 2000, 2013; Fadeeva & Kravchenko 2013; Rybya Bay of Lake Onega, on moss-covered basement rocks, 11.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on moss-covered stones in the rock wall (seismic dislocation), 11. 07.2012, M.A. Fadeeva, PTZ. 198. Peltigera malacea (Ach.) Funck – Fadeeva 2013. 199. Peltigera membranacea (Ach.) Nyl. – NE end of Bol. Klim. Isl., on moss-covered stones, 27.05.1999, M.A. Fadeeva, PTZ. 200. Peltigera neckeri Hepp ex Müll. Arg. – Fadeeva 2000; Kizhi Island, Yamka village, the shore of Lake Onega, on soil, 27.05.1999, M.A. Fadeeva, PTZ; Bol. Klim. Isl., on base of aspen trunk, 27.05.1999, M.A. Fadeeva, PTZ. 201. Peltigera neopolydactyla (Gyeln.) Gyeln. – Bol. Klim. Isl., on dead wood, 29.05.1999, M.A. Fadeeva, PTZ, Rybya Bay of Lake Onega, on moss-covered basement rocks, 11.07.2012, M.A. Fadeeva, PTZ. 218 Reports of the Finnish Environment Institute 40 | 2014 202. Peltigera occidentalis (Å. E. Dahl) Kristinsson – Bol. Klim. Isl., Lukovo Bay, 05.07.2004, P. Uotila, H; Bolshoi Lelikovsky Island, Radkolye Cape, on moss-covered basement rocks, 06.07.2004, M.A. Fadeeva, PTZ. 203. Peltigera polydactylon (Neck.) Hoffm. – Fadeeva 2000, 2013; south-eastern shore Lake Vekhkozero, on moss-covered basement rocks, 11.07.2012, M.A. Fadeeva, PTZ. 204. Peltigera praetextata (Flörke ex Sommerf.) Zopf – Fadeeva 2000, Fadeeva & Kravchenko 2013; surroundings of Zubovo village, on base of aspen, 03.07.2012, M.A. Fadeeva, PTZ; North to Oyatevshina village, on aspen, 05.07.2012, M.A. Fadeeva, PTZ; Lipovitsy, on aspen, 25.06.2013, M.A. Fadeeva, PTZ; Polya village, on stump of Salix caprea, 26.06.2013, M.A. Fadeeva, PTZ. 205. Peltigera rufescens (Weiss) Humb. – Fadeeva 2000, 2013; Bol. Klim. Isl., dry meadow, abandoned ield, on stones, 27.05.1999, M.A. Fadeeva, PTZ, Bol. Klim. Isl., Konda, 06.07.2004, P. Uotila, H; North to Ersenevo village, stony shore of Lake Onega, 05.07.2012, M.A. Fadeeva, PTZ. 206. Peltigera scabrosa Th. Fr. – Fadeeva 2013. 207. Peltigera venosa (L.) Hoffm. – Fadeeva 2013. 208. Pertusaria albescens (Huds.) M. Choisy & Werner – Podyelniki, 10.07.2012, M.A. Fadeeva, 2012, PTZ. 209. Pertusaria amara (Ach.) Nyl. – Tolpysheva et al. 2001; Fadeeva 2013; North to Zubovo village, on aspen, 04.07.2012, M.A. Fadeeva, PTZ. 210. Pertusaria chiodectonoides Bagl. ex A. Massal. – Norrlin 1876. 211. Phaeophyscia ciliata (Hoffm.) Moberg – Kainos Island (NE fromTolvuya), on aspen, 03.07.2004, P. Uotila, ; North to Oyatevshina village, clear-cut for new road, on aspen, 05.07.2012, M.A. Fadeeva, PTZ. 212. Phaeophyscia orbicularis (Neck.) Moberg – Fadeeva 2000; Shunga, on rock, 1870, J.P. Norrlin, H, Kizhi Island, 2 km to the North from the church, on trunk of Ulmus laevis, 26.05. 1999, M.A. Fadeeva, PTZ. 213. Phaeophyscia sciastra (Ach.) Moberg – Bolshoi Lelikovsky Isl., on stony shore of Lake Onega, 06.07.2004, M.A. Fadeeva, PTZ. 214. Phlyctis argena (Spreng.) Flot. – Fadeeva 2000, 2013; North to Zubovo village, on aspen, 03.07.2012, M.A. Fadeeva, PTZ. 215. Phylliscum demangeonii (Moug. & Mont.) Nyl. – Norrlin 1876. 216. Physcia adscendens (Fr.) H. Olivier – Fadeeva 2000; Shunga, 1870, J.P. Norrlin, H; Kainos Island (NE from Tolvuya), on aspen, 03.07.2004, P. Uotila, ; Pustoy Bereg abandoned village, on Ulmus laevis, 04.07.2012, M.A. Fadeeva, PTZ. 217. Physcia aipolia (Ehrh. ex Humb.) Fürnr. – Fadeeva 2000, 2013; Pustoy Bereg abandoned village, on Ulmus laevis, 04.07.2012, M.A. Fadeeva, PTZ. 218. Physcia alnophila (Vain.) Loht., Moberg, Myllys & Tehler – Fadeeva 2013; West to Zubovo village, 03.07.2012, M.A. Fadeeva, PTZ. 219. Physcia caesia (Hoffm.) Fürnr. – Tolpysheva et al. 2001; Fadeeva 2000; Podyelniki, on stone wall of the chapel, 08.07.2012, M.A. Fadeeva, PTZ. 220. Physcia dubia (Hoffm.) Lettau – Pustoy Bereg abandoned village, on Ulmus laevis, 04.07.2012, M.A. Fadeeva, PTZ. 221. Physcia phaea (Tuck.) J. W. Thomson – Norrlin 1876. 222. Physcia stellaris (L.) Nyl. – Fadeeva 2000. 223. Physcia subalbinea Nyl. – Fadeeva 2013. 224. Physcia tenella (Scop.) DC. – Norrlin 1876; Fadeeva 2000; Pustoy Bereg abandoned village, on Ulmus laevis, 04.07.2012, M.A. Fadeeva, PTZ. 225. Physconia detersa (Nyl.) Poelt – Shunga, on rock, 1870, J.P. Norrlin, ; Podyelniki, on old aspens, 10.07.2012, M.A. Fadeeva, PTZ. Reports of the Finnish Environment Institute 40 | 2014 219 226. Physconia distorta (With.) J. R. Laundon – Eastern shore Kizhi Island, on old Ulmus, 27.05. 1999, M.A. Fadeeva, PTZ. 227. Physconia enteroxantha (Nyl.) Poelt – Eastern shore Kizhi Island, on old Ulmus, 27.05. 1999, M.A. Fadeeva, PTZ. 228. Physconia perisidiosa (Erichsen) Moberg – Fadeeva 2013; eastern shore Kizhi Island, on old Ulmus, 27.05.1999, M.A. Fadeeva, PTZ. 229. Pilophorus cereolus (Ach.) Th. Fr – Nylander 1866 a; Norrlin 1876. 230. Placynthiella icmalea (Ach.) Coppins & P. James – Norrlin 1876; Fadeeva 2013; Podyelniki, on roots of fallen spruce, 06.07.2012, M.A. Fadeeva, PTZ; same place, on fallen pine, 10.07.2012, M.A. Fadeeva, PTZ. 231. Placynthium nigrum (Huds.) Gray – Norrlin 1876. 232. Platismatia glauca (L.) W. L. Culb. & C. F. Culb. – Tolpysheva et al. 2001; Fadeeva 2013; Zubovo village, on spruce, 03.07.2012, M.A. Fadeeva, PTZ. 233. Polycauliona candelaria (L.) Frödén et al. – Tolpysheva et al. 2001; Fadeeva 2000; Pustoy Bereg abandoned village, on birch, 04.07.2012, M.A. Fadeeva, PTZ. 234. Polycauliona polycarpa (Hoffm.) Frödén et al. – Fadeeva 2000. 235. Polychidium muscicola (Sw.) Gray – Fadeeva 2013. 236. Porpidia tuberculosa (Sm.) Hertel & Knoph – Shunga, 1870, J.P. Norrlin, H. 237. Protoblastenia rupestris (Scop.) J. Steiner – Norrlin 1876. 238. Protoparmelia badia (Hoffm.) Hafellner – NW shore of Lake Vekhkozero, on blocks of seismo-colluvial scree, 11.07.2012, M.A. Fadeeva, PTZ. 239. Pseudevernia furfuracea (L.) Zopf – Tolpysheva et al. 2001; Fadeeva 2013; Podyelniki, on pine, 10.07.2012, M.A. Fadeeva, PTZ. 240. Psilolechia clavulifera (Nyl.) Coppins – Lipovitsy, along the brook, on roots of fallen spruce, 25.06.2013, M.A. Fadeeva, PTZ. 241. Psilolechia lucida (Ach.) M. Choisy – Klimenitsky Monastery, 12.06.1863, Th. Simming, H; Podyelniki, on stones, 08.07.2012, M.A. Fadeeva, PTZ. 242. Pyrenopsis pleiobola Nyl. – Norrlin 1876. 243. Ramalina baltica Lettau – Velikaya Guba, 1870, J.P. Norrlin, H: Norrlin 1876; Paleostrov Island, on old Tilia cordata, 03.07.2004, M.A. Fadeeva, PTZ; Lipovitsy, on old aspen, 25.06.2013, M.A. Fadeeva, PTZ. 244. Ramalina dilacerata (Hoffm.) Hoffm. – Fadeeva 2013; North to Zubovo village, on Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Oyatevshina village, on Salix caprea, 05.07.2012, M.A. Fadeeva, PTZ: Fadeeva & Kravchenko 2013; Lipovitsy, along the brook, on drying Sorbus aucuparia, 25.06.2013, M.A. Fadeeva, PTZ. 245. Ramalina farinacea (L.) Ach. – Fadeeva 2013; surroundings of Zubovo village, on aspen, 03.07.2012, M.A. Fadeeva, PTZ; Podyelniki, on stone in the wall around old chapel, 10.07.2012, M.A. Fadeeva, PTZ. 246. Ramalina pollinaria (Westr.) Ach. – Fadeeva 2000; Podyelniki, on stone in the wall around old chapel, 10.07.2012, M.A. Fadeeva, PTZ; NW shore of Lake Vekhkozero, on stone wall, 11. 07.2012, M.A. Fadeeva, PTZ. 247. Ramalina sinensis Jatta – Fadeeva 2013; Bol. Klim. Isl., on trunk of Sorbus aucuparia, 19.07.2000, M.A. Fadeeva, PTZ. 248. Ramalina thrausta (Ach.) Nyl. – Norrlin 1876. 249. Ramboldia elabens (Fr.) Kantvilas & Elix – Vainio 1934. 250. Rhizocarpon geographicum (L.) DC. s.l. – Fadeeva 2013; Bolshoi Lelikovsky Island, Radkolye Cape, on shore rocks, 06.07.2004, M.A. Fadeeva, PTZ; 251. Rhizocarpon polycarpum (Hepp) Th. Fr. – Norrlin 1876. 252. Rimularia insularis (Nyl.) Rambold & Hertel (obligate lichenicolous lichen) – Nylander 1866 a; Norrlin 1876; Vainio 1934; Hertel 1970; Fadeeva 2001 a; Zhurbenko & Ahti 2005. 220 Reports of the Finnish Environment Institute 40 | 2014 253. Rinodina archaea (Ach.) Arnold – Norrlin 1876. 254. Rinodina confragosa (Ach.) Körb. – Shunga, on diorites in pock’s crashes, in shadow, 1876, J.P. Norrlin, H: Norrlin 1876. 255. Rinodina pyrina (Ach.) Arnold – Fadeeva 2000. 256. Sclerophora pallida (Pers.) Y. J. Jao & Spooner – Lipovitsy village SW, W of Lake Bezdonnoe, brook-side herb-rich deciduous forest, on old Ulmus, 24.8.2013, K. Syrjänen, TUR. 257. Sclerophora coniophaea (Norman) J. Mattsson & Middelb. – Velikaya Guba – SW, Zubovo –N, NE of Lake Pužej, spruce swamp – mixed herb-rich forest at E-base of siliceous cliff, on birch snag, abundant, 24.8.2013, K. Syrjänen, TUR; Tambitsy NW towards Kaskoselga, herb-rich – grassy swamp forest, on birch snag, 28.08.2013, K. Syrjänen, TUR. 258. Scoliciosporum chlorococcum (Graewe ex Stenh.) Vězda – Eastern shore Kizhi Island, Yamka village, about 0,5 km to the North, on pine, abundant, 28.05.1999, M.A. Fadeeva, PTZ. 259. Scytinium fragrans (Sm.) Otálora et al. – Fadeeva 2013. 260. Scytinium gelatinosum (With.) Otálora et al. – Norrlin 1876; Yuzhny Oleny Island, on dolomites, M.A. Fadeeva, 05.07.2004, PTZ. 261. Scytinium lichenoides (L.) Otálora et al. – Fadeeva 2013. 262. Scytinium plicatile (Ach.) Otálora et al. – Fadeeva 2013. 263. Scytinium teretiusculum (Wallr.) Otálora et al. – Fadeeva 2013; Lipovitsy, along the brook, on bark of aspen, 25.06.2013, M.A. Fadeeva, PTZ. 264. Spilonema paradoxum Bornet – Norrlin 1876. 265. Spilonema revertens Nyl. – Norrlin 1876. 266. Staurothele frustulenta Vain. – Vainio 1921. 267. +Stenocybe pullatula (Ach.) Stein – Fadeeva 2013. 268. Stereocaulon evolutum Graewe – Norrlin 1876. 269. Stereocaulon grande (H. Magn.) H. Magn. – Fadeeva 2013. 270. Stereocaulon saxatile H. Magn. – Fadeeva 2013; Ersenevo village, stony shore of Lake Onega, M.A. Fadeeva, 05.07.2012, PTZ. 271. Stereocaulon subcoralloides (Nyl.) Nyl. – Fadeeva 2013; on stone basement of old main church of Kizhi, 31.05.1999, M.A. Fadeeva, PTZ. 272. Stereocaulon tomentosum Fr. – Fadeeva 2013. 273. Strangospora moriformis (Ach.) Stein – Tolpysheva et al. 2001. 274. Strigula stigmatella (Ach.) R. C. Harris – Nylander 1866 a, Norrlin 1876; Vainio 1921. 275. Tephromela atra (Huds.) Hafellner M.A. – Podyelniki, on stones, 10.07.2012, M.A. Fadeeva, PTZ. 276. Tetramelas insignis (Nägeli ex Hepp) Kalb. – Norrlin 1876. 277. Thamnolia vermicularis (Sw.) Schaer. – Velikaya Guba -SW, Zubovo -N, NE of Lake Pužej. East facing siliceus cliff-wall and boulder scree above an open mire, on many boulders – Locally rather common, 24.08.2013, K. Syrjänen, TUR. 278. Thermutis velutina (Ach.) Flot. – Norrlin 1876. 279. Toninia squalida (Ach.) A. Massal. – Azhepnavolok Cape, on mosses, 1870, J. . Norrlin, H: Norrlin 1876; Vainio 1922. 280. Trapelia glebulosa (Sm.) J. R. Laundon – Velikaya Guba, on schist, 1870, J. . Norrlin, H: Norrlin 1876, s.n. Lecidea coarctata Ach.; Vainio 1934. 281. Trapeliopsis granulosa (Hoffm.) Lumbsch – Norrlin 1876; Podyelniki, on roots of fallen spruce, 06.07.2012, M.A. Fadeeva, PTZ. 282. Tuckermanopsis chlorophylla (Willd.) Hale – Fadeeva 2000; Tolpysheva et al. 2001; Podyelniki, on stones, 10.07. 2012, M.A. Fadeeva, PTZ. Reports of the Finnish Environment Institute 40 | 2014 221 283. Umbilicaria deusta (L.) Baumg. – Fadeeva 2000; 2013; Ersenevo village, stony shore of Lake Onega, 05.07.2012, M.A. Fadeeva, PTZ. 284. Umbilicaria hirsuta (Sw. ex Westr.) Hoffm. – Fadeeva 2013. 285. Umbilicaria hyperborea (Ach.) Hoffm. – Fadeeva 2013; Podyelniki, shore Lake Onega, on stones, 10.07.2012, M.A. Fadeeva, PTZ. 286. Umbilicaria torrefacta (Lightf.) Schrad. – Fadeeva 2013. 287. Umbilicaria vellea (L.) Hoffm. – Fadeeva 2013. 288. Usnea barbata (L.) Weber ex F.H.Wigg. – Lipovitsy, along the brook, on spruce, 25.06.2013, M.A. Fadeeva, PTZ. 289. Usnea dasypoga (Ach.) Röhl. – Tolpysheva et al. 2001; south-western shore of Lake Vekhkozero, on spruce, 11.07.2012, M.A. Fadeeva, PTZ. 290. Usnea glabrescens (Nyl. ex Vain.) Vain. – Tolpysheva et al. 2001. 291. Usnea hirta (L.) F. H. Wigg. – Tolpysheva et al. 2001; Fadeeva 2000, Podyelniki, on bark of pine, 10.07.2012, M.A. Fadeeva, PTZ. 292. Usnea lapponica Vain. – Tolpysheva et al. 2001. 293. Usnea subloridana Stirt. – Fadeeva 2013; Podyelniki, on bark of pine, 10.07.2012, M.A. Fadeeva, PTZ. 294. Vahliella leucophaea (Vahl) P. M. Jørg. – Fadeeva 2013; Ashepnavolok Cape, 1870, J.P. Norrlin, H; Bolshoi Lelikovsky Island, on rock outcrops, 06.07.2004, M.A. Fadeeva, PTZ; Rybya Bay of Lake Onega, eastern slope, on rock outcrops, 11.07.2012, M.A. Fadeeva, PTZ. 295. Vulpicida pinastri (Scop.) J.-E. Mattsson & M. J. Lai – Norrlin 1876; Tolpysheva et al. 2001; Fadeeva 2000, 2013; North to Zubovo village, on Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ. 296. Xanthoparmelia conspersa (Ehrh. exAch.) Hale – Krestovy Isl., abandoned ield, on boulders, 29.05.1999, M.A. Fadeeva, PTZ; Ersenevo village, abandoned ield, on stones, 05.07.2012, M.A. Fadeeva, PTZ; Podyelniki, abandoned ield, on stones and mossy rocks, 10.07.2012, M.A. Fadeeva, PTZ. 297. Xanthoparmelia pulla (Ach.) O.Blanco et al. – Norrlin 1876; Fadeeva 2013. 298. Xanthoparmelia stenophylla (Ach.) Ahti & D. Hawksw. – Fadeeva 2013; Ersenevo village, abandoned ield, on stones, 05.07.2012, M.A. Fadeeva, PTZ; Podyelniki, abandoned ield, on stones and mossy rocks, 10.07.2012, M.A. Fadeeva, PTZ. 299. Xanthoparmelia verruculifera (Nyl.) O.Blanco et al. – Fadeeva 2013. 300. Xylopsora friesii (Ach.) Bendiksby & Timdal – Nylander 1866 a; Norrlin 1876; Fadeeva 2013; NW shore of LakeVekhkozero, on bark of pine, 11.07.2012, M.A. Fadeeva, PTZ. 301. Xanthoria parietina (L.) Th. Fr. – Norrlin 1876; Fadeeva 2000; North to Zubovo village, on Salix caprea, 03.07.2012, M.A. Fadeeva, PTZ. 302. Xanthoria sorediata (Vain.) Poelt – Fadeeva 2013. 303. Xylographa parallela (Ach.) Fr. – Tolpysheva et al. 2001. 304. Xylographa vitiligo (Ach.) J. R. Laundon – Norrlin 1876; Fadeeva 2013; Podyelniki, on wood of pine, 10.07.2012, M.A. Fadeeva, PTZ. 222 Reports of the Finnish Environment Institute 40 | 2014 3.4 Red-listed and indicator lichens of Zaonezhye Peninsula Kimmo Syrjänen*, Olli Manninen** and Margarita A. Fadeeva*** * The Finnish Environment Institute (SYKE), P.O.Box 140, 00251 Helsinki, Finland. Corresponding author Kimmo Syrjänen E-mail: kimmo.syrjanen@ymparisto.i ** Olli Manninen, Luonto-Liitto, Annankatu 26 A, 00100 Helsinki, Finland ***Forest Research Institute of Karelian Research Center of Russian Academy of Sciences, 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia Introduction Some of the lichen collections from Zaonezhye Peninsula date back more than a hundred years, when lichenologists and other botanists of the Imperial Alexander University of Finland made ield excursions to Karelia. Also Zaonezhye Peninsula (Äänisniemi) was visited at that time. The irst lichen lora of Karelia Onegensis (Kon) was published by Johan Petter Norrlin already in 1876 (Norrlin 1876, see also Ahti & Boychuk 2006). At the time, for example, Ramalina obtusata was collected from Zaonezhye near Velikaya Guba and another threatened species of the genus Ramalina, R. thrausta, from Dianova Gora. However, most of the collections and observations of lichens from this area were made in the early 2000’s (2000–2013), mainly by researchers from the Karelian Research Center of the Russian Academy of Sciences (Fadeeva 2013, Fadeeva & Kravchenko 2013). Altogether 1276 species of lichens are found in Karelia (Fadeeva et al. 2007) and about half of them (52 %) are present in Karelia onegensis. Margarita A. Fadeeva has listed 129 lichen species from Zaonezhye Peninsula in 2013. Her article (Fadeeva 2013) includes mainly sites in northern and central parts of the peninsula. Studies by Tolpysheva et al. (2001) and Fadeeva & Kravchenko (2013) have main focus on lichen lora of Kizhi archipelago. All these works include observations of many red-listed and indicator lichen species of pristine forests and other habitat hotspots. In the summers 2012 and 2013, Fadeeva continued inventories of lichens in many parts of Zaonezhye (for example, around the villages of Lipovitsy, Podyelniki, Zubovo and Polya). List of collections is presented in chapter 3.3. Kimmo Syrjänen and Olli Manninen observed lichens in many parts of southern and southwestern Zaonezhye Peninsula during two weeks in late August 2013. As a result of the inventories of the most recent years the number of known lichen species has more than doubled in Za- Reports of the Finnish Environment Institute 40 | 2014 223 onezhye, being now over 304. Lichens specimens collected by Syrjänen and Manninen in 2013 are mainly deposited in the Turku University herbarium (TUR) and materials collected by Fadeeva are available in the Karelian Research Centre herbarium (PTZ) in Petrozavodsk. In chapter 3.3 there is a list of lichen specimens which have been collected from Zaonezhye to different scientiic herbaria in Russia and Finland. All Finnish collections of the year 2013 have not yet been entirely included in the list. Material and methods During the inventory in 2013 by the Finnish group most attention was paid to localities that were selected in earlier inventories (by the non-governmental nature conservation organization SPOK or Karelian Research Centre) or that looked promising in remote sensing images (TM/SPOT satellite imagery). We tried to visit as many forest compartments (kvartal) with pristine-like forests as possible within the study area. However, some of the forest compartments (kvartal), or parts of them, had been recently clear-cut. Nevertheless, we spent most of the time in old-growth forests, swamp forests and brook-side forests. Data were collected especially on indicator lichens, based on Andersson et al. (2009), and red-listed species of Karelia, based on Ivanter & Kuznetsov (2007). Special attention was paid to Calicioid lichens, many of which are used as indicator species of forest habitat quality (Tibell 1999, Andersson et al 2009). Many of the lichen indicator species suggest a continuity of forest habitats, a stable microclimate and an intact hydrology as well as the presence of very old living and dead trees. Although the inventories concentrated on forest habitats, the authors visited also several bogs and mires as well as some rock outcrops with both basic and siliceous bedrock. During the ield trip, we collected data on other species groups as well (vascular plants, fungi, bryophytes). Therefore, the results on lichens are far from complete, although they give a general insight into the importance of Zaonezhye for indicator and red-listed species. Because observation of crustaceous lichens is time consuming, more attention was paid to particularly easily observable species, especially Lobaria pulmonaria. Also other members of the inventory group, especially Jyri Mikkola, Olli-Pekka Tikkanen and Timo Kuuluvainen, informed us about the occurrence of Lobaria pulmonaria and other easily identiiable lichen species. Results The list of observed red-listed and indicator species and frequency of observations are shown in Table 1. Chapter 3.3. contains a more detailed list of lichens specimens collected on Zaonezhye. So far it includes 304 lichen species. Epiphytes of deciduous trees Large aspen trees (Populus tremula) are present throughout the Zaonezhye landscape, both in remote herb-rich old-growth forests and in late-successional deciduous stands close to abandoned old villages. These aspen trees host a rich epiphyte lora. The large, leafy lichen Lobaria pulmonaria is very common in Zaonezhye. Individuals of Lobaria pulmonaria were often healthy, and we observed apothecia in many places. Also, we found the parasite fungus of Lobaria pulmonaria, Plectocarpon lichenum a couple of times in Zaonezhye. In 2013 we recorded Lobaria pulmonaria from 493 sites throughout the southern half of Zaonezhye Peninsula. Another typical epiphyte of aspens in the area is the indicator lichen Leptogium saturninum. Aspen trees also host other foliose lichens that 224 Reports of the Finnish Environment Institute 40 | 2014 live in symbiosis with cyanobacteria. These include species from the genera Nephroma spp. and Peltigera spp. For example, Peltigera praetextata and P. canina are occasionally found at the base of large aspens throughout Zaonezhye. Neproma parile and Nephroma bellum are relatively common epiphyte species, whereas Nephroma resupinatum is more rare. The latter indicator species was found only in a half a dozen locations during the 2013 survey. These folious indicator species are also growing on certain other deciduous trees, mainly on Rowan (Sorbus aucuparia), Goat willow (Salix caprea) and Bay willow (Salix pentandra) and sometimes also on old birches. Old individuals of these tree species are common at the mire margins as well as in swamp forests and herb-rich forests. Other indicator epiphytes of deciduous trees in Zaonezhye include Parmeliella triptophylla, Pannaria pezizoides and Leptogium teretiusculum, which were occasionally found from old herb-rich mixed forests. The presence of these lichens on aspen and other deciduous trees indicates that there is continuity of old deciduous trees and a suitable microclimate and the landscape is connected so that most epiphyte lichen species can disperse and colonize new trees. Peltigera collina was the most rare epiphyte in its genus of folious lichens and was found only twice. Also epiphyte species of the genus Collema seem to be rare in Zaonezhye: Collema subnigrescens/nigrescens was found a few times, Collema fragrans only once. Bay willow (Salix pentandra) is a relatively common tree species in Zaonezhye. It grows regularly at the margins of mires and swamp forests as well as by the side of brooks and rivulets. Trunks of big trees seem to be good substrata for lichen epiphytes. In addition to Loparia pulmonaria and Nephoma spp. they are often colonized by several other species, including Ramalina spp. and Calicioid lichens such as Chaenotheca chlorella and Calicium lichenoides. The commonness of Bay willow is probably due to the fact that most mires have not been drained by ditching. Also beaver activity increases looding dynamics in mire ecosystems and riparian environments. This contributes to the establishment and growth of Salix pentandra. Fig. 1. Salix pentandra swamp forest (Photo: Kimmo Syrjänen). Reports of the Finnish Environment Institute 40 | 2014 225 Also some broadleaf hardwood trees such as Tilia cordata grow in the herb-rich forests of Zaonezhye. Tilia cordata is found occasionally on rich soils. Ulmus laevis grows in many sites at Zaonezhye, especially in Kizhi archipelago. One place worth mentioning is an Ulmus glabra stand southwest of the village of Lipovitsy (whose Russian name refers to a lime tree). In the upper course of a small brook that runs out of Lake Bedzdonnaye, a herb-rich deciduous forest grows about a dozen big elm trees with an interesting lichen epiphyte lora. Bacidia rubella, Gyalecta ulmi and Sclerophora pallida (syn. S. nivea) grow on the elm trunks. The presence of elm trees and these temperate lichen species are a consequence of the favourable climatic conditions and rich soils of Zaonezhye Peninsula. Small swamps forests with Alnus glutinosa occur in many brook valleys and swampy depressions. In one location, we found the crustaceous Arthonia spadicea growing on black alder trunks. It is a red-listed indicator species of black alder swamp-forests. We also found Coenogium pineti growing on trunks of black alder trees in swamp forests. It is a typical species of this habitat. In addition, Arthonia leucopellea has been found as epiphyte of Alnus glutinosa in Zaonezhye. However, most occurrences of this red-listed indicator species in Zaonezhye are on spruce trunks. It typically grows on the bark of old, living spruces in swamp forests and at mire margins. Large old birches (both Betula pendula and B. pubescens) grow in several forest habitats in Zaonezhye, including herb-rich and pristine forests as well as swamp forests and late-successional stands of deciduous forests. Even though Lobaria pulmonaria can occasionally be found also on the trunks of birches, these are not that important for folious species in Zaonezhye. However, birch trees host a wide range of crustaceous lichen species. Especially Chaenotheca brachypoda is a common indicator species on old, partly rotten birches. In swamp forests and old-growth forests, Sclerophora coniophaea is often found by the sides of brooks, on the trunks of very old living birches or dead birch snags. Usnea lichens and other fruticose epiphytes Many hanging fruticose lichens are considered to be indicators of good air quality, moist microclimate and forest continuity. Especially Usnea spp., Bryoria spp., Alectoria sarmentosa, Ramalina thrausta and Evernia divaricata are such species. In Zaonezhye Peninsula, Usnea lichens are most frequently found along bog and mire margins as well as in swamp forests and pristine old-growth forests. These species hang from twigs and trunks of both coniferous and deciduous trees. In the genus Usnea, common species Usnea dasypoga and Usnea subloridana seem to prevail, although this genus was not studied in detail during the ield trip. However, both more rare and threatened species Usnea barbata, U. chaetophora, U. glabrescens and U. lapponica have been collected from few places in Zaonetshye. In the genus Bryoria, widely distributed species like Bryoria capillaris and B. fuscescens (sensu lato) are common and can sometimes completely cover small spruces at the margins of mires. Also Bryoria furcellata, which demands a more natural environment, is generally found at these sites. The large, hanging Bryoria fremontii is not abundant on Zaonezhye Peninsula, although it has been found at a couple of sites. Bryoria nadvornikiana seems to be rare, with only a few individuals found at seven sites. Surprisingly, also Alectoria sarmentosa seems to be a relatively rare or occasional species. Especially larger healthy populations are scarce in Zaonezhye. However, Evernia divaricata was found at 58 sites, typically in transition zones between mires and forests. It can grow on the trunks and twigs of almost all tree species of the region. The size and health of individual lichens varies a lot, but most of the individuals are small and the populations scarce. There are also populations with a large amount of individuals where the length of healthy individuals of hanging 226 Reports of the Finnish Environment Institute 40 | 2014 lichens can reach approximately 20–30 cm. In our inventories there were no sightings of Ramalina thrausta, which has not been found from Zaonezhye for over 100 years. Fig. 2. Healthy hanging Evernia divaricata with Usnea sp. and Bryoria spp. (Photo: Kimmo Syrjänen). Epiphytes of spruce In addition to fruticous species on the branches and trunks of spruces, many crustaceous lichens grow on the bark of old living trees or on the bare wood of dead standing spruces. These include several indicator species of pristine forests, moist microclimate and very old trees. We found Lecanactis abietina in a few places. It is a crustaceous lichen, typically growing on the bark of old spruces. We also found Arthonia leucopellea, which prefers spruces in swamp forests, from a couple of places in the Reports of the Finnish Environment Institute 40 | 2014 227 area. This species was also recorded from Alnus glutinosa. In addition, we observed Chaenotheca subroscida, which is a Calicioid lichen, typically growing on spruce bark in moist pristine forests. We also found Lobadium disciforme from both spruce bark and deciduous trees in Zaonezhye. Lichens on dead wood Tall stumps and snags of spruces and deciduous trees are extremely important for many crustaceous lichens in old-growth pristine forests. Some species, like Chaenotheca chlorella, prefer growing on deciduous trees but are also found from dead wood of spruce and deciduous trees. Others, like Chaenotheca laevigata and Chaenotheca gracillima, grow mainly on bare wood and dead trees but can also grow on the bark of living trees. In Zaonezhye, Sclerophora coniophaea seems to often grow on snags of old birches, but it occasionally grows also on other substrate, including dead wood and bark. It was found at 25 sites in old-growth swamp forests, old herb-rich forests and forests along brooks. However, Chaenotheca gracilenta (syn. Cybebe gracilenta) grows almost exclusively on decaying stumps in the moist conditions of swamp forests and moist old-growth forests. It was observed at more than ten sites in Zaonezhye. Only a few indicator lichens species are typical for downed logs. Cladonia norvegica is common on soft, wind fallen spruce logs in forests with pristine characteristics throughout the peninsula. In places, Icmadophila ericetorum grows on the sides of large, relatively soft spruce and pine logs. Multiclavula mucida is an easy species to identify. It has a permanent green thallus that normally covers several decimeters of large, fallen and decaying aspen trunks. Unlike many other lichens, it belongs to basidiomycota and its fruiting bodies are short-lived, whitish clubs arising from the thallus. Multiclavula mucida grows in various places in Zaonezhye, mainly in herb-rich mixed forests with large aspen trees. Fig. 3. Multiclavula mucida (Photo: Kimmo Syrjänen). 228 Reports of the Finnish Environment Institute 40 | 2014 Cladonia parasitica prefers more sun-exposed conditions than the above species. It is mainly found from downed pine logs and stumps in dry heath pine forests or rocky forests. The ecology of Lecidea botryosa is similar, although it grows also on dry wood of spruce. In suitable habitats, both of these species seem to be relatively common in Zaonezhye. Pyrrhospora elabens is a more rare lichen indicator in Zaonezhye. It prefers snags of large old pines in sun-exposed environments. The species has been found from old, dry pine forests in western parts of Zaonezhye. In Zaonezhye, dead, standing pine trees and snags are common at bogs and mire margins. Shiny black spikes of Calicium denigratum are typically found on dry pinewood in these habitats. In Zaonezhye it is quite often accompanied by Chaenothecopsis fennica, which has a similar ecology to Calicium denigratum but grows also on spruce wood in the same habitats. Both of these indicator species are relatively frequent at bog and mire margins in the area. Bogs are also home for Evernia mesomorpha, аСТМС ЦКТЧХв РrШаs ШЧ ЭаТРs КЧН ЭrЮЧФs ШП sЭЮЧЭОН ЩТЧОs, ЛТrМСОs КЧН sЩrЮМОs ТЧ ШЩОЧ ЛШРs, ЛЮЭ sШЦОЭТЦОs КХsШ ШЧ ЭСО ЛrКЧМСОs ШП НОКН ЭrООs. TСО sЩОМТОs РrШаs ТЧ sОЯОrКХ ЛШРs ТЧ ГКШЧОгСвО, КХЭСШЮРС ТЭ Тs ЧШЭ КЛЮЧНКЧЭ. Basic and siliceous cliffs Carboniferous rocks of Mount Sypun are important for lichens as well as for bryophytes. The site seems to have a very rich lichen lora of basic rocks, including e.g. Collema fuscovirens, Collema polycarpon, Fuscopannaria leucophaea (syn. Vahliella leucophaea), Leptogium plicatile, Neofuscelia verruculifera (syn. Xanthoparmelia verruculifera), Peltigera lepidophora, P. leucophlebia, P. venosa and Xanthoria sorediata. Also Lobaria scrobiculata grows there (Fadeeva 2013). The conservation value of this rocky area is very high. Especially one site on a siliceous rock outcrop in Zaonezhye is worth mentioning. The site is situated east of the village of Lipovitsy, not far from the shores of Lake Onega. It is an east-facing, bare siliceous cliff wall with coarse talus scree beneath it. There is an open oligotrophic mire in front of the cliff. The cliff wall has a typical lichen lora of siliceous oligotrophic rocks, including Chrysothrix chlorina, Ramalina pollinaria, Parmelia fraudans, Alectoria sarmentosa and Hypogymnia vittata. However, there is a more interesting lichen lora on boulder scree, including Cladonia amaurocraea and a large population of Thamnolia vermicularis, which grows on the sides and tops of the boulders. The distribution of this lichen species is mainly Arctic-alpine, although it can be found in some remote locations on lowlands, especially in coastal areas. Nephroma arctica grows towards the southern end of the cliff. Fig. 4. Thamnolia vermicularis (Photo: Kimmo Syrjänen). Reports of the Finnish Environment Institute 40 | 2014 229 Discussion Our inventories revealed several hotspots of pristine-like old-growth forests in larger or smaller patches as well as other types of environments that are important for lichens, including basic and siliceous rock outcrops. These short inventories revealed 1141 locations of red-listed and indicator lichens in Zaonezhye. It is evident that the species composition and the potential for conservation of biodiversity in Zaonezhye are much higher than have previously been thought. The diverse species composition of lichens is probably due to various reasons. There are still quite large old-growth forests, with a continuity of dead wood, remote from old villages. The bogs and mires of Zaonezhye are mostly intact, and drained bogs and mires are an exception. There are often wide transition zones between the margins of peat-forming ecosystems and the forests on mineral soil, which have not been used in active forestry. Swamps forests are common in Zaonezhye. These areas have a large number of tree species, old and dead trees as well as a suitable, moist microclimate. Some of the old traditional landscapes and grazed forests close to the villages, which were more open in the past, now have old deciduous trees. For many epiphyte lichens and species of dead wood, the landscapes form a connected network of suitable habitats. Zaonezhye provides an opportunity to maintain this valuable lora by making forest conservation areas and developing green corridors to connect them. Also peatlands and waterways could be used when building connections between larger conservation areas. REFERENCES AЧНОrssШЧ, L., AХОбООЯК, N.M. & KЮгЧОЭsШЯК, E. S. (ОНs.) 2009. ., . ., . . ДSЮrЯОв ШП ЛТШХШРТМКХХв ЯКХЮКЛХО ПШrОsЭs ТЧ NШrЭС-АОsЭОrЧ EЮrШЩОКЧ RЮssТК. VШХ 2. – IНОЧЭТiМКЭТШЧ ЦКЧЮКХ ШП sЩОМТОs ЭШ ЛО ЮsОН НЮrТЧР sЮrЯОв КЭ sЭКЧН ХОЯОХЖ. SЭ-PОЭОrsЛЮrР. 258 Щ. AСЭТ, T. & BШвМСЮФ, M. 2006. TСО ЛШЭКЧТМКХ УШЮrЧОвs ШП A.K. CКУКЧНОr КЧН J.I. LТЧНrШЭС ЭШ KКrОХТК КЧН OЧОРК RТЯОr ТЧ 1898 КЧН 1899, аТЭС К ХТsЭ ШП ЭСОТr ЛrвШЩСвЭО КЧН ХТМСОЧ МШХХОМЭТШЧs. – NШrrХТЧТК 14:1–65. FКНООЯК, . ., GШХЮЛФШЯК, N. S., VТЭТФКТЧОЧ, . & AСЭТ, . 2007. . ., . ., ., . ДCШЧsЩОМЭЮs ШП ЭСО ХТМСОЧs КЧН ХТМСОЧШЩСвХШЮs ПЮЧРТ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ.194 Щ. (IЧ RЮssТКЧ). FКНООЯК, . . 2013. . . ДLТМСОЧsЖ. −IЧ: GrШЦЭsОЯ, A.N. (ОН.), SОХФК ХКЧНsМКЩОs ШП ЭСО Zaonezhkii Peninsula: Natural characteristics. Land Use. Conservation. (eds.), Karelian Research Center of RЮssТКЧAМКНОЦв ШП SМТОЧМОs.PОЭrШгКЯШНsФ. Щ. 114–121. (IЧ RЮssТКЧ). FКНООЯК, . . & KrКЯМСОЧФШ, A. V. 2013. . ., . . ДSЭЮНв ШП ЭСО ХТМСОЧ lШrК ШП ЭСО МШЧЭТЧОЧЭКХ KТгСТ ArМСТЩОХКРШЖ. − IЧ: MКrЭвКЧШЯ, R. & IОsСФШ, . (ОНs.), BЮХХОЭТЧ ШП ОЧЯТrШЧЦОЧЭКХ sЭЮНТОs ТЧ KТгСТ MЮsОЮЦ-RОsОrЯО PОЭrШгКЯШНsФ: KТгСТ MЮsОЮЦ-RОsОrЯО PЮЛХТsСТЧР CОЧЭrО. Щ. 14−16. (IЧ RЮssТКЧ). IЯКЧЭОr, E. V. & KЮгЧОЭsШЯ, O. L. (ОНs.) 2007. . ., . . ( .) ДRОН НКЭК ЛШШФ ШП ЭСО RОЩЮЛХТМ ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ, 368 Щ. NШrrХТЧ, J.P. 1876: FХШrК KКrОХТКО ШЧОРОЧsТs. II LТМСОЧОs. – MОННОХКЧНОЧ SШМТОЭКЭТs FКЮЧК FХШrК FОЧЧТМК 1:1–46. RКssТ, P., HвЯтrТЧОЧ, E., JЮsХцЧ, A. & MКЧЧОrФШsФТ, I. (ОНs.) 2010. TСО 2010 RОН LТsЭ ШП FТЧЧТsС SЩОМТОs. –ВЦЩтrТsЭöЦТЧТsЭОrТö & SЮШЦОЧ вЦЩтrТsЭöФОsФЮs. HОХsТЧФТ. 685 Щ. TТЛОХХ, L. 1999. CКХТМТШТН ХТМСОЧs КЧН ПЮЧРТ. – NШrНТМ LТМСОЧ FХШrК 1:20–70. UННОЯКХХК. TШХЩвsСОЯК, . ВЮ., LвЮЛТЦШЯК, . G., GШrsСТЧК, . S. & SТгШЯК, . P. 2001. . ., . ., . ., . . . 3. ДLТМСОЧ lШrК ШП КЧМТОЧЭ аШШНОЧ КrМСТЭОМЭЮrКХ ЦШЧЮЦОЧЭs. 3. CСЮrМС ШП TrКЧsiРЮrКЭТШЧ ТЧ KТгСТЖ. – IЧ: VОsЭЧТФ MШsФШЯsФШРШ ЮЧТЯОrsТЭОЭК, SОr. 16. BТШХШРв 1: 24–33. (IЧ RЮssТКЧ). 230 Reports of the Finnish Environment Institute 40 | 2014 Table 1. Red listed and indicator lichens of Zaonezhye. Presence of species in Karelian (KAR) and Finnish (FIN) Red Data Books is shown in the irst column (Ivanter & Kutznetsov 2007, Rassi et al. 2010). Their role as indicator (IND) of valuable forest habitats is shown in the second column (based on Andersson et al. 2009) and number of observations in the third column. Also some other lichen species with indicator characteristics are included in table. Table is based on observations by the authors in 2012–2013 and literature information (Fadeeva 2013, Fadeeva & Kravchenko 2013, Tolpysheva et al. 2001). Table includes only recent observations of valuable species; historical records are available in chapter 3.3. Species name Red Listed Alectoria sarmentosa Anaptychia ciliaris Arthonia leucopellaea Arthonia spadicea Arthonia vinosa Bacidia rubella Bryoria fremontii Bryoria nadvornikiana Calicium denigratum Chaenotheca brachypoda Chaenotheca chlorella Chaenotheca gracilenta Chaenotheca gracillima Chaenotheca laevigata Chaenotheca stemonea Chaenotheca subroscida Chaenothecopsis fennica Cladonia decorticata Cladonia norvegica Cladonia parasitica Coenogium pineti Collema laccidum Collema fragrans Collema furfuracea Collema fuscovirens Collema polycarpon Collema subnigrescens Evernia divaricata Evernia mesomorpha Fuscopannaria leucophaea Graphis scripta Gyalecta truncigena Gyalecta ulmi Hypogymnia vittata Icmadophila ericetorum Lecanactis abietina Lecidea botryosa Leptogium lichenoides Leptogium plicatile Leptogium saturninum Leptogium teretiusculum Lobaria pulmonaria Lobaria scrobiculata Lopadium disciforme Melanelia subaurifera Microcalicium disseminatum Multiclavula mucida Neofuscelia verruculifera KAR, FIN KAR KAR, FIN FIN KAR, FIN FIN KAR, FIN KAR, FIN FIN FIN KAR, FIN KAR, FIN FIN KAR, FIN KAR, FIN FIN KAR FIN FIN Indicator species IND IND IND IND IND IND IND IND IND IND IND IND IND IND IND IND IND FIN FIN FIN FIN KAR, FIN IND IND FIN KAR, FIN KAR FIN FIN FIN KAR, FIN KAR, FIN FIN KAR IND IND IND IND IND IND IND IND IND IND IND IND IND FIN KAR, FIN Number of observations 11 2 6 1 1 1 4 6 17 64 8 14 4 3 1 4 8 1 12 53 2 1 1 1 1 1 2 58 13 1 11 1 2 2 11 3 18 2 1 89 7 518 3 8 1 6 7 1 Reports of the Finnish Environment Institute 40 | 2014 231 Nephroma arcticum Nephroma bellum Nephroma parile Nephroma resupinatum Pannaria pezizoides Parmeliella triptophylla Parmelina tiliacea Peltigera collina Peltigera scabrosa Peltigera venosa Plectocarpon lichenum Pyrrhospora elabens Psilolechia clavulifera Ramalina baltica Ramalina dilacerata Ramalina sinensis Sclerophora coniophaea Sclerophora pallida Thamnolia vermicularis Usnea barbata Usnea chaetophora Usnea glabrescens Usnea lapponica 232 Reports of the Finnish Environment Institute 40 | 2014 KAR, FIN FIN FIN KAR, FIN KAR, FIN KAR, FIN FIN FIN KAR KAR, FIN KAR, FIN FIN KAR, FIN FIN KAR KAR, FIN FIN FIN FIN IND IND IND IND IND IND IND IND IND IND IND IND IND 2 36 36 6 2 12 1 2 1 2 3 3 1 2 3 4 25 1 1 1 1 1 1 3.5 Aphyllophoroid fungi of Zaonezhye Peninsula Anna Ruokolainen* and Olli Manninen** * Forest Research Institute of the Karelian Research Center of Russian Academy of Sciences 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia E-mail: anna.ruokolainen@krc.karelia.ru ** Olli Manninen, Luonto-Liitto, Annankatu 26 A, 00100 Helsinki, Finland Introduction Zaonezhye Peninsula is dominated by green-moss spruce forests. Also nemoral species grow in these forests, and thus the forests have features of southern taiga forests. In the past most of the areas on Zaonezhye Peninsula formerly covered with pristine spruce-dominated forests were cleared for slash-and-burn cultivation to give way to pastures, ploughland and meadows as well as secondary mixed forests (Kuznetsov et al. 1999). Mycological studies in Zaonezhye Peninsula and adjacent areas Mycological studies in Zaonezhye were carried out between 1996 and 1998 by the Forest Research Institute of the Karelian Research Centre of the Russian Academy of Sciences, Petrozavodsk (FRI) and V.L. Komarov Botanical Institute of the Russian Academy of Sciences, St. Petersburg (BIN RAS) (Bondartseva et al. 2000). In 1996 and 1998, Margarita Bondartseva, Vera Kotkova (Lositskaya), Vitaly Krutov and Svetlana Kiviniemi conducted research on the Kizhi and Gogolev islands. In 1997, Anna Ruokolainen carried out studies on Bolshoi Klimenetsky Island Between 2010 and 2013, Anna Ruokolainen continued her studies, in cooperation with the Finnish specialists Olli-Pekka Turunen, Olli Manninen and Jyri Mikkola, on Bolshoi Lelikovsky Island and other parts of Zaonezhye Peninsula (in the vicinity of the villages of Vegoruksa, Velikaya Guba, Velikaya Niva, Kuzaranda, Lipovitsy, Polya, Tambitsy, Tipinitsy and Shun’ga as well as lakes Vanchozero and Kosmozero). In 2012, fungi were studied on Kizhi Island and near the villages of Zharnikovo, Malkovo, Zubovo and Podyelniki with the initiative and support of the Kizhi museum-reserve. Samples from Zaonezhye Peninsula and the Kizhi archipelago are stored in the herbaria of BIN RAS (LE) and FRI (PTZ). Reports of the Finnish Environment Institute 40 | 2014 233 Data from previous decades are very sparse. The herbarium of the University of Helsinki contains two samples from Kizhi Island collected by W. Nyberg in 1863 and three samples taken by Pertti Uotila in 1991 (Bondartseva et al. 1999). According to the geobotanical zonation of Karelia (Mela & Cajander 1906), Zaonezhye Peninsula forms a part of the province of Karelia onegensis (Kon). Administratively, it belongs to the Medvezhyegorsk municipality of the Republic of Karelia. As a result of the mycological studies, a total of 360 aphyllophoroid fungus species have been reported from the province of Kon (which is the greatest number of species reported in any of the provinces in the Republic of Karelia) and 264 aphyllophoroid fungus species from the Medvezhyegorsk District (Bondartseva et al. 1999, Bondartseva et al. 2000, Lositskaya et al. 2001; Ruokolainen 2013 a, b, c). So far a relatively small number of fungus species has been recorded from the Kizhi archipelago. On one hand, this is due to intensive economic activities and the resulting changes in vegetation. On the other hand, the islands have been poorly studied in the past. There are records of 43 species from Bolshoi Klimenetsky Isl. (Bondartseva et al. 2000), 37 species from the Kizhi and Gogolev islands (Ruokolainen 2013 b) and 24 species from Bolshoi Lelikovsky Island (Ruokolainen, unpublished). Fig. 1. Anna Ruokolainen collecting polypores on dead wood. Forest near Lipovitsy village 23.08.2013 (Photo Jevgeni Jakovlev). Results To date, 233 aphyllophoroid fungus species of 113 genera, 38 families and 14 orders have been recorded from Zaonezhye Peninsula and the Kizhi archipelago. The most 234 Reports of the Finnish Environment Institute 40 | 2014 numerous order Polyporales contains 109 species of 49 genera and 7 families. Less numerous orders include Hymenochaetales (41 species of 13 genera and 3 families) and Russulales (21, 14 and 8 species, respectively). The orders Polyporales and Hymenochaetales consist basically of 5 families: Polyporaceae (35 species), Hymenochaetaceae (24), Fomitopsidaceae (30), Meruliaceae (23) and Schizoporaceae (14 species), which in turn consist of 126 species that make up 54% of all the aphyllophoroid fungus species known from the peninsula. The most numerous genera are Phellinus (14 species), Hyphodontia (12 species), Postia (10 species), Antrodia (9 species), Skeletocutis (7 species), Phlebia, Tomentella (6 species each), Polyporus, Trametes (5 species each), Antrodiella, Phanerochaete, Stereum, Trichaptum (4 species each). Nomenclature follows Index Fungorum (2014). Ninety-four species were found on conifers; 70 species were discovered on spruce (Picea abies and P. obovata) and 49 species on pine (Pinus sylvestris). A hundred species were found on deciduous tree species; 61 species were discovered on aspen (Populus tremulae), 40 on birches (Betula pendula and B. pubescens), 28 on alders (Alnus incana A. glutinosa), 22 on willow (Salix caprea), 19 on mountain ash (Sorbus aucuparia) and 5 species on elms (Ulmus laevis, U. glabra). Growing on soil and litter, there were 25 species of the genera Albatrellus, Bankera, Boletopsis, Cantharellus, Clavariadelphus, Clavulina, Coltricia, Craterellus, Hydnellum, Phaeolus, Phellodon, Ramaria, Sarcodon and Thelephora. Sixty-three species found in Zaonezhye are indicators of old-growth forests. These species are conined to the distinctive conditions of forest communities least affected by human activities (Albatrellus conluens, Amylocorticium subincarnatum, Amylocystis lapponica, Anomoporia kamchatica, Antrodia albobrunnea, A. crassa, A. pulvinascens, Antrodiella citrinella, Asterodon ferruginosus, Bankera fuligineoalba, Boletopsis grisea, Chaetoderma luna, Clavariadelphus pistillaris, Climacocystis borealis, Crustoderma corneum, C. dryinum, Dichomitus squalens, Diplomitoporus crustulinus, Fomitopsis rosea, Ganoderma lucidum, Gloeoporus pannocinctus, G. taxicola, Gloiodon strigosus, Haploporus odorus, Hericium coralloides, Junghuhnia collabens, J. luteoalba, J. pseudozilingiana, Kavinia alboviridis, Leptoporus mollis, Onnia leporina, Perenniporia subacida, Phaeolus schweinitzii, Phellinus chrysoloma, Ph. ferrugineofuscus, Ph. lundellii, Ph. nigrolimitatus, Ph. pini, Ph. populicola, Ph. viticola, Phellodon niger, Phlebia centrifuga, Ph. serialis, Piloporia sajanensis, Polyporus badius, P. pseudobetulinus, Postia guttulata, P. lateritia, P. undosa, Pseudomerulius aureus, Pycnoporellus alboluteus, P. fulgens, species of the genus Ramaria, Rhodonia placenta, Rigidoporus crocatus, Serpula himantoides, Sidera lenis, Skeletocutis odora, Sk. stellae, Tomentella crinalis, Trametes suaveolens, Tyromyces issilis). The above species indicate that these ecosystems are valuable and should be protected (Kotiranta & Niemelä 1996; Andersson et al. 2009). Twenty-one species, listed in the Red Data Book of the Republic of Karelia (2007), including Antrodia crassa, A. pulvinascens, Antrodiella citrinella, Aurantiporus issilis, Clavariadelphus pistillaris, Craterellus cornucopioides, Dichomitus squalens, Elmerina caryae, Ganoderma lucidum, Gloiodon strigosus, Haploporus odorus, Hericium coralloides, Junghuhnia collabens, J. pseudozilingiana, Kavinia alboviridis, Leptoporus mollis, Piloporia sajanensis, Polyporus pseudobetulinus, Radulodon erikssonii, Rigidoporus crocatus, Sidera lenis and Tomentella crinalis were reported from the study area. In addition, 40 species, classiied as VU (10 species), NT (25 species) and EN (5 species), were listed in the 2010 Red list of Finnish species (Rassi et al 2010). The species Amylocorticium subincarnatum, Amylocystis lapponica, Boletopsis grisea, Ceriporia excelsa, Crustoderma corneum, C. dryinum, Diplomitoporus crustulinus, D. lavescens, Fomitopsis rosea, Odonticium romellii, Perenniporia subacida, Phlebia centrifuga, Polyporus badius, Postia guttulata, P. lateritia, Pycnoporellus alboluteus, Scytinostroma galactinum, Skeletocutis brevispora, Sk. odora, Sk. stellae, Trametes suaveolens, Trichaptum laricinum Reports of the Finnish Environment Institute 40 | 2014 235 and T. pargamenum have not yet been granted a protected status in Russia, although they are already protected in neighboring countries. Species conined to pine Pine trees provide a number of habitats for fungi that colonize both living and dead trunks, snags, fallen logs and twigs at different stages of decay. In 2013, Phellinus pini was the most abundant fungal species found on pine throughout the southern part of the peninsula (120 records). The second most abundant species (in terms of frequency) was Diplomitoporus lavescens, which was found on standing, dead pine trunks. On fallen dead pines, the most abundant fungal species were Antrodia albobrunnea, Chaetoderma luna, Crustoderma corneum, Postia lateritia, P. undosa (which can colonize spruce as well) and Pseudomerulius aureus. On soil litter, we found Albatrellus conluens, Bankera fuligineoalba, Phaeolus schweinitzii, Phellodon niger, and several species of the genus Ramaria. The species growing on soil and litter include both mycorrhizal and humus saprotrophic fungi. These species are most abundant in old-growth pine forests, whereas in secondary pine forest they are usually rare. Species conined to spruce There are several indicator species of natural forests growing on spruce. Many of them are also red-listed. In 2013, the most abundant of these species were: Fomitopsis rosea (350 sites), Phellinus chrysoloma (more than 90 sites), Pycnoporellus fulgens (more than 80 sites), Phlebia centrifuga (ca. 80 sites), Amylocystis lapponica (more than 70 sites), and Phellinus viticola (more than 50 sites). Less abundant species included Climacocystis borealis, Asterodon ferruginosus, Crustoderma corneum, Gloeoporus pannocinctus, Hericium coralloides, Leptoporus mollis, Onnia leporina, Phellinus nigrolimitatus, Rhodonia placenta, and Skeletocutis odora. Finally, some indicator species and threatened species were found only on a few sites (less than 10 sites), e.g. Anomoporia kamtschatica, Antrodia inirma, A. pulvinascens, Antrodiella citrinella, Clavariadelphus pistillaris, Diplomitoporus crustulinus, Gloeoporus taxicola, Gloiodon strigosus, Haploporus odorus, Junghuhnia collabens, J. luteoalba, Pycnoporellus albolutescens, Sidera lenis, Skeletocutis chrysella, Sk. papyracea, Sk. stellae and Trametes suaveolens. Species conined to aspen Aspen trunks are usually covered with epiphytic lichens, which can in turn be succeeded by various species of fungi. Some of these fungi are parasitoids that colonize other fungal species. For instance, large fruiting bodies of Phellinus tremulae are often colonized by Junghuhnia pseudozilingiana, which is considered an indicator species of old-growth forests and is therefore included in the Red Books of Karelia (2007) and Finland (Rassi et al. 2010). In 2013, this species was recorded from 10 sites in the southern part of Zaonezhye Peninsula. In addition, Tomentella crinalis and Polyporus badius have been found in some sites on fallen aspen logs at different stages of decay. The former is included in the Red Book of Karelia (2007), while the latter has become rare in Finland and Sweden. Phellinus populicola, which is considered rare in Sweden (Artdatabanken 2010), was recorded in 2013 from approximately 90 sites in the southern part of Zaonezhye Peninsula. 236 Reports of the Finnish Environment Institute 40 | 2014 The most noteworthy indings of threatened and rare species of saproxylic fungi Antrodia crassa (P. Karst.) Ryvarden found in the end of Syar peninsula, Comparment 187, old-growth pine-dominated forest (19.08.2013, Olli Manninen leg.). This is maybe the most exclusive species conined the best pine forests preserved in the area. This inding must also be one of the southernmost indings in Fennoscandia. Ceriporia excelsa S. Lundell ex Parmasto was found on a wind-fallen deciduous tree in a small-leaved thicket on Kizhi Island. This is the irst inding of this relatively rare, southern species in the Republic of Karelia. It is also encountered in the adjacent Leningrad and Arkhangelsk Regions as well as in the Komi Republic. Ceriporia excelsa is a common species in Europe and North America. It is classiied as NT in the 2010 Red list of Finnish species (Rassi et al. 2010) and in Sweden (Artdatabanken 2010). Fig. 2. Ceriporia excelsa (Photo Anna Ruokolainen). Ganoderma lucidum (M. A. Curtis : Fr.) P. Karst. was found on a drying birch trunk in a mixed forest in the vicinity of the village of Tipinitsy. In the Republic of Karelia, this is the irst inding of the species in the Medvezhyegorsk District as well as in the Kon province. There have been sparse reports of the species from the Kl province in the Sortavala District (on a larch stump in a plantation on Valaam Island) and the Kton province in the Pudozh District (on a wind-fallen alder tree in the Vodlozero National Park). Ganoderma lucidum is common in southern Russia, but less common in middle latitudes. It occurs widely in Europe (except for northern Scandinavia and Finland), Asia, North Africa and North America. In the Red Data Book of the Republic of Karelia (2007) the species was classiied as VU. It is also included in the Red Data Book of the Russian Federation (2008) as well as regional Red Data Books. Reports of the Finnish Environment Institute 40 | 2014 237 Fig. 3. Ganoderma lucidum (Photo Anna Ruokolainen). Kavinia alboviridis (Mordan) Gilb. et Budington. One inding on old dry pieces of dead spruce (under an old living spruce) northwest of the Vatnavolok village, Syar peninsula (Comparment 134). There are sparse records of the species in the Republic of Karelia and it is only known from the Muezersky District and the environs of the Kostomuksha nature reserve. Kavinia alboviridis is classiied as DD in the Red Data Book of the Republic of Karelia (2007). Junghuhnia pseudozilingiana (Parmasto) Ryvarden was found in several parts of Zaonezhye Peninsula. It grows in mixed forests with old aspen trees, colonized and inhabited by the fungus Phellinus tremulae. The species is classiied as DD in the Red Data Book of the Republic of Karelia (2007) and the Red Nature Data Book of the Leningrad Region (2000), and VU in the 2010 Red list of Finnish species (Rassi et al. 2010). Junghuhnia pseudozilingiana occurs widely in Europe. Fig. 4. Junghuhnia pseudozilingiana (Photo Anna Ruokolainen). 238 Reports of the Finnish Environment Institute 40 | 2014 Piloporia sajanensis (Parmasto) Niemelä found in the vicinity of Uzkaya Salma village, Comparment 26 of Kizhi forestry unit. Moist spruce-dominated forest, 28.06.2013 (Olli Manninen leg.). This must be one of the southernmost indings of this rare species that is dependent on Trichaptum laricinum. Pycnoporellus alboluteus (Ellis et Everh.) Kotl. et Pouzar. Two new records South from Velikaya Guba village, at the western part of peninsula, Comparment 9 of Kizhi forestry unit in old-growth spruce forests with very much dead wood in all stages (Olli Maninen and Timo Kuuluvainen legs). This is the irst inding of the species in the Republic of Karelia. The species is classiied as EN in the 2010 Red list of Finnish species (Rassi et al. 2010) and CR in Sweden (2010). Pycnoporellus alboluteus occurs widely in Europe, Caucasus, Asia and North America. Rigidoporus crocatus (Pat.) Ryvarden was found on wind-fallen trunks of birch, alder and spruce trees in birch, motley grass-spruce and mixed forests near the villages of Zharnikovo, Lipovitsy, Polya and Tambitsy as well as on Bolshoi Klimenetsky Isl.. There are also a few reports of the species from Kondopoga and Pudozh Districts in the Republic of Karelia. The species is classiied as VU in the Red Data Book of the Republic of Karelia (2007). It is also listed in the Red Nature Data Book of the Leningrad Region (2000) and classiied as EN in the 2010 Red list of Finnish species (Rassi et al. 2010). Although Rigidoporus crocatus is rare here, it is common in other parts of Europe and North America. Fig. 5. Rigidoporus crocatus (Photo Anna Ruokolainen). Tomentella crinalis (Fr.) M.J. Larsen was found on a wind-fallen trunk of an aspen tree in a mixed forest near the villages of Tambitsy and Tipinitsy. In the Republic of Karelia, it is also found in Muezersky and Kondopoga Districts. The species is classiied as NT in the Red Data Book of Karelia (2007). Tomentella crinalis also occurs in the Leningrad and Arkhangelsk Regions. The predominance of species growing on deciduous trees indicates that the ecosystems of Zaonezhye have been transformed. However, a large number of species have been found on spruce and pine, which are the main forest-forming species. Further mycological studies and monitoring should be conducted in rocky pine forests, coastal Reports of the Finnish Environment Institute 40 | 2014 239 spruce forests and spruce forest patches along streams, as well as in old aspen forests. The large amount of rare and indicator species testiies to the importance of preserving and restoring ecosystems and habitats of species that need protection. Table 1. List of study sites, 2010–2013. 240 Latitude Longitude Place of collection, compartment, forest type Date 61,5605 35,08295 Bolshoi Lelikovsky Isl., pine forest 09/08/2010 61,560704 35,08214 Bolshoi Lelikovsky Isl., pine forest with spruce 09/08/2010 62,03355 35,03153 Recently fallen spruce trees; Bilberry spruce forest with aspen, south of the village of Uzkaya Salma 13/08/2010 62,03322 35,03274 Thick aspen trees (50-70 cm in diameter) 13/08/2010 62,03282 35,03251 Moist spruce forest with horsetail 13/08/2010 62,0259 35,04143 62,08100 35, 07234 Fallen trees (window dynamics) 11/08/2010 62,08094 35,07096 Lake shore 11/08/2010 62,07580 35,07131 Creek 11/08/2010 62,07576 35, 07101 Rock 11/08/2010 62,20098 35,08238 Rock 17/08/2010 62,23095 35,05072 Mixed forest near a ridge 17/08/2010 62,23077 35,05072 Rocky pine forest 17/08/2010 62,22324 35,05524 Lake shore 17/08/2010 62,04187 35,06582 Compartment 63, unit 20, spruce forest near a logging area 18/08/2010 62,04181 35 ,07116 Compartment 63, unit 20, spruce forest near a logging area 18/08/2010 62,04181 35 ,07116 Pine forest with aspen and spruce 18/08/2010 62,15156 35,00375 Bilberry spruce forest 19/08/2010 62,12589 34,54187 Bilberry motley-grass pine forest 19/08/2010 62,13394 34,58162 Pine forest 19/08/2010 62,17287 35,15553 13/08/2010 05/08/2011 62,10552 35,26476 South of Tambitsy, spruce forest 04/08/2011 62,10547 35,21341 South of Tambitsy, spruce forest 04/08/2011 62, 10393 35,20512 Spruce forest with overmature birch forest nearby 04/08/2011 62,11019 35,19156 Birch forest with spruce undergrowth 04/08/2011 62,16483 35,19158 Mixed forest 05/08/2011 62,20142 35,11240 Overmature motley grass-bilberry-shamrock spruce forest 05/08/2011 62,20091 35,11 010 Overmature aspen forest with spruce and birch 05/08/2011 62,20576 35,12 281 Spruce forest near a logging area 05/08/2011 62,14408 35,33 061 Motley grass birch forest with aspen and spruce 06/08/2011 62,66532 35,34077 Overmature spruce forest with aspen and birch 06/08/2011 62,15192 35,34179 Selective cutting area in green moss spruce forest with aspen 06/08/2011 62,1772 35,34074 East shore, south of Kuzaranda, spruce forest with aspen 07/08/2011 62,17527 35.34392 Aspen forest 07/08/2011 62,17446 35,34180 Spruce forest 07/08/2011 62,1772 35.34074 Pine forest 08/08/2011 62,25191 35,08184 Rocky pine forest 08/08/2011 62,25193 35,07515 Spruce forest with fallen trees (window dynamics) 08/08/2011 62,30067 34,93836 Environs of Velikaya Niva 23/08/2012 Reports of the Finnish Environment Institute 40 | 2014 62,11621 35,030734 A ridge between lakes 23/08/2012 62,62897 34,55234 Lake Vanchezero 22/08/2012 62,238002 34,88029 south of the village of Lambasruchei, Lake Onega shore 24/08/2012 62,497863 34,76967 south of the village of Lambasruchei, Lake Onega shore, a ridge 24/08/2012 62,53639 34,82289 Lake Kosmozero 25/08/2012 62,131327 35,093334 Lipovitsy, spruce forest with aspen and fallen spruce 21/08/2013 62,151863 34,943757 by the lake in pine forest, compartment 13 22/08/2013 62,10509 35,02556 Lipovitsy, spruce forest with aspen and fallen spruce, compartment 41-42 23/08/2013 62,290624 35,309113 trap, Polya, compartment 84, mixed forest with aspen and fallen spruce 24/08/2013 62,29052 35,57008 north of Tambitsy, environs of Tolsty Navolok, mixed and spruce forest, compartment 71 26/08/2013 62,1849 35,31122 Lake Korbozero, Tipinitsy, mixed and spruce forest 27/08/2013 62,17725 35,3571 Tipinitsy, spruce forest 27/08/2013 62,24515 35,49294 Tambitsy, motley grass spruce forest 28/08/2013 62,2418 35,49248 Tambitsy, spruce forest with aspen 28/08/2013 REFERENCES AЧНОrssШЧ, L., AХОбОТОЯК, N. . & KЮгЧОЭsШЯК, . S. (ОНs.) 2009. ., . ., . . . 2. , ДRОЯОКХТЧР КЧН sЭЮНв ШП ЛТШХШРТМКХХв ЯКХЮКЛХО ПШrОsЭs ТЧ ЧШrЭСаОsЭОrЧ EЮrШЩОКЧ RЮssТК. VШХ. 2. MКЧЮКХ ПШr МХКssТiМКЭТШЧ ШП ЭСО sЩОМТОs ЮsОН ПШr ЮЧТЭ-ХОЯОХ ОбКЦТЧКЭТШЧЖ. – SЭ. PОЭОrsЛЮrР. 258 Щ. (IЧ RЮssТКЧ). ArЭНКЭКЛКЧФОЧ 2010. JКЧ-OХШП TОНОЛrКЧН. RöНХТsЭКНО КrЭОr Т SЯОrТРО. SЯКЦЩКr. – TСО 2010 RОН LТsЭ ШП SаОНТsС SЩОМТОs. ArЭНКЭКЛКЧФОЧ, SLU, UЩЩsКХК, 2010. Щ. 247–284. BШЧНКrЭsОЯК, . ., LШsТЭsФКвК, V. . & RЮШФШХКТЧОЧ, . V. 1999. . ., . ., . . ( Aphillophorales) ДАШШН-НОsЭrШвТЧР ПЮЧРТ (ШrНОr Aphyllophorales) ШП ЭСО KТгСТ ArМСТЩОХКРШЖ. – IЧ: KТгСТ ArМСТЩОХКРШ ТsХКЧНs. BТРОШРrКЩСТМ НОsМrТЩЭТШЧ. TrКЧsКМЭТШЧs ШП KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. SОr. BТШРОШРrКЩСв ШП KКrОХТК. IssЮО 1. SОr. B 1: 84−86, 157−158. (IЧ RЮssТКЧ). BШЧНКrЭsОЯК, . ., KrЮЭШЯ, V. I., LШsТЭsФКвК, V. ., KТЯТЧТОЦТ, S. N. & RЮШФШХКТЧОЧ, . V. 2000. . ., . ., . ., . ., . . (AЩСвХХШЩСШrКХОs s. ХКЭШ) (Aphyllophorales s. ХКЭШ) ДAЩСвХХШЩСШrШТН ПЮЧРТ (Aphyllophorales s. ХКЭШ).Ж – IЧ: GrШЦЭsОЯ, A.N. & KrЮЭШЯ, V.I. (ОНs.), IЧЯОЧЭШrв КЧН sЭЮНв ШП ЛТШХШРТМКХ НТЯОrsТЭв ШЧ ЭСО ГКШЧОгСвО PОЧТЧsЮХК КЧН ТЧ NШrЭСОrЧ PrТХКНШгСвО: OЩОrКЭ.–ТЧПШrЦ. ЦКЭОrТКХs. – PОЭrШгКЯШНsФ. Щ. 117–122. (IЧ RЮssТКЧ). ДDШМЮЦОЧЭКЭТШЧ ШП ЭСО МШЦЩХОб ОМШХШРТМКХ ТЧЯОЧЭШrв УЮsЭТПвТЧР ОsЭКЛХТsСЦОЧЭ ШП ЭСО ГКШЧОгСsФв sЭКЭО ЧКЭЮrО ЩКrФЖ. 2013. , « » NGO “SPOK”. – PОЭrШгКЯШНsФ.108 Щ. (IЧ RЮssТКЧ). MОХК, A. J. & CКУКЧНОr, A. K. (ОНs.) 1906. SЮШЦОЧ KКsЯТШ. SЮШЦКХКТsОЧ KТrУКХХТsЮНОЧ sОЮrКЧ ЭШТЦТЭЮФsТК 53, III. – HОХsТЧФТ, Б+ 764 Щ. + 1 ЦКЩ. IЯКЧЭОr, E. V. & KЮгЧОЭsШЯ, O. L. (ОНs.) 2007. .B., . . ( .). . ДRОН DКЭК BШШФ ШП RОЩЮЛХТМ ШП KКrОХТКЖ. – PОЭrШгКЯШНsФ. 368 Щ. (IЧ RЮssТКЧ). IЧНОб FЮЧРШrЮЦ. CABI DКЭКЛКsО. URL: СЭЭЩ://ааа.ТЧНОбПЮЧРШrЮЦ.ШrР, 2013. (КЩЩХТМКЭТШЧ НКЭО: 25 AЩrТХ, 2014). KШЭТrКЧЭК, H. & NТОЦОХт, T. 1996. UСКЧКХКТsОЭ ФттЯтЭ SЮШЦОssК. – HОХsТЧФТ. 184 Щ. KЮгЧОЭsШЯ, . L., BrКгШЯsФКвК, . I. & SЭШТФТЧК, N. V. 1999. . ., . ., . . , « » ДFХШrК, ЯОРОЭКЭТШЧ КЧН РОЧОsТs ШП ЦТrОs ТЧ ЭСО ЩrШЭОМЭТШЧ гШЧО ШП KТгСТ RОsОrЯО MЮsОЮЦЖ. – IЧ: KТгСТ ArМСТЩОХКРШ ТsХКЧНs. BТШРОШРrКЩСТМ НОsМrТЩЭТШЧ. TrКЧsКМЭТШЧs ШП ЭСО KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. SОr. BТШРОШРrКЩСв ШП KКrОХТК. PОЭrШгКЯШНsФ. Щ. 48–54. (IЧ RЮssТКЧ). LШsТЭsФКвК, V. ., KrЮЭШЯ, V. I., KТЯТЧТОЦТ, S. N. & RЮШФШХКТЧОЧ, . V. 2001. . ., . ., . ., . . (Aphyllophorales s. ХКЭШ) ДAЩСвХХШЩСШrШТН fungi (Aphyllophorales s. ХКЭШ)Ж. – IЧ: IЧЯОЧЭШrв КЧН sЭЮНв ШП ЛТШХШРТМКХ НТЯОrsТЭв ТЧ CОЧЭrКХ KКrОХТК (ЧОаsХОЭЭОr). KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 101–105. (IЧ RЮssТКЧ). RКssТ, P. HвЯтrТЧОЧ, E, JЮsХцЧ, A. & MКЧЧОrФШsФТ, I. (ОНs.), 2010. SЮШЦОЧ ХКУТОЧ ЮСКЧКХКТsЮЮs. PЮЧКТЧОЧ ФТrУК. TСО 2010 RОН LТsЭ ШП FТЧЧТsС SЩОМТОs. – HОХsТЧФТ, 2010. Щ. 249–263. RОН DКЭК BШШФ ШП ЧКЭЮrО ШП LОЧТЧРrКН RОРТШЧ. PХКЧЭs КЧН ПЮЧРТ (2000). – SЭ. PОЭОrsЛЮrР. 671 Щ. Reports of the Finnish Environment Institute 40 | 2014 241 RОН DКЭК BШШФ ШП ЭСО RЮssТКЧ FОНОrКЭТШЧ (PХКЧЭs КЧН ПЮЧРТ) (2008). ( ). – MШsМШа. 855 Щ. (IЧ RЮssТКЧ). RЮШФШХКТЧОЧ, . V. 2013 . . . ( ) ДAЩСвХХШЩСШrШТН ПЮЧРТ ШП ЭСО ГКШЧОгСвО PОЧТЧsЮХК, RОЩЮЛХТМ ШП KКrОХТКЖ. - IЧ: MШНОrЧ ЛШЭКЧв ТЧ RЮssТК. – PrШМООНТЧРs ШП ЭСО 13ЭС CШЧРrОss ШП ЭСО RЮssТКЧ BШЭКЧТМКХ SШМТОЭв КЧН ЭСО CШЧПОrОЧМО “SМТОЧЭТiМ ПЮЧНКЦОЧЭКХs ШП ЭСО ЩrШЭОМЭТШЧ КЧН МШЧsОrЯКЭТШЧ ШП ЭСО ЩХКЧЭ МШЯОr ШП ЭСО VШХРК ЛКsТЧ” (TШРХТКЭЭТ, 16–22 SОЩЭОЦЛОr 2013). VШХ. 1: EЦЛrвШХШРв. SЭrЮМЭЮrКХ ЛШЭКЧв. AХРШХШРв. MвМШХШРв. LТМСОЧШХШРв. BrвШХШРв. PКХОШЛШЭКЧв. BТШsвsЭОЦКЭТМs. TШРХТКЭЭТ: CКssКЧНrК. Щ. 173–174. (IЧ RЮssТКЧ). RЮШФШХКТЧОЧ, . V. 2013 Л. . . ДAЩСвХХШЩСШrШТН ПЮЧРЮs ЛТШЭК ШП ЭСО KТгСТ ArМСТЩОХКРШЖ. – IЧ: PrШМ. AХХ-RЮss. CШЧП. “BТШНТЯОrsТЭв ШП FКr NШrЭСОrЧ ОМШsвsЭОЦs: ТЧЯОЧЭШrв, ЦШЧТЭШrТЧР КЧН ЩrШЭОМЭТШЧ” (SвФЭвЯФКr, 3–7 JЮЧО 2013). SвФЭвЯФКr: IЧsЭТЭЮЭО ШП BТШХШРв, KШЦТ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs, UrКХТКЧ BrКЧМС, RAS, Щ. 248–250. (IЧ RЮssТКЧ). RЮШФШХКТЧОЧ, . V. 2013 М. . . ДАШШН-НОsЭrШвТЧР ПЮЧРТЖ. – IЧ: GrШЦЭsОЯ A.N. (ОН.) SОХФт ХКЧНsМКЩОs ШП ЭСО ГКШЧОгвО PОЧТЧsЮХК: NКЭЮrО, НОЯОХШЩЦОЧЭ, LКЧН ЮsО, CШЧsОrЯКЭТШЧ. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. Щ. 102–108. (IЧ RЮssТКЧ). Table 2. Numbers of wood-growing fungal species recorded on Zaonezhye Peninsula (nomenclature according to Index Fungorum 2014). Order/Family Species Agaricomycetes Incertae sedis Odonticium (1) Agaricales Cyphellaceae Chondrostereum (1) Incertae sedis Plicatura (1) Atheliales Atheliaceae Amphynema (1), Piloderma (1) Auriculariales Auriculariaceae Elmerina (1) Incertae sedis Pseudohydnum (1) Boletales Amylocorticiaceae Amylocorticium (2), Ceraceomyces (2) Coniophoraceae Coniophora (2) Serpulaceae Serpula (1) Tapinellaceae Pseudomerulius (1) Cantharellales Botryobasidiaceae Botryobasidium (3), Botryohypochnus (1) Cantharellaceae Cantharellus (1), Clavulina (1), Craterellus (2) Clavulinaceae Multiclavula (1) Hydnaceae Hydnum (2), Sistotrema (1) Corticiales Corticiaceae Corticium (1), Cytidia (1) Dacrymycetales Dacrymycetaceae Calocera (1) Gloeophyllales Gloeophyllaceae Gloeophyllum (2), Veluticeps (1) Gomphales Clavariadelphaceae Clavariadelphus (2) Gomphaceae Ramaria (3) Lentariaceae Kavinia (1), Lentaria (1) Hymenochaetales 242 Hymenochaetaceae Asterodon (1), Coltricia (1), Hymenochaete (1), Inonotus (3), Onnia (1), Phellinus (14), Pseudochaete (1), Tubulicrinis (2) Repetobasidiaceae Sidera (1), Resinicium (2) Reports of the Finnish Environment Institute 40 | 2014 Schizoporaceae Basidioradulum (1), Hyphodontia (12), Schizopora (1) Polyporales Fomitopsidaceae Amylocystis (1), Anomoporia (1), Antrodia (9), Climacocystis (1), Fomitopsis (2), Ischnoderma (1), Laetiporus (1), Phaeolus (1), Piptoporus (1), Postia (10), Pycnoporellus (2) Ganodermataceae Ganoderma (2) Meripilaceae Oxyporus (2), Physisporinus (1), Rigidoporus (1) Meruliaceae Bjerkandera (1), Crustoderma (2), Gloeoporus (3), Hyphoderma (1), Junghuhnia (4), Merulius (1), Mycoacia (2), Phlebia (6), Radulodon (1), Steccherinum (2) Phanerochaetaceae Antrodiella (4), Ceriporia (2), Ceriporiopsis (2), Phanerochaete (4), Phlebiopsis (1) Polyporaceae Aurantiporus (1), Cerrena (1), Daedaleopsis (3), Datronia (1), Dichomitus (1), Diplomitoporus (2), Fomes (1), Hapalopilus (1), Haploporus (1), Lenzites (1), Leptoporus (1), Perenniporia (1), Piloporia (1), Polyporus (5) Pycnoporus (1), Rhodonia (1), Skeletocutis (7), Trametes (5), Trichaptum (4) Xenasmataceae Phlebiella (1) Russulales Albatrellaceae Albatrellus (2) Amylostereaceae Amylostereum (1) Auriscalpiaceae Auriscalpium (1), Clavicorona (1) Bondarzewiaceae Gloiodon (1), Heterobasidion (1) Hericiaceae Hericium (2), Laxitextum (1) Lachnocladiaceae Dichostereum (1), Scytinostroma (2) Peniophoraceae Peniophora (2) Stereaceae Chaetoderma (1) Gloiothele (1) Stereum (4) Thelephorales Bankeraceae Bankera (1), Boletopsis (1), Hydnellum (3), Phellodon (2), Sarcodon (3) Thelephoraceae Thelephora (1), Tomentella (6) Trechisporales Hydnodontaceae Trechispora (2) Reports of the Finnish Environment Institute 40 | 2014 243 APPENDIX List of fungi recorded from Zaonezhye Peninsula, Syar-Peninsula and adjacent islands NOTES: Each species is provided by an estimation of frequency in Zaonezhye according to the following scale: rr (very rare), r (rare), str (fairly rare), p (here and there), stfq (fairly frequent), fq (frequent and very frequent). Species status: * - Indicator species of old-growth and deciduous forests (Kotiranta & Niemelä 1996); ** - Specialist and indicator species of minimally transformed forest (Andersson et al. 2009). Threat status: EN, NT, VU, DD − species included in the Red Data Book of Karelia, Kar (Ivanter & Kuznetsov 2007) and in the 2010 Red list of Finnish species, Fin (Rassi et al. 2010); 2, 3, 4 - Species included in the Red Data Book of nature of Leningrad Region, Len (Red Data Book…2000). ABBREVIATIONS: Bol. Klim. Isl. − Bolshoi Klimenetsky Island, comp. − forest compartment (kvartal or quartal in Russian). ** Albatrellus conluens (Alb. et Schwein. : Fr.) Kotl. et Pouzar – Syar peninsula, comp. 180, 182, north of Tambitsy, environs of Tolsty Navolok, comp. 71, pine and spruce forest, on litter, 22.08.2013, 26.08.2013, A.V. Ruokolainen; 18–19.08.2013, O. Manninen; str. A. ovinus (Schaeff.) Kotl. et Pouzar – Ruokolainen 2013 c; Lipovitsy, comp. 41, Lake Korbozero, Tipinitsy, spruce-dominated and mixed forest, on litter, 23.08.2013, 27.08.2013, A.V. Ruokolainen; str. Amphynema byssoides (Pers. : Fr.) J. Erikss. – Ruokolainen 2013 c; pine forest, comp. 13, on fallen spruce, 22.08.2013; p. Amylocorticium suaveolens Parmasto – Ruokolainen 2013 a, c; Velikaya Niva, motley grass spruce forest, on fallen spruce, 23.08.2012, A.V. Ruokolainen, PTZ; Tambitsy, Myrtillus spruce forest, on fallen spruce, 28.08.2013, A.V. Ruokolainen, PTZ; str. A. subincarnatum (Peck) Pouzar – Ruokolainen 2013 c; spruce forest, on fallen spruce. Threat status: Fin – VU; str. *, ** Amylocystis lapponica (Romell) Singer – Ruokolainen 2013 a, c; Lipovitsy; Lake Korbozero, Tipinitsy, north of Tambitsy, environs of Tolsty Navolok, comp. 71, Myrtillus spruce forest, on fallen spruce, 21.08.2013, 26.08.2013, 27.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 152–153, 174–176, 180–181, 16–17.08.2013, 19.08.2013, O. Manninen; str. Threat status: Fin – NT. Amylostereum chailletii (Pers.) Boidin – Ruokolainen 2013 a; Lipovitsy, comp. 41, Myrtillus spruce forest, on fallen spruce, 23.08.2013, A.V. Ruokolainen, PTZ; str. *, ** Anomoporia kamtschatica (Parmasto) Bondartseva – old-growth pine-dominated forest, on dead pine, 27.06.2013 and 22.08.2013, O. Manninen; rr. *, ** Antrodia albobrunnea (Romell) Ryvarden – Syar peninsula, comp. 153, 182, 183, old-growth pine-dominated forest, on dead pine, 17.08.2013 and 18.08.2013, O. Manninen; stp. Threat status: Fin – NT. * A. crassa (P. Karst.) Ryvarden – Documentation ... 2013; Syar peninsula, comp. 187, old-growth pine-dominated forest, 19.08.2013, O. Manninen; r. Threat status: Kar – 2 (EN), Len – 2, Fin – EN. A. heteromorpha (Fr. : Fr.) Donk – Syar peninsula, comp. 180, on aspen, 19.08.2013, O. Manninen; r. *A. inirma Rennvall et Niemelä – Syar peninsula, comp. 180, 183, 18–19.08.2013; 24.08.2013, O. Manninen; r. Threat status: Fin – VU. 244 Reports of the Finnish Environment Institute 40 | 2014 *, ** A. pulvinascens (Pilát) Niemelä – Documentation ... 2013; Syar peninsula, comp. 181, 19.08.2013, 24.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Fin – VU. A. serialis (Fr.) Donk – Bondartseva et al. 1999; Ruokolainen 2013 c; southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 03.07.1997, A.V. Ruokolainen, PTZ; fq. A. sinuosa (Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 c; southern part on Bol. Klim. Isl., spruce forest on fallen pine, 06.07.1997, A.V. Ruokolainen, PTZ; fq. A. sitchensis (D.V. Baxter) Gilb. et Ryvarden – 24.08.2013, O. Manninen; r. Threat status: Fin – EN. A. xantha (Fr. : Fr.) Ryvarden – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 06.07.1997, A.V. Ruokolainen, PTZ; fq. *, ** Antrodiella citrinella Niemelä et Ryvarden – Documentation ... 2013; rr. Threat status: Kar – 3 (VU), Fin – NT. A. hoehnelii (Bres.) Niemelä – mixed forest on deadwood of deciduous trees, 23.08.2013, O. Manninen; rr. Threat status: Len – 3. A. pallasii Renvall, Johann. et Stenlid – Tambitsy, Myrtillus spruce forest, on fallen spruce, 27.08.2013, A.V. Ruokolainen, PTZ; r. A. pallescens (Pilát) Niemelä et Miettinen – Ruokolainen 2013 c; Zharnikovo, mixed forest on fallen Sorbus aucuparia, 01.08.2012, A.V. Ruokolainen, PTZ; p. *, **Asterodon ferruginosus Pat. – Ruokolainen 2013 c; Syar peninsula, comp. 178, 186, 18- 19.08.2013, O. Manninen; Lipovitsy, comp. 41, north of Tambitsy, environs of Tolsty Navolok, comp. 71, 23.08.2013, 26.08.2013, 28.08.2013, spruce forest on fallen aspen, pine and spruce, A.V. Ruokolainen; pine forest, comp. 13, on fallen pine, 22.08.2013, A.V. Ruokolainen, PTZ; stp. ** Aurantipoporus issilis (Berk et M.A. Curtis) H. Jahn [= Tyromyces issilis (Berk et M.A. Curtis) Donk] – Documentation ... 2013; on deciduous trees, 24.08.2013, O. Manninen; rr. Threat status: Kar – 3 (VU), Len – 3, Fin – NT. Auriscalpium vulgare Gray – near the road, 28.06.2013, O. Manninen; r. ** Bankera fuligineoalba (J.C. Schmidt) Coker et Beers ex Pouzar – Syar peninsula, comp. 185, pine forest, on litter, 19.08.2013, O. Manninen; r. Basidioradulum radula (Fr.) Nobles – Ruokolainen 2013 c; Zharnikovo, mixed forest on deadwood of Sorbus aucuparia, 01.08.2012, A.V. Ruokolainen; Palozero, mixed forest, on deadwood of deciduous trees, 23.08.2012, A.V. Ruokolainen; p. Bjerkandera adusta (Willd.: Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., H; Kizhi Isl., on deadwood of Sorbus aucuparia, 16.07.1998, V.I. Krutov, PTZ; Tipinitsy, spruce forest, on aspen, 27.08.2013; Tambitsy, spruce forest, on aspen, 28.08.2013, A.V. Ruokolainen; stfq. ** Boletopsis grisea (Peck) Bondartsev et Singer – Ruokolainen 2013 a; south of the village of Lambasruchei, pine forest, on litter, 23.08.2012, A.V. Ruokolainen; r. Threat status: Fin – NT. Botryobasidium laeve (J. Erikss.) Parmasto – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on fallen spruce; p. B. subcoronatum (Höhn. et Litsch.) Donk – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on fallen spruce; stp. B. vagum (Berk. et M.A. Curtis) D.P. Rogers – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., on fallen spruce, 05.07.1997, A.V. Ruokolainen, PTZ; p. Botryohypochnus isabellinus (Fr.) J. Erikss. – Ruokolainen 2013 c; Zharnikovo, mixed forest, on dead Alnus incana, 01.08.2012, A.V. Ruokolainen; p. Calocera viscosa (Pers. : Fr.) Fr. – Ruokolainen 2013 c; environs of Velikaya Niva, mixed spruce-dominated forest, on litter, 23.08.2012, A.V. Ruokolainen; p. Cantharellus cibarius Fr. – Ruokolainen 2013 c; south of the village of Lambasruchei, pine forest, on litter, 23.08.2012, A.V. Ruokolainen; common species, stfq. Reports of the Finnish Environment Institute 40 | 2014 245 Ceraceomyces microsporus K.H. Larss. – Ruokolainen 2013 c; pine forest, near the lake, comp. 13, on fallen pine, 22.08.2013, A.V. Ruokolainen, PTZ; p. C. serpens (Tode : Fr.) Ginns – Ruokolainen 2013 c; Paltega, motley grass birch forest, on fallen birch, 06.08.2011, A.V. Ruokolainen, PTZ; p. Ceriporia excelsa S. Lundell ex Parmasto – Ruokolainen 2013 a, b, c; Kizhi Isl., on fallen Sorbus aucuparia, 04.08.2012, A.V. Ruokolainen, PTZ; rr. Threat status: Fin – NT. C. viridans (Berk. et Broome) Donk – Ruokolainen 2013 a; northeast of Velikaya Guba, on fallen Alnus incana, 17.08.2010, A.V. Ruokolainen, PTZ; rr. Ceriporiopsis aneirina (Sommerf. : Fr.) Domański – on dead aspen, 26.06.2013, O. Manninen; rr. Threat status: Len – 3. C. resinascens (Romell) Domański – Ruokolainen 2013 c; Polya, mixed forest, on fallen aspen, 25.08.2013, A.V. Ruokolainen, PTZ; 27–28.08.2013, O. Manninen; r. Threat status: Len – 3. Cerrena unicolor (Bull.) Murrill – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen birch, 06.07.1997, A.V. Ruokolainen; Zharnikovo, mixed forest, on deadwood of Salix caprea, 01.08.2012, A.V. Ruokolainen, stfq. *, ** Chaetoderma luna (Romell ex Rogers et H.S. Jacks.) Parmasto – Ruokolainen 2013 c; environs of Velikaya Niva, pine forest, on dead pine, 17.08.2010; A.V. Ruokolainen; Syar peninsula, comp. 180, 183, pine forest, on dead pine, 18–19.08.2013, O. Manninen; r. Chondrostereum purpureum (Pers. : Fr.) Pouzar – Bondartseva et al. 1999; Kizhi Isl., on deadwood of alder, 16.07.1998, V.I. Krutov, PTZ; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest, on fallen birch, 26.08.2013, A.V. Ruokolainen; p. Clavariadelphus ligula (Schaeff. : Fr.) Donk – Ruokolainen 2013 c; south of the village of Lambas Ruchei, pine forest, on litter, 23.08.2012, A.V. Ruokolainen; r. ** C. pistillaris (L. : Fr.) Donk – Documentation ... 2013; on litter, 23.08.2013 and 26.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Len – 3. Clavicorona pyxidata (Pers.) Doty – Bondartseva et al. 1999; Ruokolainen 2013 c; Korbozero, Tipinitsy, Lipovitsy, comp. 41, north of Tambitsy, environs of Tolsty Navolok, comp. 71, mixed spruce-dominated forest, on fallen aspen, 23.08.2013, 26–27.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 178, 186, 16.08.2013, 18–19.08.2013, O. Manninen; p. Clavulina cinerea (Bull. : Fr.) J. Schröt. – Ruokolainen 2013 a; Podyelniki, ecological trail, on litter, 03.08.2012, A.V. Ruokolainen, PTZ; Kizhi Isl., on litter, 04.08.2012, A.V. Ruokolainen, PTZ; r. ** Climacocystis borealis (Fr.) Kotl. et Pouzar – Ruokolainen 2013 a, c; Lipovitsy, comp. 41, north of Tambitsy, environs of Tolsty Navolok, comp. 71, Tipinitsy, mixed herb-rich and spruce forest, on dead spruce, 23.08.2013, 26–27.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 153, 178, 181, 16.08.2013, 17–19.08.2013, O. Manninen; stfq. Coltricia perennis (L. : Fr.) Murrill – Ruokolainen 2013 c; near Lake Nizhnee Pigmosero, on dead Salix, 22.08.2012, A.V. Ruokolainen; pine forest, comp. 13, on litter, 22.08.2013, A.V. Ruokolainen; p. Coniophora arida (Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 c; fq. C. olivacea (Pers. : Fr.) P. Karst. – Ruokolainen 2013 c; Ruokolainen 2013 c; fq. Corticium roseum Pers. : Fr. – Ruokolainen 2013 c; north of Tambitsy, environs of Tolsty Navolok, comp. 71, Korbozero, Tipinitsy, spruce and mixed forest, on fallen aspen, A.V. Ruokolainen; p. Craterellus cornucopioides (L. : Fr.) Pers. – Ruokolainen 2013 c; environs of Velikaya Niva, spruce forest, on deadwood of Salix, 23.08.2012, A.V. Ruokolainen; Lipovitsy, comp. 41, Tambitsy, spruce forest on litter, 23.08.2013, 28.08.2013, A.V. Ruokolainen; stp. Threat status: Kar – 3 (NT). C. tubaeformis (Fr.) Quél. – Lipovitsy, spruce forest, on litter, stp. 246 Reports of the Finnish Environment Institute 40 | 2014 *, ** Crustoderma corneum (Bourdot et Galzin) Nakasone – Syar peninsula, comp. 180, 182–183, on fallen pine, 18–19.08.2013; 22.08.2013, O. Manninen; r. Threat status: Fin – NT. *, ** C. dryinum (Berk. et M.A. Curtis) Parmasto – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on fallen spruce, 10.08.2010, A.V. Ruokolainen; Lipovitsy, Myrtillus spruce forest, on fallen spruce, 21.08.2013, A.V. Ruokolainen, PTZ; north of Tambitsy, environs of Tolsty Navolok, comp. 71, 26.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 154, 17.08.2013, O. Manninen; stp. Threat status: Fin – NT. Cytidia salicina (Fr.) Burt – Ruokolainen 2013 c; near Lake Nizhnee Pigmosero, on deadwood of Salix, 22.08.2012, A.V. Ruokolainen; stp. Daedaleopsis confragosa (Bolton) Schröt. – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., on deadwood of Sorbus aucuparia, 16.07.1998, V.I. Krutov, PTZ; Bol. Klim. Isl., LE; like Kopanez, on birch, 15.07.1999, A.V. Polevoi, PTZ; Zharnikovo, mixed and birch forest on fallen Alnus incana and Salix, A.V. Ruokolainen; p. D. septentrionalis (P. Karst.) Niemelä – Ruokolainen 2013 c; environs of Velikaya Niva, pine forest, on dead birch, 23.08.2012; stp. D. tricolor (Bull. : Fr.) Bondartsev et Singer – Bondartseva et al. 1999; Kizhi Isl., LE; like Kopanez, on dead birch, 15.07.1999, A.V. Polevoi, PTZ; stp. Datronia mollis (Sommerf.) Donk – Bondartseva et al. 1999; Ruokolainen 2013 c; north of Tambitsy, environs of Tolsty Navolok, comp. 71, Tambitsy, Kaskoselga, south of Uzkaya Salma, mixed forest, on birch and aspen, 11.08.2010, 13.08.2010, 26.08.2013, 28.08.2013, A.V. Ruokolainen; p. * Dichomitus squalens (P. Karst.) D.A. Reid – Ruokolainen 2013 c; pine-dominated forest, on fallen spruce, 17.08.2010, A.V. Ruokolainen; r. Threat status: Kar – 3 (NT), Fin – VU. Dichostereum boreale (Pouzar) Ginns et M.N.L. Lefebvre – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on fallen spruce, 10.08.2010, A.V. Ruokolainen; stp. *, ** Diplomitoporus crustulinus (Bres.) Domański – Ruokolainen 2013 a, c; south of the village of Uzkaya Salma, moist spruce forest, on fallen spruce, 13.08.2010, A.V. Ruokolainen, PTZ; rr. Threat status: Fin – VU. D. lavescens (Bres.) Ryvarden – Ruokolainen 2013 a; Velikaya Guba, pine forest, on pine, 17.08.2010, A.V. Ruokolainen, PTZ; Ladmozero, old-growth pine forest, on dead pine, 24.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 174, 177, 180, old-growth pine forest, on dead pine, 17–19.08.2013, O. Manninen; stp. Threat status: Fin – NT. Elmerina caryae (Schwein) D.A. Rein [= Protomerulius caryae (Schwein) Ryvarden] – Bondartseva et al. 2000; Documentation ... 2013; Syar peninsula, comp. 180, 19.08.2013, O. Manninen; rr. Threat status: Kar – 3 (VU), Len – 3, Fin – NT. Fomes fomentarius (L.) Fr. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; mixed spruce-dominated forest, on dead birch, fq. Fomitopsis pinicola (Sw. : Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; mixed spruce-dominated forest on deadwood of birch, fq. *, ** F. rosea (Alb. et Schwein. : Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; Lipovitsy, comp. 41, Podyelniki, north of Tambitsy, environs of Tolsty Navolok, comp. 71, Tipinitsy, south of the village of Uzkaya Salma et al., spruce forest on deadwood of spruce, A.V. Ruokolainen; Syar peninsula, comp. 133, 151–154, 174–177, 180–183, 186, 17–19.08.2013, O. Manninen; p. Threat status: Fin – NT. Ganoderma applanatum (Pers.) Pat. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., H; Bol. Klim. Isl., LE; Zharnikovo, mixed forest, on deadwood of Sorbus aucuparia and Salix caprea, 01.08.2012, A.V. Ruokolainen; Lipovitsy, comp. 41, spruce forest on fallen aspen, 23.08.2013, A.V. Ruokolainen; p. ** G. lucidum (M. A. Curtis : Fr.) P. Karst. – Documentation ... 2013; Lake Korbozero, Tipinitsy, mixed forest on old birch, 27.08.2013, A.V. Ruokolainen, PTZ; rr. Threat status: RF – 3, Len – 3, Kar – 3 (VU). Reports of the Finnish Environment Institute 40 | 2014 247 Gloeophyllum odoratum (Wulfen : Fr.) Imazeki – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., H; near Lake Nizhnee Pigmosero, on deadwood of pine, 22.08.2012, A.V. Ruokolainen; Tipinitsy, spruce forest, on deadwood of spruce, 27.08.2013, A.V. Ruokolainen; r. G. sepiarium (Wulfen : Fr.) P. Karst. – Bondartseva et al. 1999; Bol. Klim. Isl., LE; near Lake Nizhnee Pigmosero, on deadwood of spruce, 22.08.2012, A.V. Ruokolainen; p. Gloeoporus dichrous (Fr. : Fr.) Bres. – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., LE; Zharnikovo, Tipinitsy, spruce and mixed forest, on birch, aspen and Sorbus aucuparia; p. ** G. pannocinctus (Romell) J. Erikss. – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; north of Podyelniki, spruce forest on fallen aspen, 11.08.2010, A.V. Ruokolainen, PTZ; stp. Threat status: Len – 3. *, ** G. taxicola (Pers. : Fr.) Gilb. et Ryvarden – Ruokolainen 2013 b, c; Lipovitsy, comp. 43, south of Lipovitsy, comp. 63, Myrtillus spruce forest, on fallen spruce, 18.08.2010, A.V. Ruokolainen, PTZ; Zharnikovo, pine forest on fallen pine, 02.08.2012, A.V. Ruokolainen, PTZ; Podyelniki, pine forest on fallen pine, 03.08.2012, A.V. Ruokolainen; 22–24.08.2013, O. Manninen; stp. Threat status: Len – 3. *, ** Gloiodon strigosus (Schwein. : Fr.) P. Karst. – Documentation ... 2013; mixed forest, on deadwood of deciduous trees (aspen, Salix caprea), 23–24.08.2013, 28.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Fin – NT. Gloeothele citrina (Pers.) Ginns et G.W. Freeman – Ruokolainen 2013 c; Podyelniki, Zubovo, on fallen pine, 03.08.2012, A.V. Ruokolainen, PTZ; stp. Hapalopilus rutilans (Pers.) P. Karst. – Ruokolainen 2013 c; like Kopanez, on dead birch, 15.07.1999, A.V. Polevoi, PTZ; Zharnikovo, mixed forest, on deadwood of birch, 01.08.2012, A.V. Ruokolainen; near Lake Nizhnee Pigmosero, on deadwood of birch, 22.08.2012, A.V. Ruokolainen; p. ** Haploporus odorus (Sommerf. : Fr.) Bondartsev et Singer – Documentation ... 2013; comp. 183, on old Salix caprea, 18.08.2013, O. Manninen; rr. Threat status: Kar – 3 (VU), Len – 3, Fin – NT. Hericium cirrhatum (Pers.) Nikol. – Ruokolainen 2013 c; Zharnikovo, environs of Velikaya Niva, mixed and spruce-dominated forest, on Salix caprea and aspen, 05.08.2012, 23.08.2012, A.V. Ruokolainen; r. Threat status: Len – 3. ** H. coralloides (Scop.) Pers. – Ruokolainen 2013 c; Bol. Klim. Isl., on deadwood of deciduous trees, 09.08.2010; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest on birch and aspen, 26.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 132, 180, 185, 16.08.2013, 19.08.2013, O. Manninen; stp. Threat status: Kar – 3 (NT). Heterobasidion parviporum Niemelä et Korhonen – Bondartseva et al. 1999; Ruokolainen 2013 b; Bol. Klim. Isl., LE; Bol. Klim. Isl., spruce forest, on fallen spruce, 03.07.1997, A.V. Ruokolainen, PTZ; stp. Hydnellum aurantiacum (Batsch) P. Karst. – Ruokolainen 2013 , c; Ladmozero, south of the village of Lambasruchei, Vanchozero, pine forest on litter, 24–25.08.2012, A.V. Ruokolainen; stp. H. caeruleum (Hornem.) P. Karst. – Ruokolainen 2013 c; Vanchozero, pine forest, on litter, 25.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 185, 19.08.2013, O. Manninen; stp. H. ferrugineum (Fr.) P. Karst. – Ruokolainen 2013 c; north of Podyelniki, south of the village of Lambasruchei, Vanchozero, pine forest on litter, 11.08.2010, 24–25.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 154, 177, 180, 182, 185, 17–19.08.2013, O. Manninen; stp. Hydnum repandum L. : Fr. – Ruokolainen 2013 c; environs of Velikaya Niva, spruce forest, on litter, 23.08.2012, A.V. Ruokolainen; stp. 248 Reports of the Finnish Environment Institute 40 | 2014 H. rufescens Schaeff. : Fr. – Ruokolainen 2013 c; environs of Velikaya Niva, spruce forest, on litter, 23.08.2012, A.V. Ruokolainen; stp. Hymenochaete rubiginosa (Fr.) Lév. – Bondartseva et al. 1999; Klimenetsky Isl., LE; southern part of Bol. Klim. Isl., 07.07.1997, A.V. Ruokolainen, PTZ; r. Hyphoderma setigerum (Fr.) Donk – Bondartseva et al. 1999; Kizhi Isl., LE; Kizhi Isl., on Sorbus aucuparia and Alnus incana, 16.07.1998, V.I. Krutov, PTZ; r. Hyphodontia abieticola (Bourdot et Galzin) J. Erikss. – Lake Korbozero, Tipinitsy, mixed forest on fallen pine, 27.08.2013, A.V. Ruokolainen, PTZ; stp. H. alienata (S. Lundell) J. Erikss. – Ruokolainen 2013 c; Lipovitsy, spruce forest, on fallen spruce, 21.08.2013, A.V. Ruokolainen, PTZ; stp. H. alutacea (Fr.) J. Erikss. – Ruokolainen 2013 c; north of Podyelniki, on fallen spruce, 11.08.2010, A.V. Ruokolainen; stp. H. alutaria (Burt) J. Erikss. – Ruokolainen 2013 c; 1,5 km southwestern of Velikaya Guba, Myrtillus pine forest on fallen pine, 19.08.2010, A.V. Ruokolainen, PTZ; north of Podyelniki, on fallen spruce, 10.08.2010, A.V. Ruokolainen; stp. H. arguta (Fr.) J. Erikss. – Ruokolainen 2013 c; Zharnikovo, mixed forest, on deadwood of Salix caprea and Sorbus aucuparia, 05.08.2012, A.V. Ruokolainen; stp. H. aspera (Fr.) J. Erikss. – Ruokolainen 2013 c; north of Podyelniki, on fallen pine and spruce, 10–11.08.2010, A.V. Ruokolainen; p. H. barba-jovis (Bull. : Fr.) J. Erikss. – Ruokolainen 2013 c; south of Tambitsy, birch forest with spruce on fallen birch, 04.08.2011, A.V. Ruokolainen, PTZ; p. H. breviseta (P. Karst.) J. Erikss. – Ruokolainen 2013 c; Zharnikovo, pine forest, on fallen pine; p. H. crustosa (Pers. : Fr.) J. Erikss. – Bondartseva et al. 1999; Kizhi Isl., on Alnus incana, LE; r. H. detritica (Bourdot et Galzin) J. Erikss. – Polya, mixed forest on fallen aspen, 25.08.2013, A.V. Ruokolainen, PTZ; r. H. pruni (Lasch) Svrček – Bondartseva et al. 1999; Kizhi Isl., on deadwood of Ulmus, LE; r. H. subalutacea (P. Karst.) J. Erikss. – Bondartseva et al. 1999; Bol. Klim. Isl., LE; by the lake in pine forest, comp. 13, on fallen pine, 22.08.2013, A.V. Ruokolainen, PTZ; stp. Inonotus obliquus (Pers. : Fr.) Pilát – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., on Alnus incana, 16.07.1998, S.N. Kiviniemi, V.I. Krutov, PTZ; stfq. I. radiatus (Sowerby : Fr.) P. Karst. – Ruokolainen 2013 c; Lipovitsy, comp. 41, environs of Tolsty Navolok, comp. 71, on deadwood of Alnus incana, 23.08.2013, 26.08.2013, A.V. Ruokolainen; stp. I. rheades (Pers.) Bondartsev et Singer – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; north of Podyelniki, mixed forest on deadwood of aspen, 03.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 174, 176, 17.08.2013, O. Manninen; stp. Ischnoderma bensoinum (Wahlenb. : Fr.) P. Karst. – Ruokolainen 2013 c; north of Podyelniki, environs of Tolsty Navolok, comp. 71, Lake Korbozero, Tipinitsy, Polya, comp. 82–83, spruce forest, on deadwood of spruce, 11.08.2010, 05.08.2011, 26–27.08.2013, A.V. Ruokolainen; stp. *, ** Junghuhnia collabens (Fr.) Ryvarden – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 05.07.1997, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 180, 183, 18–19.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Len – 3, Fin – NT. * J. luteoalba (P. Karst.) Ryvarden – Ruokolainen 2013 c; Velikaya Guba, Myrtillus pine forest on fallen pine, 08.08.2011, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 154, 17.08.2013, O. Manninen; r. Reports of the Finnish Environment Institute 40 | 2014 249 J. nitida (Pers. : Fr.) Ryvarden – on deadwood of deciduous trees, 24.08.2013, O. Manninen; rr. ** J. pseudozilingiana (Parmasto) Ryvarden – Ruokolainen 2013 c; Bolshoi Lelikovskiy Isl., pine forest with spruce on old birch, 09.08.2010, A.V. Ruokolainen, PTZ; Lipovitsy, spruce forest on deadwood of aspen, 21.08.2013, A.V. Ruokolainen, PTZ; Tambitsy, spruce forest with aspen, on fallen aspen, 28.08.2013, A.V. Ruokolainen, PTZ; stp. Threat status: Kar – 4 (DD), Len – 4, Fin – VU. ** Kavinia alboviridis (Mordan) Gilb. et Budington – Documentation ... 2013; Syar peninsula, comp. 134, south of Tambitsy, spruce forest on deadwood, 28.08.2013, O. Manninen; rr. Threat status: Kar – 4 (DD). Laetiporus sulphureus (Bull. : Fr.) Murrill - Lipovitsy, comp. 41, spruce forest on deadwood of aspen, 23.08.2013, A.V. Ruokolainen; rr. Laxitextum bicolor (Pers.) Lentz – Ruokolainen 2013 c; near Lake Nizhnee Pigmosero, on Alnus incana, 22.08.2012, A.V. Ruokolainen; stp. Lentaria byssiseda (Pers. : Fr.) Corner – Polya, mixed forest on Salix, 25.08.2013, A.V. Ruokolainen, PTZ; rr. Lenzites betulina (L.) Fr. – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., on deadwood of Sorbus aucuparia, LE; stp. *, ** Leptoporus mollis (Pers.) Quél. – Ruokolainen 2013 c; south of Tambitsy, birch forest with spruce on fallen spruce, 04.08.2011, A.V. Ruokolainen, PTZ; Lipovitsy, comp. 41, spruce forest on on deadwood of spruce, 23.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 133, 178, on deadwood of spruce. 16.08.2013, 18.08.2013, O. Manninen; stp. Threat status: Kar – 3 (NT), Len – 3. Merulius tremellosus Schrad. : Fr. – Ruokolainen 2013 c; Zharnikovo, mixed forest, on deadwood of aspen, 05.08.2012, A.V. Ruokolainen; Lipovitsy, spruce forest on fallen aspen, 21.08.2013, A.V. Ruokolainen; Lake Korbozero, Tipinitsy, spruce forest, on deadwood of aspen, 27.08.2013, A.V. Ruokolainen; p. ** Multiclavula mucida (Pers. : Fr.) R.H. Petersen – northwest of the Vatnavolok village, Syar peninsula, comp. 174, on deadwood of aspen, 17.08.2013, O. Manninen; 24.08.2013, O. Manninen; north of Tambitsy, environs of Tolsty Navolok, comp. 71, mixed forest, on deadwood of aspen, 26.08.2013, A.V. Ruokolainen; stp. Mycoacia fuscoatra (Fr. : Fr.) Donk – Lipovitsy, comp. 41, spruce forest on deadwood of aspen, 23.08.2013; stp. Threat status: Len – 3. M. uda (Fr.) Donk – Ruokolainen 2013 c; south of the village of Lambasruchei, Lake Onega shore, pine forest on fallen aspen, 24.08.2012, A.V. Ruokolainen, PTZ; stp. Odonticium romellii (S. Lundell) Parmasto – northwest of the Vatnavolok village, Syar peninsula, comp. 154, 180, 185, on deadwood of pine, 17.08.2013, 19.08.2013; 22.08.2013, 27.08.2013, O. Manninen; r. Threat status: Fin – NT. *, ** Onnia leporina (Fr.) H. Jahn – Ruokolainen 2013 c; Syar peninsula, comp. 154, 176, on deadwood of spruce, 17.08.2013, O. Manninen; north of Tambitsy, environs of Tolsty Navolok, Tambitsy, Lake Korbozero, Tipinitsy, comp. 71, 132, 177, 193, mixed herbrich and spruce forest on old deadwood spruce, 26–28.08.2013, A.V. Ruokolainen; stp. Oxyporus corticola (Fr.) Ryvarden – Bondartseva et al. 1999; southern part on Bol. Klim. Isl., spruce forest on fallen aspen, 04.07.1997, A.V. Ruokolainen, PTZ; Zharnikovo, mixed forest on fallen of Sorbus aucuparia, A.V. Ruokolainen; Syar peninsula, comp. 153, 180, 17.08.2013, 19.08.2013, O. Manninen; p. O. populinus (Schumach. : Fr.) Donk – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., H; Zharnikovo, mixed forest on Salix, A.V. Ruokolainen; Tambitsy, spruce forest on deadwood of aspen, 28.08.2013, A.V. Ruokolainen; p. Peniophora incarnata (Pers.) P. Karst. – Ruokolainen 2013 c; south of the village of Uzkaya Salma, moist spruce forest on fallen aspen, 13.08.2010, A.V. Ruokolainen, PTZ; p. 250 Reports of the Finnish Environment Institute 40 | 2014 P. rufa (Pers. : Fr.) M.P. Christ. – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; r. *, ** Perenniporia subacida (Peck) Donk – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; Polya, Myrtillus spruce forest, on fallen spruce, 25.08.2013, A.V. Ruokolainen, PTZ; r. Threat status: Fin – NT. *, ** Phaeolus schweinitzii (Fr.) Pat. – northwest of the Vatnavolok village, Syar peninsula, comp. 154, 184, in old-growth forest on the roors of pine, 17.08.2013, 19.08.2013, O. Manninen; r. Phanerochaete laevis (Fr.) J. Erikss. et Ryvarden – Ruokolainen 2013 c; environs of Velikaya Niva, spruce forest on deadwood of aspen, 23.08.2012, A.V. Ruokolainen; p. Ph. sanguinea (Fr.) Pouzar – Ruokolainen 2013 c; south of the village of Uzkaya Salma, north of Podyelniki, spruce forest on fallen pine and spruce, 11.08.2010, 13.08.2010, A.V. Ruokolainen; Tambitsy, spruce forest on deadwood of birch, 28.08.2013, A.V. Ruokolainen; p. Ph. sordida (P. Karst.) J. Erikss. et Ryvarden – Ruokolainen 2013 c; Zharnikovo, mixed forest, on Alnus incana, 05.08.2012; p. Ph. velutina (DC. : Fr.) P. Karst. – Tambitsy, Myrtillus spruce forest, on fallen spruce, 28.08.2013, A.V. Ruokolainen, PTZ; stp. Phellinus alni (Bondartsev) Parmasto – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., Zharnikovo, pine and mixed forest, on Alnus incana, A.V. Ruokolainen; p. *, ** Ph. chrysoloma (Fr.) Donk – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 03.07.1997, A.V. Ruokolainen, PTZ; north of Podyelniki, 03.08.2012, A.V. Ruokolainen; Lipovitsy, Polya, north of Tambitsy, environs of Tolsty Navolok, Tambitsy, Lake Korbozero, Tipinitsy, comp. 41, 71, 84, 177, 193 et al., spruce forest on old deadwood spruce, 23– 24.08.2013, 26–27.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 151–154, 177–178, 180–181, 183, 16–19.08.2013, O. Manninen; p. Ph. conchatus (Pers. : Fr.) Quél. – Ruokolainen 2013 b, c; like Kopanez, on deadwood of deciduous trees, 13.07.1999, A.V. Polevoi, PTZ; Lake Korbozero, Tipinitsy, environs of Velikaya Niva, Zharnikovo, north of Podyelniki, Polya, spruce and mixed forest on deadwood of Salix caprea, 23.08.2012, A.V. Ruokolainen; p. *, ** Ph. ferrugineofuscus (P. Karst.) Bourdot – Bondartseva et al. 1999; Ruokolainen 2013 a, c; Bol. Klim. Isl., LE; environs of Velikaya Niva, spruce forest on deadwood of spruce, 23.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 153–154, 174–178, 180, 181, 183, 186, 17–19.08.2013, O. Manninen; Lipovitsy, Polya, Lake Korbozero, north of Podyelniki, Tambitsy, Tipinitsy, comp. 41, 84, 177, 132, et al., A.V. Ruokolainen; p. Ph. igniarius (L. : Fr.) Quél. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., on deadwood of Salix caprea, 16.07.1998, V.I. Krutov, PTZ; Kizhi Isl., LE; southern part on Bol. Klim. Isl., LE; Zharnikovo, A.V. Ruokolainen; p. Ph. laevigatus (P. Karst.) Bourdot et Galzin – Ruokolainen 2013 c; Bolshoi Lelikovskiy Isl., pine forest with spruce on old deadwood birch, 09.08.2010, north of Podyelniki, south of the village of Uzkaya Salma, 10–11.08.2010, 13.08.2010, A.V. Ruokolainen; Syar peninsula, comp. 153, 17.08.2013, O. Manninen; stp. * Ph. lundelii Niemelä – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest on deadwood of birch, 07.07.1997, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 132, 176, 16–17.08.2013, O. Manninen; Lipovitsy, north of Tambitsy, environs of Tolsty Navolok, Tambitsy, A.V. Ruokolainen; stp. Ph. nigricans (Fr.) P. Karst. – Bondartseva et al. 1999 (Ph. igniarius); Ruokolainen 2013 b, c; Bolshoi Lelikovskiy Isl., southern part on Bol. Klim. Isl., Zharnikovo, Polya, Tambitsy, mixed spruce-dominated forest on dead birch; fq. *, ** Ph. nigrolimitatus (Romell) Bourdot et Galzin – Ruokolainen 2013 a, c; north of Podyelniki, Lipovitsy, spruce forest on dead spruce, 11.08.2010, 05–06.08.2011, 23.08.2013, Reports of the Finnish Environment Institute 40 | 2014 251 A.V. Ruokolainen; Syar peninsula, comp. 174, 176, 186, 17.08.2013, 19.08.2013, O. Manninen; stp. *, ** Ph. pini (Brot. : Fr.) A. Ames – Ruokolainen 2013 a, c; south of the village of Lambasruchei, old-growth pine forest, on old pine, 24.08.2012, 22.08.2013, 27.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 134, 152–154, 174–178, 180–184, 186, 16–19.08.2013, O. Manninen; p. ** Ph. populicola Niemelä – Ruokolainen 2013 a, c; south of the village of Lambasruchei, Lake Onega shore, Lipovitsy, Tipinitsy, mixed forest on dead of aspen, 24.08.2012, 23–25.08.2013, A.V. Ruokolainen; Syar peninsula, comp. 133–134, 153–154, 174–175, 177, 180, 182–183, 17–19.08.2013, O. Manninen; stp. Ph. punctatus (P. Karst.) Pilát – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi Isl., on deadwood of Salix caprea, 16.07.1998, V.I. Krutov, PTZ; Zharnikovo, Polya, on Alnus incana and Sorbus aucuparia, 01.08.2012, 24.08.2013, A.V. Ruokolainen; p. Ph. tremulae (Bondartsev) Bondartsev et P.N. Borisov – Bondartseva et al. 1999, Ruokolainen 2013 a, b, c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest on dead aspen, 09.07.1997, A.V. Ruokolainen, PTZ; Polya, Zharnikovo, spruce-dominated forest on dead aspen, A.V. Ruokolainen, fq. *, ** Ph. viticola (Schwein. ex Fr.) Donk – Ruokolainen 2013 a, c; Syar peninsula, on deadwood of conifers, comp. 153–154, 176–178, 183, 17–18.08.2013, O. Manninen; environs of Velikaya Niva, spruce forest on dead spruce, 23.08.2012, A.V. Ruokolainen; Lipovitsy, Polya, north of Tambitsy, environs of Tolsty Navolok, Tambitsy, Tipinitsy, comp. 41, 71, 84 et al., A.V. Ruokolainen; stp. ** Phellodon niger (Fr. : Fr.) P. Karst. – Syar peninsula, on litter, 18.08.2013, O. Manninen; pine forest, comp. 13, on litter, 22.08.2013, A.V. Ruokolainen, PTZ; r. Ph. tomentosus (L.) Banker – Ruokolainen 2013 c; Syar peninsula, on litter, 19.08.2013, O. Manninen; Ladmozero, Vanchozero, pine forest, on litter, 24–25.08.2012, A.V. Ruokolainen; pine forest, comp. 13, on litter, 22.08.2013, A.V. Ruokolainen; stp. *, ** Phlebia centrifuga P. Karst. – Bondartseva et al. 1999; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest on fallen pine, 07.07.1997, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 177–178, 180, 183, 186, on spruce, 19.08.2013, O. Manninen; Tambitsy, Myrtillus spruce forest, on fallen spruce, 28.08.2013, A.V. Ruokolainen, PTZ; stp. Threat status: Fin – NT. Ph. livida (Pers. : Fr.) Bres. – Ruokolainen 2013 c; north of Podyelniki, pine forest, on fallen pine, 10.08.2010, A.V. Ruokolainen, PTZ; r. Ph. radiata Fr. – Ruokolainen 2013 c; Zharnikovo, mixed forest, on fallen Salix, A.V. Ruokolainen; stp. Ph. rufa (Pers. : Fr.) M.P. Christ. – Ruokolainen 2013 c; Kizhi Isl., LE; Kizhi Isl., on deadwood of Sorbus aucuparia, 16.07.1998, V.I. Krutov, PTZ; stp. Ph. segregata (Bourdot et Galzin) Parmasto – north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest, on old fallen spruce, 26.08.2013, A.V. Ruokolainen, PTZ; r. * Ph. serialis (Fr. : Fr.) Donk – northwest of the Vatnavolok village, Syar peninsula, comp. 183, on deadwood of conifers 18.08.2013; 27.06.2013, 23.08.2013, O. Manninen; r. Phlebiella sulphurea (Pers.) Ginns et M.N.L. Lefebvre – Ruokolainen 2013 c ; spruce, pine and mixed forest on deadwood of coniferous and deciduous trees; p. Phlebiopsis gigantea (Fr.) Jülich – Ruokolainen 2013 c; north of Podyelniki, south of Uzkaya Salma, Tambitsy, spruce forest on dead of spruce, 10.08.2010, 13.08.2010, 28.08.2013, A.V. Ruokolainen; stp. Physisporinus vitreus (Pers. : Fr.) P. Karst. – Lipovitsy, comp. 41–42, spruce forest, on deadwood of coniferous and deciduous trees, 23.08.2013, 24.08.2013, O. Manninen; r. Threat status: Len – 3. Piloderma bicolor (Peck) Jülich – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on deadwood of coniferous and deciduous trees, A.V. Ruokolainen; p. 252 Reports of the Finnish Environment Institute 40 | 2014 ** Piloporia sajanensis (Parmasto) Niemelä – Documentation ... 2013; Uzkaya Salma village, comp. 26, moist spruce forest, on fallen spruce on fruitbody of Trichaptum laricinum, 28.06.2013, O. Manninen, A.V. Kravchenko, PTZ; rr. Threat status: Kar – 3 (VU), Fin – EN. Piptoporus betulinus (Bull. : Fr.) P. Karst. – Ruokolainen 2013 b, c; Bol. Klim. Isl., environs of Lipovitsy, Podyelniki, Polya, Tambitsy, Tipinitsy, Uzkaya Salma, Velikaya Guba, Zharnikovo, pine, spruce and mixed forest,on dead birch, A.V. Ruokolainen; fq. Plicatura nivea (Sommerf. : Fr.) P. Karst. – Bondartseva et al. 1999; Ruokolainen 2013 c; southern part on Bol. Klim. Isl., spruce forest, on fallen Alnus incana, LE; stp. ** Polyporus badius (Pers.) Schwein. – Ruokolainen 2013 c; Bolshoi Lelikovskiy Isl., mixed forest, on fallen aspen, 09.08.2010, A.V. Markovsky, O. Turunen, PTZ; Zharnikovo, mixed forest, on fallen aspen, 05.08.2012, A.V. Ruokolainen, PTZ; Tipinitsy, spruce forest on fallen aspen, 27.08.2013, A.V. Ruokolainen, PTZ; stp. Threat status: Fin – VU. P. leptocephalus (Jacq.) Fr. [= P. varius (Pers.) Fr.] – Bondartseva et al. 1999; Ruokolainen 2013 c; Bolshoi Lelikovskiy Isl., mixed forest, on fallen aspen, 09.08.2010, A.V. Ruokolainen; Zharnikovo, mixed forest, on fallen aspen, 05.08.2012, A.V. Ruokolainen; p. P. melanopus (Pers.) Fr. – Ruokolainen 2013 c; Podyelniki, Zubovo, mixed forest, on old deadwood of birch, 03.08.2012, A.V. Ruokolainen, PTZ; stp. ** P. pseudobetulinus (Pilát) Thorn. Kotir. et Niemelä – Documentation ... 2013; on old aspen, rr. Threat status: Kar – 2 (EN), Fin – VU. P. squamosus (Huds.) Fr. – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Kizhi and Bolshoi Lelikovskiy Isl.s, north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest mixed forest, on deadwood of Salix caprea and aspen, 09.08.2010, 04.08.2012, 26.08.2013, A.V. Ruokolainen; stp. Postia alni Niemelä et Vampola – Ruokolainen 2013 b, c; Zharnikovo, Lipovitsy, comp. 41, spruce and mixed forest, on deadwood of Salix caprea, Sorbus aucuparia and alder, A.V. Ruokolainen; stp. P. caesia (Schrad. : Fr.) P. Karst. – Bondartseva et al. 2000; Ruokolainen 2013 c; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest on deadwood of spruce, 26.08.2013, A.V. Ruokolainen; stp. P. fragilis (Fr.) Jülich – Ruokolainen 2013 c; spruce forest on fallen pine, 05.08.2011, A.V. Ruokolainen, PTZ; Zharnikovo, pine forest, on dead pine, 02.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 186, 19.08.2013, O. Manninen; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest on fallen pine and spruce, 26.08.2013, A.V. Ruokolainen; Tambitsy, motley grass spruce forest, on fallen spruce, 28.08.2013, A.V. Ruokolainen; p. *, ** P. guttulata (Peck) Jülich – Ruokolainen 2013 b, c; south of the village of Uzkaya Salma, spruce forest, on dead spruce, 13.08.2010, A.V. Ruokolainen; Podyelniki, mixed fores,t on the roots of dry spruce, 03.08.2012, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 181, 186, on deadwood of spruce, 19.08.2013, O. Manninen; stp. Threat status: Fin – NT. *, ** P. lateritia Rennvall – Ruokolainen 2013 a; Syar peninsula, comp. 175, 180, 183, 186, on deadwood of conifers, 17–19.08.2013; 22.08.2013, O. Manninen; stp. Threat status: Fin – NT. ** P. leucomallella (Murrill) Jülich – Zharnikovo, pine forest,on dead pine, 02.08.2012, A.V. Ruokolainen; Syar peninsula, comp. 174, 182, 186, on dead of pine, 17–19.08.2013; 28.08.2013, O. Manninen; stp. Threat status: Len – 3. P. sericeomollis (Romell) Jülich – Syar peninsula, comp. 152, 183, spruce forest, on deadwood of conifers, 16.08.2013, 18.08.2013; 25.06.2013, 27.06.2013, 22.08.2013, O. Manninen; stp. P. stiptica (Pers. : Fr.) Jülich – Ruokolainen 2013 c; Lake Korbozero, Tipinitsy, mixed forest on deadwood of spruce, 27.08.2013, A.V. Ruokolainen; Tambitsy, motley grass spruce forest on deadwood of spruce, 28.08.2013, A.V. Ruokolainen; stp. Reports of the Finnish Environment Institute 40 | 2014 253 P. tephroleuca (Fr.) Jülich – Ruokolainen 2013 c; Bolshoi Lelikovskiy Isl., mixed forest on fallen aspen, 09.08.2010, A.V. Ruokolainen, PTZ; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest, on fallen birch and spruce, 26.08.2013, A.V. Ruokolainen; stp. ** P. undosa (Peck) Jülich [= Spongiporus undosus (Peck) A. David] – north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest on fallen pine and spruce, 26.08.2013, A.V. Ruokolainen, PTZ; r. Threat status: Len – 3. Pseudochaete tabacina (Sowerby) T. Wagner et M. Fisch. [= Hymenochaete tabacina (Sowerby) Lév.] – Ruokolainen 2013 c; Kizhi Isl., mixed forest on fallen aspen, 04.08.2012, A.V. Ruokolainen; Zharnikovo, mixed forest on fallen Sorbus aucuparia, 01.08.2012, A.V. Ruokolainen; stp. Pseudohydnum gelatinosum (Scop. : Fr.) P. Karst. – spruce forest, on fallen spruce, 27.08.2013, O. Manninen; r. * Pseudomerulius aureus (Fr.) Jülich – Syar peninsula, comp. 133, 180, 183, 16.08.2013, 18–19.08.2013, O. Manninen; r. ** Pycnoporellus alboluteus (Ellis et Everh.) Kotl. et Pouzar – south from Velikaya Guba village, at the western part of peninsula, comp. 9 of Kizhi forestry unit in old-growth spruce forests on fallen 24.08.2013, O. Manninen, T. Kuuluvainen; rr. Threat status: Fin – EN. *, ** P. fulgens (Fr.) Donk – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; Bol. Klim. Isl., spruce forest, on fallen spruce, 07.07.1997, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 153–154, 174, 176, 178, 180, 185–186, 17–19.08.2013, O. Manninen; Lipovitsy, north of Tambitsy, environs of Tolsty Navolok, Tambitsy, Kaskoselga, Lake Korbozero, Tipinitsy, comp. 41, 71, 132, 177 et al., spruce forest on old deadwood spruce, 21–23.08.2013, 26–28.08.2013, A.V. Ruokolainen; p. Threat status: Len – 3. Pycnoporus cinnabarinus (Jacq.) P. Karst. – Ruokolainen 2013 c; Zharnikovo, mixed forest, on deadwood of birch, 01.08.2012, A.V. Ruokolainen; stp. Radulodon erikssonii Ryvarden – Ruokolainen 2013 c; spruce forest on old deadwood aspen; rr. Threat status: Kar – 3 (VU), Fin – VU. ** Ramaria aurea (Schaeff.) Quél. – Ruokolainen 2013 c; pine forest, 22.08.2013; rr. ** R. eumorpha (P. Karst.) Corner [= R. invalii (Cotton et Wakef.] – Bondartseva et al. 1999; Kizhi Isl., LE; Podyelniki, spruce forest on litter, 03.08.2012, A.V. Ruokolainen, PTZ; r. R. suecica (Fr. : Fr.) Donk – Kizhi Isl., on litter, 04.08.2012, A.V. Ruokolainen, PTZ; r. Resinicium bicolor (Alb. et Schwein.) Parmasto – Ruokolainen 2013 c; Podyelniki, Zharnikovo, spruce and pine forest on fallen spruce; stp. R. furfuraceum (Bres.) Parmasto – Bondartseva et al. 1999; Bol. Klim. Isl., LE; Bol. Klim. Isl., spruce forest, on fallen spruce, 04.07.1997, A.V. Ruokolainen, PTZ; stp. *, ** Rhodonia placenta (Fr.) Niemelä, K.H. Larss. et Schigel – Ruokolainen 2013 a, c; south of the village of Uzkaya Salma, moist spruce forest, on fallen spruce, 13.08.2010, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 178, 180, 183, 186, 18–19.08.2013, O. Manninen; Lipovitsy, comp. 41, spruce forest on deadwood of spruce, 23.08.2013, A.V. Ruokolainen; stp. ** Rigidoporus crocatus (Pat.) Ryvarden – Bondartseva et al. 1999; Ruokolainen 2013 b, c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 03.07.1997, A.V. Ruokolainen, PTZ; Bol. Klim. Isl., spruce forest on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; Zharnikovo, birch forest on deadwood of deciduous trees, 05.08.2012, A.V. Ruokolainen, PTZ; Tambitsy, motley grass spruce forest, on fallen birch, 28.08.2013, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 180–181, 19.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Len – 3, Fin – EN. Sarcodon fennicus (P. Karst.) P. Karst. – Ruokolainen 2013 c; south of the village of Lambasruchei, Lake Onega shore, pine forest, on litter, 24.08.2012, A.V. Ruokolainen; by the lake in pine forest, comp. 13, on litter, 22.08.2013, A.V. Ruokolainen; r. 254 Reports of the Finnish Environment Institute 40 | 2014 S. glaucopus Maas Geest. et Nannf. – Syar peninsula, comp. 177, 180, 182, 185–186, pine forest on litter, 18–19.08.2013; 27.08.2013, O. Manninen; r. S. imbricatus (L. : Fr.) P. Karst. – north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest on litter, 26.08.2013, A.V. Ruokolainen; r. Schizopora paradoxa (Schrad. : Fr.) Donk – Ruokolainen 2013 c; on deadwood of aspen and birch; r. Scytinostroma galactinum (Fr.) Donk – Ruokolainen 2013 c; Zharnikovo, pine forest, on fallen birch, 02.08.2012, A.V. Ruokolainen, PTZ; r. Threat status: Fin – NT. S. odoratum (Fr.) Donk – Tambitsy, Myrtillus spruce forest, on fallen spruce, 28.08.2013, A.V. Ruokolainen, PTZ; r. ** Serpula himantioides (Fr. : Fr.) P. Karst. – 27.06.2013, O. Manninen; r. *, **, Sidera lenis (P. Karst.) Miettinen [= Skeletocutis lenis (P. Karst.) Niemelä] – Documentation ... 2013; Syar peninsula, comp. 153, 176–177, on fallen pine, 17–18.08.2013, O. Manninen; 22.08.2013 and 25.08.2013, O. Manninen; r. Threat status: Kar – 3 (VU), Len – 3, Fin – NT. Sistotrema raduloides (P. Karst.) Donk – Velikaya Niva, mixed forest, on fallen aspen, 23.08.2012, A.V. Ruokolainen, PTZ; r. Skeletocutis amorpha (Fr.) Kotl. et Pouzar – Ruokolainen 2013 b, c; Kizhi Isl., on pine wood, 04.08.2012, A.V. Ruokolainen; r. Sk. biguttulata (Romell) Niemelä – Ruokolainen 2013 c; north of Podyelniki, pine forest, on fallen pine, 11.08.2010, A.V. Ruokolainen, PTZ; r. Sk. brevispora Niemelä – Ruokolainen 2013 c; north of Podyelniki, spruce forest, on fallen spruce, 10.08.2010, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 153, 17.08.2013, O. Manninen; r. Threat status: Fin – NT. Sk. chrysella Niemelä – spruce forest, on fallen spruce, 23.08.2013, O. Manninen; rr. Threat status: Fin – NT. *, ** Sk. odora (Sacc.) Ginns – Ruokolainen 2013 a, c; south of the village of Uzkaya Salma, moist spruce forest, on fallen spruce, 13.08.2010, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 180–183, 18–19.08.2013, O. Manninen; r. Threat status: Fin – NT. Sk. papyracea A. David – Ruokolainen 2013 c; Zharnikovo, pine forest, on fallen pine, 02.08.2012, A.V. Ruokolainen, PTZ; Syar peninsula, comp. 177, 182, 18.08.2013; 25.06.2013, 24.08.2013, O. Manninen; r. *, ** Sk. stellae (Pilát) J. Keller – Syar peninsula, comp. 182–183, 18.08.2013; 27.06.2013, 23.08.2013, 26.08.2013, O. Manninen; r. Threat status: Fin – VU. Steccherinum imbriatum (Pers. : Fr.) J. Erikss. – Ruokolainen 2013 c; Tambitsy, spruce forest, on fallen aspen, 28.08.2013, A.V. Ruokolainen; stp. St. ochraceum (Pers.) Gray – Bondartseva et al. 1999; Bol. Klim. Isl., LE; Bol. Klim. Isl., on fallen deadwood of deciduous trees, 06.07.1997, A.V. Ruokolainen, PTZ; stp. Stereum hirsutum (Willd.) Pers. – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., spruce forest, on fallen birch, 06.07.1997, A.V. Ruokolainen, PTZ; Kizhi Isl., on deadwood of Sorbus aucuparia and alder, 16.07.1998, V.I. Krutov, PTZ; p. S. rugosum Pers. – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., on deadwood of alder, 16.07.1998, V.I. Krutov, PTZ; p. S. sanguinolentum (Alb. et Schwein.) Fr. – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; southern part on Bol. Klim. Isl., on fallen spruce, 06.07.1997, A.V. Ruokolainen, PTZ; stp. S. subtomentosum Pouzar – Bondartseva et al. 1999; Bol. Klim. Isl., LE; Bol. Klim. Isl., on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; stp. Thelephora terrestris Ehrh. – Ruokolainen 2013 c; Lipovitsy, comp. 41, spruce forest, on litter, A.V. Ruokolainen; stp. Reports of the Finnish Environment Institute 40 | 2014 255 Tomentella bryophila (Peck) M.J. Larsen – Lipovitsy, spruce forest, on fallen aspen, 21.08.2013, A.V. Ruokolainen, PTZ; stp. ** T. crinalis (Fr.) M.J. Larsen – Ruokolainen 2013 a, c; south of Uzkaya Salma, spruce forest with aspen, on old fallen aspen, 13.08.2010, A.V. Ruokolainen, PTZ; north of Tambitsy, environs of Tolsty Navolok, comp. 71, spruce forest, on old fallen aspen, 26.08.2013, A.V. Ruokolainen, PTZ; Lake Korbozero, Tipinitsy, mixed forest, on old fallen aspen, 27.08.2013, A.V. Ruokolainen, PTZ; Threat status: Kar – 3 (NT); r. T. lateritia Pat. – Ruokolainen 2013 a, c; mixed forest, on fallen aspen; stp. T. stuposa (Link) Stalpers – Ruokolainen 2013 c; Velikaya Niva, motley grass birch forest, 23.08.2012, A.V. Ruokolainen, PTZ; r. T. sublilacina (Ellis et Holw.) Wakef. – Ruokolainen 2013 c; Zharnikovo, mixed forest on deadwood of deciduous trees, 02.08.2012, A.V. Ruokolainen, PTZ; r. T. terrestris (Berk. et Broome) M.J. Larsen – Ruokolainen 2013 c; north of Podyelniki, spruce forest, near fallen aspen, 11.08.2010, A.V. Ruokolainen, PTZ; r. Trametes hirsuta (Wulfen) Lloyd – Bondartseva et al. 1999; Ruokolainen 2013 c; Kizhi Isl., on deadwood of Sorbus aucuparia, 07.08.1998, V.I. Krutov, PTZ; Bol. Klim. Isl., Zharnikovo, mixed forest, on fallen Sorbus aucuparia and birch, 01.08.2012, A.V. Ruokolainen; p. T. ochracea (Pers.) Gilb. et Ryvarden – Bondartseva et al. 1999; Ruokolainen 2013 c; Bol. Klim. Isl., LE; Bol. Klim. Isl., spruce forest, on fallen aspen, 06.07.1997, A.V. Ruokolainen, PTZ; Zharnikovo, mixed forest on fallen aspen and birch, 01.08.2012, A.V. Ruokolainen; fq. T. pubescens (Schumach.) Pilát – Ruokolainen 2013 c; Zharnikovo, mixed forest, on fallen birch and alder, 01.08.2012, A.V. Ruokolainen; p. ** T. suaveolens (L. : Fr.) Fr. – the river Padma, on deadwood of Salix caprea, 04.09.2005, A.V. Ruokolainen, PTZ; 26.06.2013, 27.08.2013, 28.08.2013, O. Manninen; r. Threat status: Len – 3, Fin – NT. T. trogii Berk – Syar peninsula, comp. 153, 17.08.2013; 27-28.08.2013, O. Manninen; r. Threat status: Fin – VU. Trecispora hymenocystis (Berk. et Broome) K.H. Larss. – 27.08.2013, O. Manninen; r. T. mollusca (Pers. : Fr.) Liberta – 25.08.2013 and 27.08.2013, O. Manninen; r. Trichaptum abietinum (Dicks.) Ryvarden – Bondartseva et al. 1999; in the southern part on Bol. Klim. Isl., spruce forest, on fallen spruce, 05.07.1997, A.V. Ruokolainen, PTZ; fq. T. fuscoviolaceum (Ehrenb.) Ryvarden – Ruokolainen 2013 c; the river Padma, on fallen pine, 04.09.2005, A.V. Ruokolainen, PTZ; stp. T. laricinum (P. Karst.) Ryvarden – Ruokolainen 2013 c; Syar peninsula, comp. 181, 19.08.2013, O. Manninen; rr. Threat status: Fin – NT. T. pargamenum (Fr.) G. Cunn. – Bondartseva et al. 1999; Syar peninsula, comp. 186, 19.08.2013; Polya, mixed, pine and spruce forest, on fallen birch, 22.08.2013, 24.08.2013, A.V. Ruokolainen; 27.08.2013, O. Manninen; stp. Threat status: Fin – NT. Tubulicrinis calothrix (Pat.) Donk – Bondartseva et al. 1999; Bol. Klim. Isl., LE; Bol. Klim. Isl., spruce forest on fallen pine, 06.07.1997, A.V. Ruokolainen, PTZ; pine forest, comp. 13, on fallen pine, 22.08.2013, A.V. Ruokolainen, PTZ; stp. T. effugiens (Bourdot et Galzin) Liberta – Bondartseva et al. 1999; Bol. Klim. Isl., LE; r. Veluticeps abietina (Pers. : Fr.) Hjortstam et Tellería – Ruokolainen 2013 a, c; near Lake Nizhnee Pigmosero, 22.08.2012; Polya, spruce forest, on dead spruce, 25.08.2012, A.V. Ruokolainen; stp. 256 Reports of the Finnish Environment Institute 40 | 2014 3.6 Insect fauna of Zaonezhye Peninsula and adjacent islands Jevgeni Jakovlev*#, Alexei Polevoi** and Andrei Humala** * The Finnish Environment Institute (SYKE) Mechelininkatu 34a. P.O. Box 140, FIN-00251 Helsinki, Finland ** Forest Research Institute of Karelian Research Center of Russian Academy of Sciences 11 Pushkinskaya St., 185910 Petrozavodsk, Karelia, Russia # - Corresponding author E-mail: jevgeni.jakovlev@ymparisto.i Introduction Zaonezhye Peninsula is situated on the northwestern coast of Lake Onega, in the eastern part of the biogeographical province of Karelia onegensis. In the east its shores are washed by Zaonezhye Gulf, while in the west the peninsula is bordered by Lizhma Bay and Bolshoye Onego Gulf of Lake Onega. Zaonezhye Peninsula lies on the basement rocks of Fennoscandia and characterized by underlying basic limestone and carbonate rocks. This, together with highly fertile soils, has contributed to the diversity of habitats and plant species on Zaonezhye Peninsula. For this reason, it is considered a separate vegetation region (Ramenskaya 1983). The same is true of the insect fauna, which has interested entomologists for a long time. History of entomological studies on Zaonezhye Peninsula Entomological studies on Zaonezhye Peninsula began in the second half of the 19 th century. At that time it was one of the most developed agricultural areas in Karelia with good connection to Petrozavodsk by water transport. The earliest records from this area date back to 1859–1899 when the apothecary of Alexandrovsky plant (Petrozavodsk), Alexander Günther, collected insects mainly around Petrozavodsk, covering eastern parts of the provinces Kon and Kol (Pekkarinen & Huldén 1995). The collections of Alexander Günther are not available in Russia. However, he maintained contact with Finnish entomologists and published species lists of Lepidoptera (Günther 1868, 1896 a) and Coleoptera (Günther 1896 b). A large part of his collections have been identiied by Finnish entomologists and subsequently published, e.g. Kaisila (1947) for Lepidoptera, and Poppius (1899) for Coleoptera. Most of the samples are stored in the Zoological Museum of Helsinki. Reports of the Finnish Environment Institute 40 | 2014 257 The irst detailed study of beetles (Coleoptera) around Lake Onega was conducted by the famous Finnish entomologist Bertil Robert Poppius (Poppius 1899). Between June and August 1896, he visited several places on the shores of the lake, including Zaonezhye Peninsula inland areas (locations Dianova Gora, Kosmozero, Unitsa), villages on its eastern and southern shores, Kuzaranda, Shun’ga (Schungu in Poppius’ transcription), Tolvyua (Tolvoja), Velikaya Guba (Velikaja-guba), and the Kizhi archipelago, islands Bolshoi Klimenetsky, Kizhi (Kischi), and Southern Oleny (Yu. Oleny in the species list). Several species are recorded as ‘Saoneshje-halfön’ without indication of certan locality As a result, more than 400 of presently recognized beetle species were reported for the irst time from Zaonezhye area. The next records of insect from Zaonezhye Peninsula were by Finnish entomologists during the Second World War (Kaisila 1947, Valle 1952, Kontuniemi 1965, etc.). After the war, the insect fauna of the area was not studied until the middle of the 1990s when entomologists from the Forest research institute of the Karelian Research Center of the Russian Academy of Sciences started inventories of the Kizhi archipelago, including the islands of Kizhi, Bolshoi Klimenetsky, Volkostrov and Yuzhnyi Oleniy (Jakovlev et al. 1999). Later, faunistic studies have been continued in the same areas as well as on the southern end of the peninsula, adjacent to the Kizhi archipelago, (e.g. Podyelniki and Oyatevschina). Additional materials of Lepidoptera have been collected by Dr. Vyacheslav Gorbach (Petrozavodsk State University) and Finnish entomologists around the village of Sennaya Guba (Gorbach & Saarinen 2002; Gorbach & Kabanen 2010). All these areas are a part of the Kizhi nature reserve (zakaznik). As a result, nearly 2 000 insect species have been recorded from the entire Kizhi archipelago (Humala & Polevoi 2012). Areas north of the Kizhi Nature Reserve remained unstudied from the time of Poppius until 2012 when approximately 1 000 insect species were recorded in the northern part of the peninsula, including the villages of Kosmozero, Myagrozero, Shun’ga and Turastamozero (Polevoi & Humala 2013). These areas are proposed to be included in the planned Zaonezhye landscape reserve (zakaznik). The latest samples were collected outside of the planned landscape reserve in 2013 during the joint Finnish-Russian expedition to the southern lowlands of Zaonezhye Peninsula (Kizhi forestry unit, or lesnichestvo, and a part of the Velikaya Niva forestry unit, compartments (quartals) 46-47, 69-71, 79-83, 97-100, 102-104, 114-117, 123-124,140143, 158-162). Also, Karelian entomologists collected samples during a short visit to the coastal areas of Zaonezhye Peninsula and adjacent islands in 2004, and northern part of the Kizhi Nature Reserve in 2014 (Eglov Island and its vicinities). Study area and methods Materials were collected between 1994 and 2013 in the Medvezhiegorsk and Kondopoga municipalities of the Republic of Karelia, within the biogeographical province of Karelia onegensis. Our samples originated from approximately 74 sites (Fig. 1), which have been grouped into 40 generalised locations in the species list. 258 Reports of the Finnish Environment Institute 40 | 2014 Fig. 1. Study sites in Zaonezhye Peninsula: 1–Vikshezero, 2–Unitsa, 3–Dianova Gora, 4–Nikonova Guba, 5–Shun’ga, 6–Paleostrov Isl., 7–Isl. Kainos and Vavlok, 8–Turastamozero, 9–Kazhma, 10– Verkhnee and Nizhnee Myagrozero, 11–Tolvuya, 12–Lizhma, 13–Kosmozero, 14–Velikaya Niva, 15–Kuzaranda, 16–Tambitsy, 17–Polya, 18–Velikaya Guba, 19–Vegoruksy, 20–Tipinitsy, 21–Uzkaya Salma, 22–Lipovitsy, 23–Khvost Isl., 24–Isl. Eglov and Rogachev, 25–Isl. Shunevskiy, 26–Volkostrov Isl., 27–Pod’elniki, 28–Kizhi Isl., 29–Kurgenitsy, 30–Yuzhnyi Olen Isl., 31–Vorobyi, 32–Oyatevschina, 33–Kopanets Lake, 34–Vertilovo, 35–Myal’ Isl. and Lelikovo, 36–Sennaya Guba, 37–Voinavolok, 38–Isl. Ernitskiy, Lyudskoy and Kuivakhda, 39–Bolshoy Lelikovskiy Isl., 40–Klimenitsy. We used a variety of collecting methods in order to capture different insect groups: sweep netting, portable Malaise traps (Jaschoff & Didham 2002) (Fig 2), yellow pan traps (Masner 1976), polypore traps (Kaila 1993) as well as light trapping with an ultraviolet lamp and a white sheet. In addition, we collected insects on dead wood, fungi and lowers (Fig. 3). In 2013, three Malaise traps were placed in the Kizhi forestry unit (surroundings of the villages Uzkaya Salma and Lipovitsy) and Velikaya Niva forestry unit (near the village Polya) for the period between 26th June and 25th August. Easily distinguishable species were identiied by appearance, or photographed. We concentrated on three large insect orders: Coleoptera, Hymenoptera and Diptera. In the order Lepidoptera we recorded mostly representatives of the suborder Rhopalocera. Some insect groups were excluded due to problems in identiication. Other groups have limited samples due to selective methods used. Original materials are stored at the Forest research institute of Karelian Research Center of the Russian Academy of Sciences (Petrozavodsk), and in Finnish Environment Institute (Helsinki). There are also old insect collections from Zaonezhye area which are now stored in the Zoological Museum of the University of Helsinki (Finland). We could not manage checking of all these materials, but listed only published records. Reports of the Finnish Environment Institute 40 | 2014 259 Fig. 2. Malaise trap in spruce-dominated unmanaged forest with great proportion of aspen. NE of the abandoned Lipovitsy village (Photo Jevgeni Jakovlev). Fig. 3. Handpicking from thin dead branches of windfallen aspen trees of a dark black color – typical larval microhabitat of a rare beetle species, Leiopus punctulatus (Photo Andrei Humala). Results In total, approximately 2453 insect species were recorded from Zaonezhye Peninsula and adjacent archipelagos. Of these: Ephemeroptera–1, Odonata– 27, Orthoptera–14, Blattoptera–2, Mecoptera–2, Raphidioptera–1, Neuroptera–3, Hemiptera–61, Coleoptera–583, Lepidoptera–218, Hymenoptera– 428, and Diptera–1113 species. The characteristics of insect fauna are determined not only by the diversity of natural habitats, but also by the history of landuse on Zaonezhye Peninsula. In addition 260 Reports of the Finnish Environment Institute 40 | 2014 to species typical of old-growth forests, there are species associated with secondary forests with a large amount of dead wood of deciduous trees, as well as meadow insect fauna. Originally the area was covered with high quality coniferous forests, growing in conditions close to optimal. At present, intact coniferous forests are preserved only in paludiied areas and on steep, rocky slopes. The rest of the forests have been affected by selective cuttings. Especially close to the villages, forests have grown naturally on abandoned ields and hay meadows. According to forest inventory data from 1999 (Gromtsev & Krutov 2000), pine- and spruce-dominated forests occupy nearly 60 percent of the forest cover in approximately equal proportions. The remaining area is covered by forests dominated by birch (ca. 30%), aspen (5%) or grey alder (6 %). The studied forests in the lowland parts of Zaonezhye Peninsula can be divided roughly into three classes. These are (1) high quality primeval forests with negligible human impact, (2) forest of high conservation potential, rapidly restoring natural values after earlier human use, and (3) successional forests, which are developing after the abandonment of ields and forest pastures (see Kuuluvainen and Tikkanen, Reports of the Finnish Environment Institute 40 | 2014). Human impact on the study area has always been signiicant. During our sampling trips in 2012 (northern parts of Zaonezhye Peninsula) and 2013 (southern parts), we found only a few sites of high quality spruce dominated forests and mire-spruce stands that could be characterized as near primeval forest. At least, two threatened beetle species, Pytho kolwensis and Monochamus urussovi seem to be fairly well-preserved here. Forests of the second class which has been used to some extent in the past for selective cutting, slash-and-burn cultivation, etc., and then developed naturally during dozens of years occupy large areas in Zaonezhye Peninsula and in some islands, e.g. Bolshoy Klimenetsky. Although of secondary origin, these forests are rich in coarse woody debris and, therefore, host a series of saproxylic beetle (Coleoptera) species that are typical for intact boreal forests, e.g. Ceruchus chrysomelinus (Lucanidae), Phaenops cyanea, Chrysobothris chrysostigma (Buprestidae), Phryganophilus ruicollis (Melandryidae), Nivellia sanguinosa, Pedostrangalia pubescens and Leptura nigripes (Cerambycidae) as well as their parasitoids, e.g. ichneumonoid wasps Arotes albicinctus and Coleocentrus exareolatus (Hymenoptera). Many of these species have declined dramatically in Western Europe, many are redlisted. Pine-dominated stands usually contain old trees bearing signs of resin extraction which was carried out some tens years ago, however, neither signs of insect epidemics, nor symptoms of forest decline due to insect pests have been observed. The third class of forests - mixed deciduous stands with alder, birch and aspen occupy abandoned ields, slash-and-burn sites and pastures near former villages. In many sites, there is plenty of dead wood of aspen where we found several internationally rare insect species, including lies Symmerus nobilis and Xylomya czekanovskii (Diptera), beetles Hylochares cruentatus, Rhizophagus pincticollis, and Leiopus punctulatus (Coleoptera). In Finland these species are highly threatened, ranging from vulnerable (VU) to regionally extinct (RE). In Karelia they have been recorded only in southern part from limited areas like Kivach Nature Reserve (Ivanter & Kuznetsov 2007). In Zaonezhye they seem to be well-preserved in secondary forests on fertile soils. Grasslands are located mainly in the southern and eastern lowlands where they have been intensively used as hay meadows and pastures. Relatively large areas have been covered with arable land. At present, most of these areas are abandoned, gradually transforming into young secondary deciduous forest. We found and observed only a few intact grasslands on the islands of the Kizhi archipelago and in the eastern shore of Zaonezhye Peninsula. Wet grasslands can be found in the narrow bays along Reports of the Finnish Environment Institute 40 | 2014 261 the shoreline. Formerly, local population used these grasslands for haymaking, whereas presently they are occupied with a combination of mire and meadow vegetation (Kuznetsov 1993). Typical grassland species include Psophus stridulus (Orthoptera) and several species of butterlies, e.g. internationally rare Parnassius mnemosyne and Zygaena osterodensis, which are considered very rare and threatened both in Karelia and the entire Europe. Very interesting is a recent inding of a longhorn beetle species, Aromia moschata at the edge of abandoned ield on Bolshoy Klimenetsky Island. This species develops primarily in willows. Conclusions Zaonezhye Peninsula was one of the most highly developed rural regions in Karelia during the extended period. Long history of traditional agriculture and its general decline in the recent years led to formation of huge variety of habitats in the area including open meadows, secondary stands on abandoned ields and remnants of natural coniferous forests. Such variety together with a set of favorable abiotic conditions provide successful existence of various insect group: saproxylic species, requiring dead wood of certain tree species at different stages of decay; herbivores, trophically associated with certain plant species; aquatic species, which require special water conditions, etc. Many of such species nowadays become very rare or even extinct in other parts of Karelia as well as in whole Fennoscandia. Our indings undoubtedly indicate the uniqueness of Zaonezhye Peninsula territory and its signiicant value in terms of insects’ biodiversity conservation. It is a strong ecological argument to establish protected areas for conservation of the habitats of saproxylic insects and insects conined to intact grasslands which were revealed during the entomological studies. Zaonezhye Peninsula and adjacent islands is an exceptional area in Karelia for which there is a considerable amount of old records of insects made before vast-scale mechanical forest logging was started in Karelia. It allows tracing dynamics of distribution of the threatened insect species in forests and grasslands. The twenty-year studies in 1994-2014, showed that saproxylic insects associated with aspen are well preserved in many places. Also, several threatened Coleoptera species associated with spruce and birch have been rediscovered in suitable habitats. These are, for instance, Pytho kolwensis, Phryganophillys ruicollis, Ceruchus chrysomelinus which are strongly declined throughout Northern Europe. All these species have a special value for nature conservation. On the other hand, we have failed to rediscover many Coleoptera species associated with pine, e.g. a bark beetle Ips sexdentatus which was recorded from the area by Poppius (1899) more than hundred years ago. This species is possibly extinct in Southern Karelia, and can be found only in places of stored barked pine wood (Jakovlev et al. 2000). A buprestid species, Phaenops cyanea which also seems to be declined in southern part of Karelia has been found in the timber store. Among the insects dependent on traditional agriculture landcapes, several species were evidently strongly declined. For instance, we have not found a dung beetle Onthophagus nuchicornis recorded by Poppius (1899). At the same time, several threatened insect inhabiting dry meadows still exist, inspite of the declining of agriculture and overgrowth of their natural habitats. The most interesting inding is the rattle grasshopper, Psophus stridulus which was mentiond by old authors (Ozeretskovsky 1989) as a common species in Southern Karelia. At present, P. stridulus population in Kizhi archipelago seems to be the only one in Russian Karelia. To maintain it, the special measures aimed to restore dry meadows in Zaonezhye are in urgent need. In Finland, the rattle grasshopper is considered as rapidly-declining, endangered species inhabit primarily dry and sunny sandy areas and eskers, 262 Reports of the Finnish Environment Institute 40 | 2014 and gradually moving from its natural biotopes to manmade environments, like the embankments of railroad tracks and roadside verges (Intke & Piirainen 2014). There are ecological groups, e.g. aquatic insects, and many taxonomic groups of insects which were not studied in the area yet. Further research is needed for these groups, as well as for localities which are not covered for entomological research in Zaonezhye Peninsula and adjacent islands. Acknowledgements We thank Mrs. N.N. Kutenkova (Kivach Nature Reserve) for the help in identifying Lepidoptera species, Mr. Juho Paukkunen (Helsinki Zoological Museum, Finland) for the help with identifying of some aculeates (Hymenoptera) and results of his trip in 2010 to Kizhi Nature Reserve. The study was partly supported in 1994–2014 by the Russian Foundation for Basic Research (grant No 13-04-98821), the Presidium of the Russian Academy of Sciences (Prorgamm of Fundamental Research Living Nature: Modern State and Development Problems), Kizhi Nature Reserve (State Zakaznik Kizhsky), and the project Barents Protected Area Network (BPAN) leaded by the Finnish Environment Institute. Annotated list of the insect species included in Red Data Book of the Republic of Karelia (Ivanter & Kuznetsov 2007) and other noteworthy insect species The threat status is given according to the following sources: Karelia (Kar) – Ivanter & Kuznetsov (2007), Leningrad Region (Len) – Noskov (2002), Finland (Fin) – Rassi et al. (2010). Species reported for the irst time in Karelia are marked with asterisks. ODONATA Aeshnidae Aeshna viridis Eversmann, 1836 Material. 5 km N of Nikonova Guba, 1 ♂, under an electric power line, 22/8/2012 (A.Humala). There are old records of the species from northern Ladoga (Valle 1927; Tiensuu 1933). There are also unconirmed indings in the Kondopoga region (S.Uzenbaev, pers. comm.). Larvae of the species develop in thickets of Water soldiers (Stratiotes aloides L.). Due to habitat speciication, the species is scarse and under threat over much of its range (Dijkstra, Lewington, 2006). Threat status: Kar – 4 (DD); Len– 3 (VU). Libellulidae Libellula fulva Müller, 1764 Material. 5 km S of Turastamozero, 1♂, 1♀, on the shore of a small river, 21/7/2012 (A.Polevoi). This is the irst modern record of the species in Karelia. It was previously known only from northern Ladoga (Valle 1927; Tiensuu 1933). The species requires a speciic combination of water quality and habitat structure and is therefore only locally common in Europe (Dijkstra, Lewington 2006). Threat status: Kar – 4 (DD). ORTHOPTERA Acrididae Psophus stridulus (Linnaeus, 1758) (Fig. 4) Material. Bolshoi Klimenetsky Island, Vorob’i, numerous specimens, 18-22/8/2008 (Polevoi, Humala). Reports of the Finnish Environment Institute 40 | 2014 263 An outstanding representative of the order Orthoptera. In adults, the hind wings have a bright red colour, and the males emit a characteristic chatter during light. The species was irst recorded in Karelia, near Konchezero, at the end of the 18th century (Ozeretskovsky 1989). Previously the species seems to have been distributed throughout the southern part of Karelia up to the border of the middle taiga (Albrecht 1979). However, it had not been observed here for over 50 years, and was considered as regionally extinct (Ivanter & Kuznetsov 1995) until it has been rediscovered in Kizhi archipelago. The cause of decline is the overgrowth of its natural habitats. Threat status: Kar – 1(CR); Len – 3 (VU); Fin – VU. Fig. 4. Psophus stridulus (Photo Alexei Polevoi). COLEOPTERA Scarabaeidae Onthophagus nuchicornis (Linnaeus, 1758) The species was recorded from Kizhi Island by Poppius in 1896 (Poppius 1899). It has been formerly distributed in southern parts of Fennoscandia. At present, the species is probably extinct in Russian Karelia, as well as in Finland, where the most recent record are from the years 1946 and 1955, respectively (Muona et al. 1998). In Zaonezhye, well-developed traditional husbandry provided the optimal habitats for O. nuchicornis. However, environmental changes caused by decline of the agricultural ecosystems are suggested as a reason for the decline in the occurrence of this vulnerable species with dung-living larvae. Threat status: Kar – 0 (RE); Fin – RE. Lucanidae Ceruchus chrysomelinus (Hochenwarth, 1785) Material: larvae inside spruce logs: Bolshoi Klimenetsky Island, 18.07.2000 (Jakovlev), Polya, 25/8/2013 (Polevoi). This is typical inhabitant of old-growth forest with big amount of coarse woody debris. Larvae live in well-decayed wood with brown rot fungi. They can colonize different tree species. In Karelia, most records are from spruce. Considered as threatened in all countries on Northern Europe, the threat factor is reduction of the area of old-growth forests. In Karelia has been recorded only from southern part. Common 264 Reports of the Finnish Environment Institute 40 | 2014 in Kivach Nature Reserve (Jakovlev et al. 1986). Threat status: Kar – 3 (Vu); Fin –EN. The risk of extinction of this species is assigned also in the global level – category NT in the global Red List (IUCN 2014). Pythidae Pytho kolwensis Sahlberg, 1833 (Fig. 5) Material: larvae under bark of spruce logs: Bolshoi Klimenetsky Island, July 2000, Lipovitsy, 25/6/2013 (Jakovlev); Polya, 25/8/2013 (Humala), Tambitsy, 27/8/2013 (Polevoi). A species with a narrow ecological specialization. Larvae live under the bark of fallen, old spruce trees, usually in wet places. Sharply declined in Northern Europe due to forest management and drainage of spruce-mire moist forest. It is possible that P. kolwensis became extinct in large parts of southern Finland as early as the 1800s or even earlier, in regions where slash and burn cultivation was intensive at the time (Siitonen & Saaristo 2000). In Zaonezhye peninsula it survived in remains of old-growth forests. Generally, the species is widespread in Karelia, but recorded only in areas of old-grown forests with a lot of dead wood (Jakovlev et al. 2000). Threat status: Kar – 3 (NT); Len – 2 (EN); Fin – EN. Fig. 5. Larva of Pytho kolwensis (Photo Andrei Humala). Eucnemidae Hylochares populi Brüstle & Muona1 Material. Polya, 2 specimens under the bark of an old, dead aspen tree, 26/6/2013 (Humala); Tambitsy, cavities and holes on aspen trunks, 26/8/2013 (Polevoi). This species develops in large, dead aspens in old-growth forests. In Karelia, there are only two known populations in the Kondopoga and Pudozh municipalities (Ivanter & Kuznetsov 2007, Jakovlev 2009). There are also old records from the Olonets municipality (Palmén 1946). Threat status: Kar – 3(VU); Fin – EN. Buprestidae Chrysobothris chrysostigma (Linnaeus, 1758) (Fig. 3) Material. Nizhnee Myagrozero, 1 specimen on a spruce trunk near the road, 22/7/2012 (Polevoi); Vegoruksy, 1 specimen, 25/6/2013 (Kravchenko), 2 specimens on spruce 1 AММШrНТЧР ЭШ BrüsЭХО КЧН MЮШЧК (2009), КХХ KКrОХТКЧ sЩОМТЦОЧs ПШЮЧН ШЧ КsЩОЧs sСШЮХН ЛО МШЧsТНОrОН H.populi. H.cruentatus (GвХХОЧСКХ) НОЯОХШЩs ШЧ аТХХШаs КЧН ЭШ НКЭО Тs ШЧХв ФЧШаЧ ПrШЦ sШЮЭСОrЧ FТЧХКЧН. HШаОЯОr, sШЦО КЮЭСШrs qЮОsЭТШЧ ЭСО ЯКХТНТЭв sЭКЭЮs ШП H.populi (Kovalev 2014). Reports of the Finnish Environment Institute 40 | 2014 265 trunks near the road, 27/6/2013 (Polevoi, Humala); 7 km south of Kosmozero, 1 specimen on a dead spruce at the edge of a clear-cut, 26/6/2013 (Polevoi). This species develops under the bark of dying or dead conifers. In Karelia, the species is conined to old-growth forests. However, it is probably more widely distributed than previously thought. There are a few known old and modern records from southern Karelia (Palmén 1946; Humala & Polevoi 2009). Threat status: Kar – 3 (NT). Phaenops cyanea (Fabricius, 1775) (Fig. 6) Material. Vegoruksy, several specimens on pine trunks near the road, 27/6/2013 (Polevoi, Humala). This species develops inside and under the bark of dead or dying pines, especially of those damaged by ire. In the past it was a common species in southern Karelia (Palmén 1946). The latest records from the vicinities of Petrozavodsk date back to 1954 (Yakovlev et al. 1986). Threat status: Kar – 3 (VU). Nitidulidae Cyllodes ater (Herbst, 1792) Material. Bolshoi Klimenetsky Island 7/06/1995, 17/07/2000 (Jakovlev), Zharnikovo, 12/07/1999 (Polevoi), Lipovitsy 25/6/2013 (Humala), on the fruiting bodies of wood-growing fungi Fomes fomentarius, Piptoporus betulinus and Pleurotus pulmonarius. This species is relatively common in Karelia. It is associated with forests with great amount of dead aspens. Threat status: Kar – 3 (LC); Fin – NT. Monotomidae Rhizophagus puncticollis Sahlberg, 1837 Material. Mixed spruce dominated forest with great proportion of aspen, Kopanets Lake shore. 1 specimen (imago), under bark of dead aspen trunk, 15/07/1999 (Polevoi). This species has been drastically declining in Northern Europe due to eradication of aspen. In Karelia recorded only from southern part: Kivach Strict Nature Reserve, Kotkozero (Olonets municipality) and Gumbaritsa (SE shore of Ladoga Lake) (Siitonen et al. 1996). Threat status: Kar – 3 (NT); Fin – RE. Melandryidae Phryganophilus ruicollis (Fabricus, 1798) Material. Bolshoi Klimenetsky Island, 1 specimen have been collected by window trap, 5-10.06.1995 (Jakovlev). This species develops feeding on fungal mycelia in dead wood rotten by Fomes fomentarius and other white rot fungi. In Northern Europe, most records are from fungus infected trunks of spruce and birch, in Sweden − also from oak (Ehnsröm & Axelsson 2002), and it has been suggested to be favoured by forest ires (Lundberg 1993). Estimated as very rare species in all countries from where it has been recorded. There are only ca. 20 records from Northern Europe, of these three records from southern Karelia: Kivach Strict Nature Reserve, Kizhi Nature Reserve (Ivanter & Kuznetsov 2007) and vicinity of Matrossy village (Kolström & Leinonen 2000) In Karelia, Finland, Sweden and Norway, P.ruicollis has been assessed as threatened species based on a small area of occupancy and a small distribution area due to the reduction in the area of natural forests. Threat status: Kar 2(EN); FIN – VU. 266 Reports of the Finnish Environment Institute 40 | 2014 Fig. 6. Phaenops cyanea (Photo Andrei Humala). Cerambycidae Nivellia sanguinosa (Gyllenhal, 1827) Material. Vikshezero, 1 ♀, on lowers at the edge of an abandoned hayield, 28/6/2007 (Humala). This is a rare species developing in coarse woody debris (thin trunks, stumps and branches), most often – Alnus spp, also birch and some other deciduous trees like Prunus and Corylus (Ehnström & Axelsson 2002). It is known from only a few records in southern Karelia (Jakovlev et al., 1986; Polevoi et al. 2005). Threat status: Kar – 4 (DD); Fin – VU. Pedostrangalia pubescens (Fabricius, 1787) Material. Turastamozero, 1 ♀, on lowers, 24/7/2012 (Polevoi). The species develops in dead wood of pine (also on hardwoods in southern parts of its range). Its earlier records in Karelia are from northern Ladoga (Humala & Polevoi 2011). Threat status: Kar – 4 (DD); Fin – VU. Leptura nigripes DeGeer, 1775 (Fig. 7) Material. Turastamozero, 1 specimen, 20/7/2012 (Humala, Polevoi); Vegoruksy, 1 specimen, 27/6/2013 (Humala). On lowers at the edges of hayields. Larvae develop in dead wood of deciduous trees. The species is found in southern Karelia, although it is relatively rare across its range (Jakovlev et al. 1986). Threat status: Kar – 4 (DD); Fin – EN. Reports of the Finnish Environment Institute 40 | 2014 267 Fig. 7. Leptura nigripes (Photo Andrei Humala). Leiopus punctulatus (Paykull, 1800) Material. Polya, 1 specimen, on a branch of a fallen aspen, 25/8/2013 (Jakovlev). Larvae of this species feed subcortically in relatively thin dead branches of windfallen aspen trees of a dark black color caused by a fungus Encoelia fascicularis (Ascomycota). This species is probably extinct in Finland, and has been viewed as extinct since 1902 also in Sweden, but had been recently rediscovered (Lundberg & Martin 1991). To date only two locations were known in Karelia: Kivach Nature Reserve (Jaakko Mattila leg., 2002, unpubl.) and Pudozh municipality (Humala & Polevoi 2009). Threat status: Fin – RE. Phytoecia cylindrica (Linnaeus, 1758) Material. Vikshezero, 1 ♀, on lowers at the edge of an abandoned hayield, 28/6/2007 (Polevoi); Vegoruksy, 1 ♀, 25/6/2013 (Polevoi). The species develops in the stems of Apiaceae and Asteraceae. There are only a few, mostly old, records from Karelia (Silfverberg & Biström, 1981, Polevoi et al. 2005). Threat status: Kar – 4 (DD). Curculionidae Ips sexdentatus (Börner 1776), or six-toothed bark beetle. Recorded from Kosmozero by Poppius (Poppius 1899) as Tomicus stenographus Duffschmidt. This is the largest species of scolytids in boreal forest zone. Larvae develop under thick bark of recently fallen old pines. Generally, six-toothed bark beetle is known as forest pest which is able to attack healthy trees of Scotch pine under outbreak conditions. However, during last century it has become extremely rare in Northern Europe. In Russian Karelia it has been recorded only in fallen logs in places of long-time storage (Jakovlev et al. 2000). Threat status: Fin – VU. 268 Reports of the Finnish Environment Institute 40 | 2014 LEPIDOPTERA Papilionidae Parnassius mnemosyne (Linnaeus, 1758) (Fig. 8) Material. Velikaya Niva, numerous specimens along the road, 10/6/2000 (Humala, Polevoi). The distribution of Clouded Apollo is limited to southern Karelia (Bolotov et al. 2012). It has irst been reported from Zaonezhye (Velikaya Niva and Bolshoy Klimenetsky Island) in the middle of the 20th century (Kaisila 1947). Recently large but scattered populations have been found on the Kizhi skerries (Jakovlev et al. 1999; Gorbach & Kabanen 2010). However, its distribution on the mainland of Zaonezhye Peninsula needs to be clariied. The species is also recorded from southeastern parts of Karelia and Ladoga area (Humala 1998; Humala & Polevoi 2009; Gorbach & Reznichenko 2009). Threat status: Russia – 2; Kar – 3 (VU); Len – 2 (EN); Fin – VU. Fig. 8. Parnassius mnemosyne (Photo Andrei Humala). Lycaenidae Thecla betulae (Linnaeus, 1758) (Fig. 9) Material. 5 km N of Nikonova Guba, 1 ♀, along the road, 22/8/2012 (Humala). In Karelia the species is known only from old records (Gorbach & Reznichenko 2009). Threat status: Kar - 4 (DD). Reports of the Finnish Environment Institute 40 | 2014 269 Fig. 9. Thecla betulae (Photo Andrei Humala). Lasiocampidae Gastropacha quercifolia (Linnaeus, 1758) Material. Vegoruksy, 1 ♂, light trap, 26/6/2013 (Polevoi, Humala). A rare species; there are a few earlier records from the Kivach nature reserve (Kutenkova 2006). Arctiidae Rhyparia purpurata (Linnaeus, 1758) (Fig. 10) Material. Vegoruksy, 2 specimens, light trap, 26/6/2013 (Polevoi, Humala); Paleostrov Island, 1 specimen, 3/7/2004, (Polevoi); Kuzaranda, 2 specimens, 4/7/2004 (Humala); Eglov island, 1 specimen 29/6/2014 (Polevoi). The species inhabits meadows. The only other place in Fennoscandia where the species occurs is southern Finland (Hydén et al. 2006). Threat status: Fin – NT. Fig. 10. Rhyparia purpurata (Photo Alexei Polevoi). 270 Reports of the Finnish Environment Institute 40 | 2014 Zygaenidae Zygaena osterodensis (Linnaeus, 1758) (Fig. 11) Material. Podyelniki, numerous specimens, 20-25/7/2011 (Polevoi, Humala); Eglov and Rogachev islands, numerous specimens, 26-29/6/2014, (Polevoi, Humala). This species is very endangered in Finland. It is also quite rare in Karelia, although locally abundant in Zaonezhye. Threat status: Kar – 3(NT); Fin – RE. Fig. 11. Zygaena osterodensis (Photo Andrei Humala). HYMENOPTERA Argidae Aprosthema hyalinopterum Conde, 1934 Material. Bukol’nikov Island, 1 ♂, 25/6/2003 (Humala). The irst record from Karelia. Vespidae Discoelius dufourii Lepeletier, 1841 Material. Bolshoi Klimenetsky Isl., 2 km NE of Kurgenitsy, 1 ♀, 19/7/2000 (Humala). A rare species; there are only a few records from Karelia (Polevoi et al. 2005, Polevoi & Humala 2013, Kutenkova 2006). Threat status: Kar - 3(VU); Finland – VU. Pompilidae Dipogon vechti Day, 1979 Material. Nizhnee Myagrozero, meadow, 1 ♀, 20/7/2012 (Humala); Myagrozero, meadow, 1 ♀, 22/7/2012 (Humala). In Karelia, the species has only been recorded from samples from Velikaya Guba (Wolf 1967). Threat status: Fin – VU. Crabronidae *Ectemnius spinipes (A. Morawitz, 1866) Material. Turastamozero, meadow, 1 ♀, 20/7/2012 (Humala). This forest-dwelling digger wasp species has not been reported previously from Karelia. Even though the species occurs in many Central European countries, it is not known from Finland and Scandinavia, west of Zaonezhye (Lomholdt 1984). Reports of the Finnish Environment Institute 40 | 2014 271 Ichneumonidae **Apechtis capulifera (Kriechbaumer, 1887) Material. Turastamozero, 1 ♀, 24/7/2012, (Humala). This is the irst record of the species in Karelia. *Perithous albicinctus (Gravenhorst, 1829) Material. Turastamozero, meadow, 1 ♂, 21/7/2012, (Humala). This is the irst record of the species in Karelia. Zatypota albicoxa (Walker, 1874) Material. Tambitsy, 1 ♂, 26/8/2013 (Humala). In Karelia, cocoons of this parasitoid spider have only been found from the Lake Ladoga area. Threat status: Kar – 3 (LC). Rossemia longithorax Humala1997 Material. Polya, 1 ♀, Malaise trap, 26/6-25/8/2013 (Humala, Polevoi). The species is described from the Kivach nature reserve (Humala 1997 a). It has also been recorded from the Pudozh district (Humala & Polevoi 2009). Coleocentrus exareolatus Kriechbaumer, 1894 Material. 3 km NE of Lipovitsy, 1 ♀, Malaise trap, 25/6-21/8/2013 (Humala, Polevoi). The species is a parasite of larvae of longhorn beetles and horntails from the genus Urocerus, inhabiting coniferous tree trunks. In Karelia, it has previously been known only from the Kivach nature reserve (Humala 1997 b). Threat status: Fin – RE. Arotes albicinctus (Gravenhorst, 1829) Material. Verkhnee Myagrozero, 1 ♀, mixed forest, 27/7/2012 (Polevoi). This ichneumon wasp species is associated with longhorn beetles. This is second record of the species in Karelia. It was irst recorded by Walter Hellén in the surroundings of the Maselgskaya station in 1943. Threat status: Fin – EN; recommended to be included in the Red Data Book of Karelia as “requiring monitoring”. *Lycorina triangulifera Holmgren, 1859 Material. Radkolye Island, 1 ♂, meadow, 25/6/2003 (Humala). The species has not been found in Karelia before. Threat status: Fin – VU. *Tranosemella coxalis (Brischke,1880) Material. Bolshoi Klimenetsky Isl., 2 km NE of Kurgenitsy, 1 ♀, 19/7/2000 (Humala). This is the irst record of the species in Karelia. *Heteropelma amictum Fabricius, 1775 (=capitatum Desvignes, 1856) Material. Tipinitsy, 1 ♂, 27/8/2013 (Humala). This is the irst record of the species in Karelia. DIPTERA Limoniidae Limonia badia (Walker, 1848) Material. Tipinitsy, 5 ♂♂, 1 ♀, 27/8/2013 (Polevoi). This poorly known species has been described from North America and it has only recently been discovered in Fennoscandia (Starý & Salmela 2004). There are few records from Karelia to date (Polevoi & Salmela, 2014). The species is probably an old-growth forest specialist. It is understood that its larvae develop in dead aspens (Starý & Salmela, 2004; Halme et al. 2013). Threat status: Fin – NT. 272 Reports of the Finnish Environment Institute 40 | 2014 Ditomyiidae Symmerus nobilis Lackschewitz, 1937 Material. 7 km S of Kosmozero, 1 ♂, 26/6/2013 (Polevoi). Symmerus nobilis has been found in several Central European countries but is considered a rare species everywhere (Jakovlev et al. 2014). All the records of adults are from broadleaved forests, with the exception of Russian Karelia that lies entirely within the boreal forest zone. In Karelia, there are only two earlier records of female specimens from the Kivach nature reserve (Polevoi 2000). In Finland it has been recorded only once from Ruissalo Strict Nature Reserve, from an herb-rich spruce-dominated forest with aspen, birch, lime and oak (Quercus robur). Both the Finnish and the Karelian sites are old-growth forests, growing on fertile soils. There is a high amount of dead aspen wood, in which larvae of the species most probably develop. Threat status: Fin – VU. Mycetophilidae Boletina kivachiana Polevoi & Hedmark, 2004 Material. Turastamozero, 21 ♂♂, 21-24/7/2012 (Polevoi). In Fennoscandia, this is a characteristic species of old-growth boreal forests. However, its distribution in Karelia is still poorly known. Threat status: Fin – VU. Asilidae Choerades tenebraus Esipenko, 1974 Material. Verkhnee Myagrozero, 1 ♂, edge of a clear-cut, 22/7/2012 (Polevoi). This is the irst record in the European part of Russia. The species has previously been known from Primorye, Sakhalin and Krasnoyarsk Krai in the East (Lehr, 1999). The biology of the species is not known but its larvae probably inhabit dead wood, like other species of the genus Choerades. Two females from the Kivach nature reserve have previously been misidentiied as Choerades marginata (Jakovlev & Polevoi 1991, Polevoi, 1997). However, after inding the male of Ch. tenebraus and re-examinining old samples, it has became clear that the specimens belong to the same species. Rhagionidae Rhagio annulatus DeGeer, 1776 Material. Kainos Island, 1 ♀, 3/7/2004 (Polevoi) In Karelia, this species has previously been known only from the Kivach nature reserve (Polevoi 1997). Threat status: Fin – NT. Syrphidae Ceriana conopsoides (Linnaeus, 1758) (Fig. 12) Material. Turastamozero, 2 ♂♂, abandoned hay meadows 20-21/7/2012 (Polevoi) Larvae of the species develop in wet, decaying wood of deciduous trees. In Karelia, the species has been recorded previously from Petrozavodsk (Polevoi et al. 2009). There are also old and new unpublished indings from different parts of southern Karelia. Threat status: Kar – 4 (DD); Fin – NT. Strongylophthalmidae Strongylophthalmyia pictipes Frey, 1935 Material. Vavlok Island, 7 ♂♂, 2 ♀♀, 3/7/2004 (Polevoi). Larvae of the species develop under the bark of dead aspens. In southern Karelia, the species is relatively common in forests with a large proportion of aspen (Polevoi 1997, Humala & Polevoi 1999; Jakovlev et al. 2001, Polevoi et al. 2005). Threat status: Fin – VU. Reports of the Finnish Environment Institute 40 | 2014 273 Tachnidae Tachina grossa Linnaeus, 1758 (Fig. 13) Material. Turastamozero, 1 ♀, 21/7/2012 (Polevoi) A large and distinctive species. Larvae are parasites in caterpillars of moths of the family Lasiocampidae. It is a relatively rare species, although it may be more abundant in southern areas. In 2013 it was encountered in large numbers in southern Olonets region. Threat status: Len – 3 (NT). Fig. 12. Ceriana conopsoides (Photo Andrei Humala). Fig. 13. Tachina grossa (Photo Andrei Humala). 274 Reports of the Finnish Environment Institute 40 | 2014 List of insect species recorded in Zaonezhye and adjacent islands * – species not present in the collections, is known for the studied territory from literature only ? – doubtful identiication Abbreviations: Bol. Klim.Isl. − Bolshoi Klimenetsky Island EPHEMEROPTERA Ephemeridae Ephemera vulgata L. – Vorobyi, Eglov Isl., Khvost Isl., Rogachev Isl. ODONATA Calopterygidae Calopteryx splendens Harr. – Turastamozero, Oyatevschina, Velikaya Niva (Valle 1952) Calopteryx virgo L. – Kosmozero, Oyatevschina Coenagrionidae Coenagrion armatum Charp. – Kizhi Isl. Coenagrion hastulatum Charp. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kizhi Isl., Kosmozero, Podyelniki, Polya, Vegoruksy, Velikaya Niva (Valle 1952) Ischnura elegans V.d.Lind. – Eglov Isl., Verkhnee Myagrozero Erythromma najas Hans. – Eglov Isl., Kizhi Isl., Podyelniki Enallagma cyathigerum Charp. – Eglov Isl., Khvost Isl., Kizhi Isl., Podyelniki, Rogachev Isl., Turastamozero, Vikshezero, Vorobyi Lestidae Lestes sponsa Hans. – Bol. Klim. Isl., Oyatevschina, Turastamozero Lestes dryas Kirby – Kazhma, Kosmozero, Oyatevschina, Shun’ga, Podyelniki, Turastamozero, Cordulegasteridae Cordulegaster boltoni (Donovan) – Turastamozero, Vikshezero. Gomphidae Gomphus vulgatissimus L. – Bol. Klim. Isl., Myagrozero, Verkhnee Myagrozero Onychogomphus forcipatus L. – Vikshezero Corduliidae Cordulia aenea L. – Bol. Klim. Isl., Eglov Isl., Kazhma, Turastamozero Somatochlora lavomaculata V.d.Lind. – Kizhi Isl., Oyatevschina Somatochlora metallica V.d.Lind. – Bol. Klim. Isl., Eglov Isl., Rogachev Isl., Velikaya Niva (Valla 1952) Libellulidae Sympetrum danae Sulzer – Kazhma, Shun’ga, Turastamozero, Vorobyi, Sympetrum laveolum L. – Bol. Klim. Isl., Kazhma, Kizhi Isl., Kosmozero, Nizhneje Myagrozero, Oyatevschina, Podyelniki, Shun’ga, Turastamozero, Vegoruksy, Vorobyi, o. Yu. Oleniy. Leucorrhinia albifrons Burm. – Podyelniki Leucorrhinia caudalis Charp. – Podyelniki Leucorrhinia dubia V.d.Lind. – Bol. Klim. Isl. Leucorrhinia rubicunda L. – Bol. Klim. Isl., Kizhi Isl., Polya Libellula fulva Müller – Turastamozero Libellula quadrimaculata L. – Bol. Klim. Isl., Eglov Isl., Kizhi Isl., Nizhneje Myagrozero, Polya, Vegoruksy, Velikaya Guba (Valle 1952), Volkostrov Isl. Aeshniidae Aeshna cyanea Müll. – Tambitsy, Uzkaya Salma, Uzkaya Salma l., Tipinitsy. Aeshna grandis L. – Bol. Klim. Isl., Eglov Isl., Kosmozero, Myagrozero, Podyelniki, Polya, Shun’ga, Tambitsy, Turastamozero, Vegoruksy, Vorobyi Reports of the Finnish Environment Institute 40 | 2014 275 Aeshna juncea L. – Kazhma, Nizhneje Myagrozero, Shun’ga, Turastamozero, Vegoruksy, Vorobyi Aeshna viridis Eversmann – Nikonova Guba ORTHOPTERA Tettigoniidae Decticus verrucivorus L. – Bol. Klim. Isl., Kosmozero, Podyelniki, Rogachev Isl., Turastamozero, Vegoruksy Metrioptera brachyptera L. – Bol. Klim. Isl., Podyelniki Metrioptera roeseli Hagenbach – Turastamozero, Vegoruksy Tettigonia cantans Fuessly – Podyelniki Tetrigidae Tetrix bipunctata (L.) – Zaonezhye (Albrecht 1979), Nizhnee Myagrozero, Bol. Klim. Isl. *Tetrix subulata (L.) – Zaonezhye (Albrecht 1979) *Tetrix tenuicornis (Sahlberg) – Zaonezhye (Albrecht 1979) Acrididae Podisma pedestris (L.) – Zaonezhye (Albrecht 1979), Bol. Klim. Isl., Podyelniki, Turastamozero, Vegoruksy, Kosmozero Omocestus viridulus L. – Khvost Isl., Kosmozero, Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Turastamozero ? Chorthippus biguttulus L. – Bol. Klim. Isl. Chorthippus brunneus (Thunb.) – Bol. Klim. Isl., Turastamozero Pseudochorthippus montanus (Charp.) – Zaonezhye (Albrecht 1979), Turastamozero Pseudohorthippus parallelus (Zett.) – Turastamozero Psophus stridulus L. – Vorobyi BLATTOPTERA Blattellidae Ectobius lapponicus L. – Nizhneje Myagrozero E. sylvestris Poda – Eglov Isl., Nizhneje Myagrozero, Vegoruksy MECOPTERA Panorpidae Panorpa alpina Ramb. – Bol. Klim. Isl. P. communis L. – Kizhi Isl., Velikaya Niva, Eglov Isl., Kazhma, Khvost Isl., Kosmozero, Rogachev Isl., Shun’ga, Vegoruksy, Velikaya Niva. RAPHIDIOPTERA Raphidia xanthostigma Schumm. – Zaonezhye NEUROPTERA Chrysopidae Chrysopa perla L. – Kizhi Isl., Eglov Isl., Khvost Isl., Rogachev Isl. Anisochrysa prasina (Burm.) – Kosmozero, Bol. Klim. Isl. Hemerobiidae Drepanopteryx phalaenoides L. – Podyelniki HEMIPTERA Cixiidae Cixius cunicularius L. – Eglov Isl. ? Cixius distinguendus Kirschbaum – Podyelniki 276 Reports of the Finnish Environment Institute 40 | 2014 Membracidae Centrotus cornutus L. – Eglov Isl. Cicadellidae Cicadella viridis L. – Podyelniki Evacanthus interruptus (L.) – Turastamozero Aphrophoridae Aphrophora alni (Fall.) – Velikaya Niva, Nikonova Guba, Podyelniki,Turastamozero Aphrophora pectoralis (Mats.) – Velikaya Niva, Shun’ga, Turastamozero, Velikaya Niva Lepyronia coleoptrata L. – Eglov Isl., Rogachev Isl. Berytidae Berytinus clavipes F. – Vegoruksy Neides tipularius L. – Eglov Isl. Notonectidae Notonecta lutea Mull. – Vorobyi Microphysidae Myrmedobia coleoptrata Fallen – Shun’ga Miridae ? Adelphocoris lineolatus Goeze – Podyelniki Adelphocoris cf. seticornis F. – Podyelniki Adelphocoris quadripunctatus F. – Nizhneje Myagrozero, Podyelniki Adelphocoris seticornis F. – Nizhneje Myagrozero, Podyelniki Atractotomus parvulus Reuter – Uzkaya Salma Capsus ater L. – Vegoruksy Capsus wagneri Rem. – Podyelniki, Rogachev Isl. Closterotomus biclavatus (H-Sch.) – Uzkaya Salma. Closterotomus fulvomaculatus DeGeer – Polya ? Dicyphus constrictus Boheman – Tambitsy Globiceps lavomaculatus Deg. – Podyelniki ? Globiceps juniperi Reuter – Podyelniki Halticus apterus L. – Podyelniki Labops sahlbergii Fallen – Eglov Isl. Leptopterna dolabrata L. – Eglov Isl., Nizhneje Myagrozero, Rogachev Isl., Turastamozero, Vegoruksy Megaloceroea recticornis Geoffr. – Nizhneje Myagrozero ? Monalocoris ilicis L. – Tipinitsy ? Orthops kalmii L. – Nizhneje Myagrozero, Vegoruksy ? Plagiognathus arbustorum F. – Podyelniki Polymerus palustris Reut. – Oyatevschina, Podyelniki Polymerus unifasciatus Fabricius – Rogachev Isl. Stenodema holsata F. – Tambitsy, Tipinitsy Stenotus binotatus F. – Oyatevschina, Podyelniki Nabiidae Dolichonabis limbatus Dhlb. – Podyelniki, Tambitsy, Turastamozero Nabis lavomarginatus Scholtz – Nikonova Guba, Nizhneje Myagrozero, Podyelniki, Shun’ga, Turastamozero Anthocoridae Anthocoris nemorum (L.) – Podyelniki, Turastamozero Coreidae Coreus marginatus L. – Eglov Isl., Podyelniki, Turastamozero Rhopalidae Corizus hyoscyami L. – Eglov Isl., Oyatevschina, Podyelniki, Turastamozero Myrmus miriformis Fallen – Vegoruksy Reports of the Finnish Environment Institute 40 | 2014 277 Stictopleurus punctatonervosus (Goeze) – Oyatevschina, Podyelniki, Tipinitsy Acanthosomatidae Acanthosoma haemorrhoidale L. – Vegoruksy Elasmostethus interstinctus L. – Tipinitsy Elasmucha betulae Deg. – Podyelniki, Velikaya Niva Elasmucha ferrugata F. – Tambitsy Elasmucha grisea L. – Velikaya Niva Aradidae Aradus betulae F. – Lipovitsy Aradus depressus F. – Nizhneje Myagrozero Aradus pictus Baerensprung – Lipovitsy, Vegoruksy Lygaeidae Drymus brunneus R.F. Sahlberg – Uzkaya Salma ? Nysius thymi Wolff – Oyatevschina Pentatomidae Neottiglossa pusilla Gmel. – Eglov Isl., Podyelniki, Tipinitsy ? Carpocoris pudicus Poda – Oyatevschina Carpocoris purpureipennis Deg. – Eglov Isl., Lipovitsy, Nizhneje Myagrozero, Podyelniki, Turastamozero Dolycoris baccarum L. – Eglov Isl., Nikonova Guba, Nizhneje Myagrozero, Oyatevschina, Podyelniki, Rogachev Isl., Shun’ga, Turastamozero, Vegoruksy. Aelia acuminata (L.) – Podyelniki, Tipinitsy, Vegoruksy Chlorochroa pinicola Mulsant & Rey – Kazhma, Nizhneje Myagrozero Eurydema oleracea L. – Nizhneje Myagrozero Picromerus bidens L. – Velikaya Niva, Nikonova Guba, Podyelniki, Shun’ga, Turastamozero, Vegoruksy. Troilus luridus Fabricius – Nikonova Guba, Shun’ga COLEOPTERA (Nomenclature follows Silfverberg 2010. Species’ names within families appear in the alphabetic order) ADEPHAGA Gyrinidae *Gyrinus marinus Gyllenhal – Tolvuya, Shun’ga (Poppius 1899) Haliplidae *Haliplus luviatilus Aubé – Tolvuya (Poppius 1899) * Haliplus fulvus (Fabricius) – Shun’ga (Poppius 1899) *Haliplus furcatus Seidlitz – Tolvuya (Poppius 1899) *Haliplus lineolatus Mannerheim – Shun’ga (Poppius 1899) *Haliplus ruicollis DeGeer – Tolvuya, Kosmozero (Poppius 1899) Dytiscidae *Acathodes fuscipennis Paykull var. obscurior J.Sahlb. – Tolvuya (Poppius 1899) Acilius canaliculatus Nicolai – Podyelniki * Agabus biguttulus Thomson – Zaonezhye (Poppius 1899) * Agabus congener (Thunberg) – Zaonezhye (Poppius 1899) * Agabus setulosus J.Sahlb. – Tolvuya (Poppius 1899) * Agabus uliginosus L. – Tolvuya (Poppius 1899) *Agabus sturmii (Gyllenhal) – Tolvuya (Poppius 1899) *Bidessus unistriatus (Goeze) – Kizhi Isl., Tolvuya, Velikaya Guba (Poppius 1899) *Coelambus impressopunctatus (Schaller) – Tolvuya, Velikaya Guba (Poppius 1899) Colymbetes paykulli Er. – Velikaya Guba (Poppius 1899), Oyatevschina, Podyelniki *Colymbetes striatus L. – Tolvuya (Poppius 1899) 278 Reports of the Finnish Environment Institute 40 | 2014 *Dytiscus marginalis L. – Tolvuya (Poppius 1899) * Graptodytes granularus (L.) – Tolvuya (Poppius 1899) * Graptodytes pictus (Fabricius.) – Tolvuya (Poppius 1899) *Heterocerus fuculus Kiesenwetter – Oleny Island (Poppius 1899) *Hydroporus ruifrons (Müller) – Kosmozero, Tolvuya (Poppius 1899) ? *Hydroporus fennicus Seidlitz – Kosmozero, Velikaya Guba (Poppius 1899) *Hydroporus erythrocephalus (L.) – Kosmozero, Tolvuya (Poppius 1899) *Hydroporus pubescens (Gyllenhal) – Tolvuya (Poppius 1899) *Hydroporus melanarius Sturm – Velikaya Guba (Poppius 1899) *Hydroporus obscurus Sturm – Kizhi Isl., Tolvuya (Poppius 1899) *Hydroporus tristis Paykull – Velikaya Guba (Poppius 1899) *Hydroporus striola (Gyllenhal) – Kosmozero, Tolvuya (Poppius 1899) *Hydrotus inaequalis (Fabricius) – Tolvuya (Poppius 1899) *Ilybius obcurus Marshall – Tolvuya (Poppius 1899) *Ilybius wasastjernae Sahlberg – Velikaya Guba (Poppius 1899) *Nebrioporus depressus (Fabricius) – Kizhi Isl., Tolvuya (Poppius 1899) *Noterus crassicornis Fabricius – Kizhi Isl., Oleny Island (Poppius 1899) *Parnus prolifericornis Fabricius – Kosmozero, Tolvuya, Shun’ga (Poppius 1899) *Rantus bistriatus (Bergsträsser) – Tolvuya (Poppius 1899) Carabidae *Agonum afrum (Duftschmid) – Velikaya Guba, Shun’ga (Poppius 1899) Agonum ericeti (Panzer) – Velikaya Guba (Poppius 1899), Kizhi Isl., B. Klim. Isl. Agonum fuliginosum (Panzer) – Kizhi Isl., B. Klim. Isl. *Agonum gracile Sturm – Shun’ga (Poppius 1899) *Agonum viduum (Panzer) – Shun’ga (Poppius 1899) *Amara apricaria Paykull – Shun’ga (Poppius 1899) *Amara aulica Panz. – Unitsa (Poppius 1899) Amara brunnea (Gyllenhal) – Unitsa (Poppius 1899), Kizhi Isl., Bol. Klim. Isl., Yu. Oleny Isl. *Amara communis Panzer – Tolvuya, Kosmozero (Poppius 1899) *Amara familiaris (Duftschmid) – Tolvuya (Poppius 1899) *Amara plebeja (Gyllenhal) – Tolvuya, Velikaya Guba (Poppius 1899) *Anchomenus sexpunctatus L. – Velikaya Guba, Kosmozero (Poppius 1899) *Badister peltatus (Panzer) – Kosmozero (Poppius 1899) *Bembidion doris (Panzer) –Tolvuya, Lizhmajärvi (Poppius 1899) *Bembidion lampros (Herbst) – Kizhi Isl., Velikaya Guba, Kosmozero, Tolvuya, Shun’ga (Poppius 1899), Vegoruksy *Bembidion obliquum Sturm – Velikaya Guba (Poppius 1899) Bembidion quadrimaculatum L. – Velikaya Guba, Tolvuya, Shun’ga (Poppius 1899), Vegoruksy *Blethisa multipunctata L. – Tolvuya (Poppius 1899) *Calathus erratus Sahlberg – Tolvuya, Kosmozero (Poppius 1899) Calathus micropterus (Duftschmid) – B. Klim. Isl., Yu. Oleny Isl., Lipovitsy Carabus glabratus L. Tolvuya (Poppius 1899), Kosmozero, B. Klim. Island, Vegoruksy, Lipovitsy Carabus violaceus L. – B. Klim. Isl. *Cicindela campestris L. – Kizhi Isl. (Poppius 1899) *Cicindela hybrida L. – Kosmozero (Poppius 1899) *Clivina fossor L. – Shun’ga (Poppius 1899) Cychrus caraboides L. – B. Klim. Isl. (Poppius 1899), Kosmozero Dromius agilis L. – Unitsa (Poppius 1899), B. Klim. Island, Lipovitsy Reports of the Finnish Environment Institute 40 | 2014 279 *Dromius sigma Rossi – Unitsa (Poppius 1899) *Dyschirius aeneus (Dejean) – Tolvuya (Poppius 1899) *Dyschirius globosus (Herbst) – Zaonezhye (Poppius 1899) Elaphrus cupreus Duftschmid – Vikshezero ?*Feronia vitrea Dejean – Unitsa (Poppius 1899) Harpalus afinis (Schrank). – Kosmozero, Tolvuya, Shun’ga (Poppius 1899), B. Klim. Isl. Harpalus latus (L). – Kosmozero (Poppius 1899), Lipovitsy Lebia chlorocephala L. – Kizhi Isl. (Poppius 1899), B. Klim. Isl. * Lebia cruxminor L. – Kizhi Isl. (Poppius 1899) *Nebria gyllenhalii Schönh. – Tolvuya (Poppius 1899) *Oodes helopioides (Fabricius) – Velikaya Guba (Poppius 1899) *Patrobus excavatus Paykull var. assimilis Chaud. – Tolvuya (Poppius 1899) * Poecilus versicolor Sturm – Velikaya Guba (Poppius 1899) Pterostichus diligens (Sturm.) − Bol. Klim. Isl. Pterostichus melanarius (Illiger) − Bol. Klim. Isl. Pterostichus minor (Gyllenhal, 1827) – Shun’ga (Poppius 1899) Pterostichus niger (Schall.) − Bol. Klim. Isl. Pterostichus nigrita (Paykull) − Bol. Klim. Isl. Pterostichus oblongopunctatus (Fabricius) − Bol. Klim. Isl., Yu. Oleny Isl. *Tachys nanus Gyllenhal – Kizhi Isl., Velikaya Guba (Poppius 1899) *Taphria nivalis (Panzer) – Tolvuya, Shun’ga (Poppius 1899) *Trechys rivularis Gyllenhal – Velikaya Guba (Poppius 1899) *Trechys secalis Paykull – Tolvuya (Poppius 1899) POLYPHAGA HYDROPHILOIDEA Hydrophilidae *Berosus luridus L. – Velikaya Guba (Poppius 1899) *Laccobius minutus L. – Kosmozero, Tolvuya, Shun’ga (Poppius 1899) *Philydrus frontalis Er. – Velikaya Guba, Tolvuya (Poppius 1899) *Choetarthria seminulum Paykull – Shun’ga (Poppius 1899) * Coelostoma orbiculare Fabricius – Velikaya Guba (Poppius 1899) *Cercyon haemorrhoidalis (Fabricius) – Velikaya Guba, Shun’ga (Poppius 1899) *Cercyon unipunctatus (L.) – Velikaya Guba (Poppius 1899) ?*Cryptopleurum atomarium (Fabricius) – Velikaya Guba, Tolvuya (Poppius 1899) *Helophorus aquaticus (L.) – Tolvuya, Shun’ga (Poppius 1899) *Hydrochus elongatus (Schaller) – Kosmozero (Poppius 1899) *Hydrochus brevis (Herbst) – Kizhi Isl. (Poppius 1899) HISTEROIDEA Sphaeritidae Sphaerites glabratus (Fabricius) − Bol. Klim.Isl. Histeridae *Platysoma minus (Rossi) – Kizhi Isl. (Poppius 1899) *Platysoma deplanatum (Gyllenhal) – Kizhi Isl. (Poppius 1899) *Margarinotus ventralis (Marseul) – Kizhi Isl. (Poppius 1899) Plegaderus vulneratus (Panzer) – Kizhi Isl. (Poppius 1899), Bol. Klim.Isl. 280 Reports of the Finnish Environment Institute 40 | 2014 STAPHYLINOIDEA Hydraenidae *Limnebius truncatellus (Thunberg) – Kizhi Isl., Kosmozero, Tolvuya, Shun’ga (Poppius 1899) Ptiliidae *Acrotrichis grandicollis Mannerheim – Kosmozero (Poppius 1899) *Acrotrichis thoracica (Waltl) – Shun’ga (Poppius 1899) *Acrotrichis montandonii (Allibert) – Unitsa (Poppius 1899) *Pteryx suturalis (Heer) – Unitsa (Poppius 1899) *Ptiliolum caledonicum (Sharp) – Unitsa (Poppius 1899) Leiodidae *Leiodes gyllenhalii Stephens – Kizhi Isl., Tolvuya (Poppius 1899) *Leiodes polita (Marsham) – Unitsa (Poppius 1899) Anisotoma axillaris (Gyll.) − Bol. Klim.Isl., Volkostrov Isl. Anisotoma castanea (Hbst.) − Bol. Klim.Isl. Anisotoma glabra (Kug.) − Bol. Klim.Isl., Yu. Oleny Isl. Anisotoma humeralis (Fabricius) − Bol. Klim.Isl., Oyatevschina, Yu. Oleny Isl., Volkostrov Isl. Anisotoma orbicularis (Hbst.) − Bol. Klim.Isl. Amphicyllus globus Fabricius − Bol. Klim.Isl., Oyatevschina, Volkostrov Isl. Agathidium badium Erich. − Bol. Klim.Isl., Yu. Oleny Isl. Agathidium confusum Bris. de Barn. − Bol. Klim. Isl. Agathidium discoideum Erich. − Bol. Klim. Isl., Yu. Oleny Isl. Agathidium pisanum Bris. de Barn. − Bol. Klim.Isl. Agathidium seminulum (L.) − Bol. Klim.Isl., Volkostrov Isl. Sciodrepoides watsoni (Spence) – Velikaya Guba (Poppius 1899), Bol. Klim. Isl., Volkostrov Isl. *Stenichnus bicolor (Denny) – Kizhi Isl. (Poppius 1899) Silphidae Necrodes littoralis (L.) – Unitsa (Poppius 1899), Podyelniki Nicrophorus vespillo (L.) − Bol. Klim.Isl. Nicrophorus vespilloides Herbst − Bol. Klim.Isl. Oiceoptoma thoracica (L.) – Velikaya Guba (Poppius 1899), Lipovitsy, Bol. Klim. Isl. Phosphuga atrata (L.) − Vorobyi Staphylinidae *Acrotona aterrima Gravenhorst – Shun’ga , Tolvuya (Poppius 1899) *Acryria inlata Gyllenhal – Kizhi Isl. (Poppius 1899) *Amisha analis Gravenhorst – Shun’ga (Poppius 1899) *Anthobium longipanne Er. – Kosmozero (Poppius 1899) *Anthobium ophthalmicum Paykull – Kizhi Isl., Kosmozero (Poppius 1899) *Atheta celata Er. – Unitsa (Poppius 1899) *Baptolinus alternans Gravenhorst – Velikaya Guba (Poppius 1899) *Baryodma lanuginosa Gravenhorst – Unitsa (Poppius 1899) *Baryodma lugubris Aubé – Tolvuya (Poppius 1899) *Baryodma morion Gravenhorst – Shun’ga (Poppius 1899) *Baryodma nitida Gravenhorst – Kizhi Isl. (Poppius 1899) *Bledius fracticornis Paykull – Shun’ga (Poppius 1899) *Bolitochara pulchra (Gravenhorst) – Kosmozero (Poppius 1899) *Bryaxis bulbifer Reich. – Shun’ga (Poppius 1899) *Creophilus maxillosus L. – Shun’ga (Poppius 1899) *Cryptobium fracticorne Paykull – Shun’ga (Poppius 1899) *Dinarcaea aequata Er. – Kizhi Isl., Velikaya Guba (Poppius 1899) Reports of the Finnish Environment Institute 40 | 2014 281 *Etheothassa concinna Marsh. – Kizhi Isl. (Poppius 1899) *Euplectus karsteni Reichenbach, – Kizhi Isl. (Poppius 1899) *Gabrius splendidulus Gravenhorst – Kizhi Isl., Kosmozero (Poppius 1899) *Gabrius trossulus Nordmann – Unitsa (Poppius 1899) *Geodromicus plagiatus Fabricius, var. nigrita Mull. – Tolvuya (Poppius 1899) *Gyrophaena laevipennis Kr. – Kosmozero, Unitsa (Poppius 1899) *Gyrophaena manca Er. – Kosmozero (Poppius 1899) *Haploderus caelatus Gravenhorst – Shun’ga (Poppius 1899) *Ischnosoma splendida Gravenhorst – Kosmozero, Velikaya Guba (Poppius 1899) *Leptusa analis Gyllenhal – Kizhi Isl. (Poppius 1899) Lordithon lunulatus L. – Kurgenitsy *Micrisaurus xantopus Er. – Unitsa (Poppius 1899) *Omalium caesum Gravenhorst – Shun’ga (Poppius 1899) *Omalium excavatum Steph. – Shun’ga (Poppius 1899) *Othius lapidicola Kiesw. – Unitsa (Poppius 1899) Oxyporus maxillosus Fabricius – Kurgenitsy Oxyporus rufus (L.) – Kurgenitsy *Oxytelus fulvipes Er. – Shun’ga (Poppius 1899) *Oxytelus rugosus Sahlb. – Shun’ga (Poppius 1899) *Philonthus agilis Gravenhorst – Shun’ga (Poppius 1899) *Philonthus cephalotes Gravenhorst – Kizhi Isl., Shun’ga (Poppius 1899) *Philonthus fulvipes Fabricius – Shun’ga (Poppius 1899) *Philonthus micans Gravenhorst – Tolvuya (Poppius 1899) *Philonthus opacus Gyllenhal – Kizhi Isl., Shun’ga , Tolvuya (Poppius 1899) *Philonthus sordidus Gravenhors – Kizhi Isl. (Poppius 1899) *Philonthus splendens Fabricius – Kizhi Isl. (Poppius 1899) *Philonthus umbratilis Gravenhorst – Shun’ga (Poppius 1899) *Phyllodrepa ruipes Geoffroy – Shun’ga (Poppius 1899) *Placusa inima Er. – Unitsa (Poppius 1899) *Placusa pumilio Er. – Unitsa (Poppius 1899) *Platystethus nodufrons Sahlb. – Shun’ga, Tolvuya (Poppius 1899) *Raphirus attenuatus Gyllenhal – Tolvuya, Unitsa (Poppius 1899) *Raphirus umbrinus Er. – Unitsa (Poppius 1899) Scaphidium quadrimaculatum Olivier − Bol. Klim. Isl. Scaphisoma agaricinum (L.) Kizhi Isl., Tolvuya (Poppius 1899), Bol. Klim.I sl., Volkostrov Isl. Scaphisoma boleti (L.) – Bol. Klim.Isl., Yu. Oleny Isl. Scaphisoma boreale (Lundbl.) – Bol. Klim. Isl., Volkostrov Isl. *Scaphisoma subalpinum Reitter – Kizhi Isl., Kosmozero (Poppius 1899) *Stenus bifoveolatus Gyllenhal – Unitsa (Poppius 1899) *Stenus biguttatus L. – Tolvuya (Poppius 1899) *Stenus canaliculatus Gyllenhal – Tolvuya (Poppius 1899) *Stenus carbonarius Gyllenhal – Kizhi Isl., Shun’ga, Unitsa (Poppius 1899) *Stenus fornicatus Steph. – Kizhi Isl. (Poppius 1899) *Stenus fuscicornis Steph. – Shun’ga (Poppius 1899) *Stenus fuscipes Gravenhorst – Unitsa (Poppius 1899) *Stenus melanarius Steph. – Kizhi Isl., Oleny Island (Poppius 1899) *Stenus nanus Steph. – Unitsa (Poppius 1899) *Stenus nitens Steph. – Shun’ga (Poppius 1899) *Stenus oculatus Gravenhorst – Unitsa (Poppius 1899) *Stenus opticus Gravenhorst – Kizhi Isl. (Poppius 1899) *Stenus palposus Zetterstedt – Shun’ga (Poppius 1899) *Stenus proditor Er. – Velikaya Guba (Poppius 1899) 282 Reports of the Finnish Environment Institute 40 | 2014 *Stenus pussilus Steph. – Kizhi Isl. (Poppius 1899) *Stenus scabriculus J.Sahlb. – Unitsa (Poppius 1899) *Stenus speculator (Lac.) – Kuzaranda, Shun’ga (Poppius 1899) *Stenus tarsatus Ljung. – Kizhi Isl., Kosmozero, Shun’ga, Tolvuya, Velikaya Guba (Poppius 1899) *Stenus vafellus Er. – Velikaya Guba (Poppius 1899) *Tachinus collaris Gravenhorst – Shun’ga (Poppius 1899) *Tachinus imetarius Gravenhorst – Kizhi Isl. (Poppius 1899) *Tachinus laticollis Gravenhorst – Velikaya Guba (Poppius 1899) *Tachinus marginatus Gyllenhal – Tolvuya (Poppius 1899) Tachyporus obtusus L. – Tipinitsy *Tachyporus scitulus Er. – Unitsa (Poppius 1899) *Tanycraerus laqueatus Marsh. – Kizhi Isl. (Poppius 1899) *Trichoderma pubescens DeGeer. – Bol. Klim. Isl. (Poppius 1899) *Xantholinus distans Muls. & Rey. – Unitsa (Poppius 1899) SCARABAEOIDEA Lucanidae Ceruchus chrysomelinus (Hochenwarth) – Lipovitsy Platycerus caprea (DeGeer) – Bol. Klim. Isl., Volkostrov Isl. Geotrupidae Geotrupes stercorosus (Scriba) – Zaonezhye (Poppius 1899), Lipovitsy, Kosmozero, Eglov Isl. Kizhi Isl., Bol. Klim.Isl. Scarabaeidae *Aphodius merdarius Fabricius – Velikaya Guba (Poppius 1899) *Aphodius niger (Panzer, 1797) – Tolvuya (Poppius 1899) *Aphodius plagiatus (L.) – Tolvuya (Poppius 1899) *Aphodius prodromus (Brahm) – Velikaya Guba (Poppius 1899) *Aphodius punctatosulcatus Sturm) – Velikaya Guba (Poppius 1899) Aphodius ruipes (L.) – Kizhi Isl. (Poppius 1899), Bol. Klim.I sl., KIzhIsl., Volkostrov Isl. *Aphodius sordidus (Fabricius) – Tolvuya (Poppius 1899) Cetonia aurata (L.) − Bol. Klim. Isl. *Onthophagus nuchicornis (L.) – Kizhi Isl. (Poppius 1899) Phylloperta horticola (L.) − Bol. Klim.Isl., Volkostrov Isl. Protaetia cuprea (Fabricius, 1775) ssp. metallica Herbst − Kurgenitsy, Yu. Oleny Isl., Nizhneje Myagrozero, Eglov Isl., Khvost Isl., Rogachev Isl. Trichius fasciatus (L.) – Kizhi Isl., Kosmozero, Kuzaranda, Velikaya Guba (Poppius 1899), Bol. Klim. Isl., Eglov Isl., Khvost Isl., Nizhneje Myagrozero, Podyelniki, Uzkaya Salma, Vegoruksy, Lipovitsy. SCIRTOIDEA Scritidae Microcara testacea (L.) – Tolvuya (Poppius 1899), Khvost Isl. *Cyphon variabilis (Thunberg) – Kosmozero (Poppius 1899) Melyridae Dasytes niger (L) – Kosmozero, Shun’ga , Tolvuya (Poppius 1899) DASCILLOIDEA Dascilidae Dascillus cervinus (L.) – Kizhi Isl., Kosmozero (Poppius 1899), Bol. Klim.Isl. Reports of the Finnish Environment Institute 40 | 2014 283 BUPRESTOIDEA Buprestidae Anthaxia quadripunctata (L.) – Tolvuya (Poppius 1899), Oyatevschina, Vegoruksy, Uzkaya Salma Chrysobothris chrysostigma (L.) – Nizhnee Myagrozero, Kosmozero, Vegoruksy *Habroloma nanum (Paykull) – Kizhi Isl. (Poppius 1899) Phaenops cyanea (Fabricius) – Vegoruksy Trachys minutus L. – Khvost Isl. BYRRHOIDEA Byrrhidae *Byrrhus pilula (L.) – Kizhi Isl. (Poppius 1899) *Byrrhus pustulatus (Forster) – Kizhi Isl. (Poppius 1899) *Cytilus auricomus (Duftschmid) – Kosmozero (Poppius 1899) DRYOPOIDEA Elmidae * Normandia nitens (Müller) – Shun’ga (Poppius 1899) ELATEROIDEA Eucnemidae Hylochares populi Muona & Brustle – Polya, Tambitsy Microrrhagus pygmaeus (Fabricius) − Bol. Klim.Isl. Elateridae Ampedus balteatus (L.) − Bol. Klim.Isl., Eglov Isl. *Ampedus cinnabarinus (Eschscholtz) – Kizhi Isl. (Poppius 1899) Ampedus erythrogonus (Müller) − Bol. Klim. Isl., Volkostrov Isl. Ampedus nigrinus (Herbst) – Unitsa (Poppius 1899) − Bol. Klim.Isl., Volkostrov Isl. *Ampedus pomorum (Herbst) – Kosmozero (Poppius 1899) Ampedus sanguineus (L.) – Oyatevschina Ampedus tristis (L.) − Bol. Klim. Isl., Kizhi Isl. Athous subfuscus (Müller) – Velikaya Guba (Poppius 1899), Bol. Klim. Isl., Eglov Isl., Volkostrov Isl. * Cidnopus aeruginosus (Olivier) – Kizhi Isl. (Poppius 1899) Ctenicera pectinicornis (L.) – Kizhi Isl. (Poppius 1899), Bol. Klim.Isl., Volkostrov Isl. Ctenicera cuprea (Fabricius) – Eglov Isl., Khvost Isl., Rogachev Isl. *Dalopius marginatus (L.) – Shun’ga (Poppius 1899), Bol. Klim. Isl. *Denticollis borealis (Paykull) – Kizhi Isl. (Poppius 1899) Denticollis linearis L. – Kizhi Isl., Lipovitsy, Kosmozero (Poppius 1899), Bol. Klim. Isl. Eanus costalis (Paykull) − Bol. Klim.Isl., Kizhi Isl., Volkostrov Isl. *Ectinus aterrimus (L.) – Kizhi Isl. (Poppius 1899) Harminius undulatus (Deg.) − Bol. Klim. Isl., Kosmozero, Yu. Oleny Isl. *Lacon fasciatus (L.) – Tolvuya, Velikaya Guba (Poppius 1899) *Liotrichus affmis (Paykull) − Bol. Klim.Isl. (Poppius 1899) Melanotus castanipes (Paykull) − Bol. Klim. Isl. *Oedostethus quadripustulatus (Fabricius) – Tolvuya, Kosmozero (Poppius 1899) Prosternon tessellatum (L.) – Kizhi Isl., Velikaya Guba (Poppius 1899), Eglov Isl., Rogachev Isl. Sericus brunneus (L.) − Bol. Klim. Isl. Selatosomus aeneus (L.) – Eglov Isl., Rogachev Isl. Selatosomus cruciatus (L.) − Bol. Klim. Isl., Volkostrov Isl. Selatosomus melancholicus (Fabricius) − Bol. Klim. Isl. 284 Reports of the Finnish Environment Institute 40 | 2014 CANTHAROIDEA Lycidae Dictyoptera aurora (Herbst) – Velikaya Guba (Poppius 1899), Kurgenitsy Lopheros rubens (Gyllenhal) – Vikshezero Lygistopterus sanguineus L. – Velikaya Guba (Poppius 1899), Bol. Klim.Isl., Nizhneje Myagrozero, Vikshezero Platycis minutus Fabricius – Turastamozero Lampyriae Lampyrus noctiluca L. – Kizhi Isl., Kosmozero, Uzkaya Salma, Velikaya Guba (Poppius 1899), Bol. Klim.Isl., Kizhi Cantharidae Abdisia schoenherri (Dejean) – Dianova Gora, Kosmozero (Poppius 1899), Bol. Klim. Isl. Polya, Uzkaya Salma, Volkostrov Isl. Cantharis igurata Mannerheim – Kizhi Isl., Kosmozero, Velikaya Guba (Poppius 1899), Eglov Isl., Khvost Isl. *Cantharis lavilabris Fallén – Kosmozero, Shun’ga , Tolvuya (Poppius 1899) Cantharis nigricans (Müller) – Eglov Isl., Rogachev Isl. Cantharis pellucida Fabricius – Lipovitsy, Rogachev Isl. Malthinus biguttatus (L.) – Kuzaranda, Tolvuya (Poppius 1899), Bol. Klim.Isl. Eglov Isl. Malthinus punctatus (Geoffroy) – Kosmozero (Poppius 1899) Eglov Isl., Khvost Isl., Uzkaya Salma Malthodes brevicollis (Paykull) – Kizhi Isl. (Poppius 1899), Eglov Isl. *Malthodes lavoguttatus Kiesenwetter –Tolvuya (Poppius 1899) Malthodes fuscus Waltl – Uzkaya Salma *Malthodes mysticus Kiesenwetter – Schunga (Poppius 1899) *Malthodes maurus (Laporte de Castelnau) – Kizhi Isl. (Poppius 1899) Podabrus lapponicus (Gyllenhal) –Velikaya Guba (Poppius 1899) Rhagonycha atra (L.) – Kizhi Isl., Kosmozero (Poppius 1899), Bol. Klim.Isl. Lipovitsy Rhagonycha elongata (Fallen) – Bol. Klim.Isl. Rhagonycha lignosa (Müller) – Eglov Isl., Lipovitsy, Polya Rhagonycha nigriventris Motschulsky– Khvost Isl., Polya Rhagonycha testacea (L.) – Kizhi Isl. (Poppius 1899) BOSTRICHOIDEA Dermestidae Dermestes lardarius L. – Kizhi Isl. Trogoderma glabrum (Herbst) – Kizhi Isl. Anthrenus museorum (L.) – Schun’ga (Poppius 1899), Kizhi Isl., Oyatevschina Anobiidae Anobium ruipes Fabricius – Kizhi Isl., Oyatevschina, Bol. Klim. Isl. Anobium thomsoni (Kraatz.) – Bol. Klim. Isl. Caenocara bovistae (Hoffmann.) – Kizhi Isl. (Poppius 1899) Dorcatoma dresdensis (Herbst). –Kosmozero (Poppius 1899), Bol. Klim.Isl., Volkostrov Isl. Dorcatoma robusta Strand. – Bol. Klim.Isl. , Volkostrov Isl. Hadrobregmus pertinax (L.) – Kizhi Isl., Bol. Klim. Isl. Hadrobregnus confusus (Kraatz) – Kizhi Isl. Priobium carpini (Herbst) – Kizhi Isl., Kosmozero, Schun’ga (Poppius 1899), Kizhi Isl. Ptilinus fuscus Geoffroy – Bol. Klim. Isl., Lipovitsy, Polya,Vegoruksy, Turastamozero, Volkostrov Isl., Yu. Oleny Ptinus raptor Sturm – Kizhi Isl. Ptinus villiger Reitter – Kizhi Isl. Reports of the Finnish Environment Institute 40 | 2014 285 LYMEXYLOIDEA Lymexylonidae Hylecoetus dermestoides (L.) – Bol. Klim.Isl., Kosmozero, Volkostrov Isl. CLEROIDEA Trogossitidae Grynocharis oblonga (L.) – Kizhi Isl. Ostoma ferruginea (L.) – Uzkaya Salma, Bol. Klim.Isl., Kosmozero, Lipovitsy Peltis grossa (L.) – Dianova Gora (Poppius 1899), Lipovitsy, Kurgenitsy Cleridae Thanasimus formicarius L. – Vikshezero Dasytidae Dasytes niger (L.) – Rogachev Isl. Dolichosoma lineare (Rossi) – Eglov Isl., Rogachev Isl. Malachidae Malachius bipustulatus (L.) – Velikaya Guba (Poppius 1899), Eglov Isl., Kizhi Isl., Vikshezero CUCUJOIDEA Kateretidae *Brachypterolus pulicarius (L.) – Kizhi Isl. (Poppius 1899) *Brachypterus urticae (Fabricius) – Shun’ga (Poppius 1899) *Kateretes pusillus (Thunberg) – Kosmozero (Poppius 1899) Nitidulidae Cychramus luteus (Fabricius) – Kosmozero, Unitsa (Poppius 1899), Velikaya Niva, Bol. Klim.Isl., Volkostrov Isl. Cychramus variegatus (Herbst) – Bol. Klim.Isl., Tambitsy, Tipinitsy, Uzkaya Salma, Volkostrov Isl. Cyllodes ater Hbst. – Kurgenitsy, Oyatevschina, Lipovitsy, Uzkaya Salma, Volkostrov Isl. *Epuraea lapponica (J.Sahlberg ) – Shun’ga , Tolvuya (Poppius 1899) *Epuraea longula Erichson – Velikaya Guba (Poppius 1899) *Epuraea marseuli Reitter – Velikaya Guba (Poppius 1899) *Epuraea pallescens (Stephens) – Kizhi Isl., Tolvuya (Poppius 1899) *Epuraea terminalis (Mannerheim) – Unitsa (Poppius 1899) Glischrochilus hortensis (Geoffroy) – Bol. Klim. Isl. Glischrochilus quadripunctatus (L.) – Bol. Klim. Isl., Tipinitsy, Vikshezero Ipidia binotata Reitter – Volkostrov Isl. *Meligethes aeneus (Fabricius) – Kosmozero, Tolvuya (Poppius 1899) *Meligethes lavimanus Stephens, 1830 – Unitsa (Poppius 1899) *Meligethes subrugosus (Gyllenhal, 1808) – Kizhi Isl., Tolvuya (Poppius 1899) *Meligethes viduatus Sturm – Shun’ga, Kosmozero (Poppius 1899) Pityophagus ferrugineus L. – Volkostrov Isl. Pocadius ferrugineus (Fabricius) – Velikaya Guba (Poppius 1899), Bol. Klim. Isl. Soronia punctatissima (Ill.) – Bol. Klim. Isl. Monotomidae *Rhizophagus bipustulatus (Fabricius) – Shun’ga, Kosmozero (Poppius 1899) Rhizophagus cribratus (Gyllenhal) – Bol. Klim. Isl. Rhizophagus depressus (Fabricius) – Bol. Klim. Isl. Rhizophagus dispar (Paykull) – Kizhi Isl., Kosmozero (Poppius 1899), Bol. Klim. Isl., Volkostrov Isl. 286 Reports of the Finnish Environment Institute 40 | 2014 Rhizophagus puncticollis Sahlberg – Kopanets Lake, Kurgenitsy Silvanidae * Silvanus unidentatus (Olivier) – Dianova Gora,Velikaya Guba (Poppius 1899) Phalacridae *Phalacrius substriatus Gyllenhal – Kizhi Isl., Kosmozero, Shun’ga, Tolvuya, Velikaya Guba (Poppius 1899) Cryptophagidae *Antherophagus pallens (L.) – Kizhi Isl. (Poppius 1899) *Atomaria fuscata (Schönherr) – Unitsa, Velikaya Guba (Poppius 1899) *Atomaria peltata Kraatz – Unitsa (Poppius 1899) Micrambe abietis (Paykull) – Bol. Klim. Isl. Erotylidae Dacne bipustulata (Thunberg) – Bol. Klim. Isl. Triplax aenea Schall. – Bol. Klim. Isl., Lipovitsy, Kosmozero Triplax ruipes Fabricius – Vikshezero Triplax russica L. – Zaonezhye (Poppius 1899), Bol. Klim. Isl., Volkostrov Isl., Yu. Oleny, Turastamozero, Uzkaya Salma Triplax scutellaris (Charp.) – Kurgenitsy Byturidae Byturus tomentosus (Deg.) – Bol. Klim.Isl., Volkostrov Isl. Cerylonidae Cerylon fagi Brisout de Barneville − Bol. Klim. Isl., Volkostrov Isl. Cerylon ferrugineum Stephens − Volkostrov Isl. Cerylon histeroides (Fabricius) – Kosmozero, Unitsa (Poppius 1899), Bol. Klim. Isl. Endomychidae Endomychus coccineus (L.) – Volkostrov Isl. Coccinellidae Anatis ocellata L. – Turastamozero Anisosticta novemdecimpunctata L. – Vorobyi Calvia quatuordecimguttata L. – Oyatevschina, Podyelniki, Rogachev Isl., Turastamozero Chilocorus renipustulatus Scriba – Turastamozero Coccinella hieroglyphica L. –Eglov Isl., Podyelniki, Turastamozero, Verkhnee Myagrozero *Coccinella magniica Redtenbacher – Unitsa (Poppius 1899) Coccinella septempunctata L. – Kizhi Isl., Kosmozero, Vikshezero, Bol. Klim. Isl., Tolvuya (Poppius 1899) Coccinula quatuordecimpustulata L. – Vorobyi, Eglov Isl., Oyatevschina, Podyelniki, Verkhnee Myagrozero, Vikshezero Hippodamia notata L. – B. Klim. Isl., Oyatevschina, Podyelniki, Uzkaya Salma, Vegoruksy, Vorobyi Hippodamia septemmaculata DeGeer – Vorobyi Myrrha octodecimguttata L. – Kizhi Isl. (Poppius 1899), Eglov Isl., Turastamozero Myzia oblongoguttata (L.) – Vegoruksy, Eglov Isl. *Oenopia conglobata L – Kosmozero (Poppius 1899) Propylea quatuordecimpunctata L. – Vorobyi, Eglov Isl., Podyelniki, Rogachev Isl., Tipinitsy, Turastamozero, Vikshezero Psyllobora vigintiduopunctata (L.) – Vorobyi, Eglov Isl., Tambitsy, Vegoruksy, Vikshezero Latridiidae Corticarina fuscula (Gyllenhal) – Kizhi Isl., Kosmozero, Shun’ga , Velikaya Guba (Poppius 1899) *Corticaria ferruginea Marsham – Tolvuya (Poppius 1899) Corticaria lapponica Zett. – Bol. Klim. Isl. Reports of the Finnish Environment Institute 40 | 2014 287 *Corticaria lateritia Mannerheim – Oleny Isl. (Poppius 1899) *Corticaria pubescens (Gyllenhal) – Shun’ga (Poppius 1899) Enicmus rugosus (Herbst) – Bol. Klim. Isl., Volkostrov Isl. Latridius hirtus (Gyllenhal) – Bol. Klim. Isl. *Latridius minutus (L.) – Shun’ga (Poppius 1899) *Stephostethus lardarius (DeGeer) – Oleny Isl. (Poppius 1899) Mordellidae *Mordellochroa abdominalis (Fabricius, 1775)– Kuzaranda (Poppius 1899) Mordella aculeata L. – Bol. Klim. Isl. Mordella holomelaena Apfelbeck – Shunevskiy Isl. Mordellistena humeralis (L.) – Shun’ga (Poppius 1899), Shunevskiy Isl. Mordellistena parvula (Gyllenhal) – Kizhi Isl. (Poppius 1899), Bol. Klim. Isl. Mordellistena pumila (Gyllenhal, 1810)– Vorobyi Tomoxia bucephala Costa – Bol. Klim. Isl., Podyelniki Zopheridae Bitoma crenata (Fabricius) – Dianova Gora, Unitsa (Poppius 1899) TENEBRIONOIDEA Mycetophagidae Litargus connexus (Geoffroy) – Bol. Klim. Isl. *Mycetophagus decempunctatus Fabricius – Kizhi Isl. (Poppius 1899) Mycetophagus fulvicollis Fabricius – Bol. Klim. Isl. Mycetophagus multipunctatus Fabricius – Kosmozero, Unitsa (Poppius 1899), Bol. Klim. Isl. Mycetophagus piceus (Fabricius) – Velikaya Guba (Poppius 1899), Bol. Klim. Isl. Mycetophagus populi Fabricius – Bol. Klim. Isl. Mycetophagus quadripustulatus (L.) – Velikaya Guba (Poppius 1899), Kurgenitsy, Volkostrov Isl. Ciidae *Cis comptus (Gyllenhal) – Dianova Gora, Schun’ga, Unitsa (Poppius 1899) *Cis bidentatus (Olivier) – Kosmozero (Poppius 1899) Cis jacquemartii Mellié – Bol. Klim.Isl. Cis micans (Fabricius) – Dianova Gora, Unitsa (Poppius 1899), B. Klim. Isl. *Cis rugulosus Mellié –Schun’ga (Poppius 1899) *Dolichocis laricinus (Mellié, 1848) – Kosmozero (Poppius 1899) *Octotemnus glabriculus (Gyllenhal) – Dianova Gora (Poppius 1899) Orthocis alni (Gyllenhal) – Bol. Klim. Isl., Volkostrov Isl. *Sulcacis fronticornis (Panzer, 1805) – Dianova Gora (Poppius 1899) Tenebrionidae Bolitophagus reticulatus (L.) – Bol. Klim. Isl., Uzkaya Salma, Polya, Volkostrov Isl. Diaperis boleti (L.) – Bol. Klim. Isl. Lagria hirta (L.) – Zaonezhye (Poppius 1899), Vorobyi, Eglov Isl., Khvost Isl., Nizhneje Myagrozero, Podyelniki, Rogachev Isl. Mycetochara lavipes (Fabricius) – Kizhi Isl., Rogachev Isl. *Tenebrio molitor L. – Unitsa (Poppius 1899) *Uloma culinaris (L.) – Unitsa (Poppius 1899) Oedemeridae Chrysanthia geniculata Heyden – Nizhneje Myagrozero, Verkhnee Myagrozero Chrysanthia viridissima (L.) – Kosmozero, Tolvuya (Poppius 1899), Bol. Klim.Isl. Oedemera virescens L. – Rogachev Isl. Tetratomidae Tetratoma ancora (Fabricius) – Bol. Klim. Isl. Hallomenus binotatus (Quensel) – Bol. Klim. Isl. 288 Reports of the Finnish Environment Institute 40 | 2014 Melandryidae Melandrya dubia Schall. – Bol. Klim. Isl. Orchesia fasciata (Illiger) – Bol. Klim. Isl., Podyelniki Orchesia micans (Panzer) – Bol. Klim.Isl., Volkostrov Isl. Phryganophilus ruicollis (Fabricius) – Bol. Klim. Isl. Xylita laevigata (Hellenius) – Bol. Klim. Isl. Pythidae Pytho depressus (L.) – Bol. Klim. Isl., Velikaya Guba (Poppius 1899), Kosmozero, Uzkaya Salma Pytho kolwensis Sahlberg – Lipovitsy, Polya, Tambitsy Pyrochroidae Schizotus pectinicornis (L.) – Zaonezhye (Poppius 1899), Bol. Klim. Isl. Anthicidae Latreille, 1819 *Notoxus monoceros (L.) – Tolvuya (Poppius 1899) Scraptiidae Anaspis arctica Zetterstedt – Dianova Gora, Kosmozero, Unitsa (Poppius 1899), Bol. Klim. Isl., Volkostrov Isl. *Anaspis frontalis (L.) – Kizhi Isl., Kosmozero, Oleny Isl., Shun’ga, Velikaya Guba (Poppius 1899) Anaspis marginicollis Lindberg – Bol. Klim. Isl. Salpingidae *Salpingus planirostris (Fabricius) – Shun’ga (Poppius 1899), Kizhi Isl. Salpingus ruicollis L. – Zaonezhye *Sphaeriestes stockmanni (Biström) – Kizhi Isl. (Poppius 1899) CHRYSOMELOIDEA Cerambycidae *Acmaeops pratensis (Laicharting) – Kizhi Isl. (Poppius 1899) Aegomorphus clavipes (Schrank) – Kosmozero (Poppius 1899), Bol. Klim. Isl., Verkhnee Myagrozero Agapanthia villosoviridescens DeGeer – Rogachev Isl. Alosterna tabacicolor DeGeer – Kosmozero (Poppius 1899), Bol. Klim. Isl., Kizhi Isl., Eglov Isl., Klimenicy, Lipovitsy, Rogachev Isl., Uzkaya Salma, Vikshezero Anoplodera livida (Fabricius) – Podyelniki, Vorobyi Anoplodera maculicornis (L.) – Vorobyi, Podyelniki, Vegoruksy, Polya, Eglov Isl., Kizhi Isl., Nizhneje Myagrozero, Rogachev Isl., Shunevskiy Isl. Anoplodera reyi (Heyden) – Podyelniki, Kuzaranda, Eglov Isl., Kainos Isl., Nizhneje Myagrozero, Polya, Turastamozero, Uzkaya Salma, Vegoruksy, Verkhnee Myagrozero Anoplodera sanguinolenta L. – Podyelniki, Nizhneje Myagrozero, Oyatevschina, Vikshezero Anoplodera virens L. – Kuzaranda (Poppius 1899), Kosmozero, Bol. Klim.Isl., Kizhi Isl., Podyelniki, Nizhneje Myagrozero, Volkostrov Isl. *Arhopalus rusticus (L.) – Kizhi Isl., Velikaya Guba (Poppius 1899) Aromia moschata (L.) – Bol. Klim. Isl. Brachyta interrogationis (L.) – Kizhi Isl., Velikaya Guba (Poppius 1899), Tipinitsy, Bol. Klim.Isl. Callidium coriaceum Paykull – Velikaya Guba (Poppius 1899), Bol. Klim. Isl., Lipovitsy, Vikshezero Callidium violaceum (L.) – Kizhi Isl. Gaurotes virginea L. –Velikaya Guba (Poppius 1899), Lipovitsy, Vegoruksy, Uzkaya Salma, Tipinitsy, Vikshezero Judolia sexmaculata L. – Kuzaranda (Poppius 1899), Bol. Klim. Isl., Turastamozero Reports of the Finnish Environment Institute 40 | 2014 289 Leiopus punctulatus (Paykull) – Polya Leptura melanura L. – Kizhi Isl., Bol. Klim.Isl., Kosmozero, Eglov Isl., Nizhneje Myagrozero, Rogachev Isl., Vorobyi Leptura nigripes (DeGeer) – Velikaya Guba (Poppius 1899), Podyelniki, Oyatevschina, Turastamozero, Vegoruksy Leptura pubescens Fabricius – Turastamozero Leptura quadrifasciata L. – Kosmozero (Poppius 1899), Kizhi Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Turastamozero, Vorobyi *Molorchus minor (L.) – Kizhi Isl. (Poppius 1899) Monochamus galloprovincialis Olivier – Tolvuya (Poppius 1899), Podyelniki, Nizhneje Myagrozero Monochamus sutor L. Turastamozero, Nizhneje Myagrozero Monochamus urussovi Fischer von Waldheim – Turastamozero, Nizhneje Myagrozero, Oyatevschina Necydalis major L. – Kosmozero, Kurgenitsy Nivellia sanguinosa (Gyllenhal) – Oyatevschina, Vikshezero Pachyta quadrimaculata L. – Kosmozero, Nizhneje Myagrozero, Podyelniki Pedostrangalia pubescens (Fabricius) – Turastamozero. Phytoecia cylindrica (L.) – Vegoruksy, Bol. Klim. Isl. Pogonocherus fasciculatus (DeGeer) – Bol. Klim. Isl. Rhagium inquisitor L. – Lipovitsy Rhagium mordax Deg. – Bol. Klim. Isl., Kazhma, Volkostrov Isl. Saperda carcharias (L.) – Bol. Klim. Isl. Saperda perforata Pallas – Verkhnee Myagrozero * Saperda scalaris (L.) – Kizhi Isl. (Poppius 1899) Tetropium castaneum (L.) – Lipovitsy Tetrops praeusta (L.) – Tolvuya (Poppius 1899), Rogachev Isl. Xylotrechus rusticus (L.) – Bol. Klim.Isl., Turastamozero, Nizhneje Myagrozero Chrysomelidae *Altica oleracea (L.) – Tolvuya (Poppius 1899) *Aphthona erichsoni (Zetterstedt) – Unitsa (Poppius 1899) (Silfverberg 1987) Bromius obscurus L. – Podyelniki, Eglov Isl., Khvost Isl., Kizhi Isl., Nizhneje Myagrozero, Oyatevschina, Rogachev Isl., Tipinitsy, Vegoruksy, Vikshezero *Bruchus atomarius L. – Bol. Klim.Isl., Kosmozero (Poppius 1899) *Cassida denticollis Suffrian – Kizhi Isl., Oleny Isl. (Poppius 1899) *Cassida nebulosa L. – Shun’ga (Poppius 1899) *Cassida rubiginosa Müller – Shun’ga (Poppius 1899) *Cassida sanguinosa Suffrian – Kosmozero, Tolvuya (Poppius 1899) Cassida viridis L. – Verkhnee Myagrozero *Chaetocnema aerosa (Letzner) – Shun’ga (Poppius 1899) *Chaetocnema aridula (Gyllenhal, 1827) – Kuzaranda (Poppius 1899) polita (L.) – Tolvuya (Poppius 1899), Eglov Isl. *Chrysolina hyperici (Forster) – Kizhi Isl. (Poppius 1899) Chrysolina varians (Schaller) – Podyelniki, Nizhneje Myagrozero, Verkhnee Myagrozero, Vikshezero Chrysomela collaris L. – Kosmozero, Tolvuya (Poppius 1899), Uzkaya Salma Chrysomela cuprea Fabricius – Kizhi Isl. (Poppius 1899), Vorobyi Chrysomela lapponica L. – Oleny Isl. (Poppius 1899), Tipinitsy, Turastamozero, Uzkaya Salma, Verkhnee Myagrozero Clytra quadripunctata L. – Eglov Isl. Crepidodera fulvicornis Fabricius – Tipinitsy 290 Reports of the Finnish Environment Institute 40 | 2014 Cryptocephalus aureolus Suffrian – Vikshezero, Vorobyi, Zaonezhye (Silfverberg 1987) *Cryptocephalus bipunctatus (L.) – Kosmozero (Poppius 1899), Zaonezhye (Silfverberg 1987) *Cryptocephalus cordiger (L.) – Kizhi Isl. (Poppius 1899), Zaonezhye (Silfverberg 1987) Cryptocephalus coryli L. – Rogachev Isl. *Cryptocephalus distinguendus Schneider – Bol. Klim. Isl., Kizhi Isl. (Poppius 1899), Zaonezhye Chrysolina *Cryptocephalus exiguus Schneider – Kosmozero, Shun’ga , Velikaya Guba (Poppius 1899), Zaonezhye (Silfverberg 1987) *Cryptocephalus labiatus (L.) – Kizhi Isl., Tolvuya, Shun’ga (Poppius 1899), Zaonezhye (Silfverberg 1987) Cryptocephalus moraei (L.) – Zaonezhye (Silfverberg 1987) *Cryptocephalus nitidulus Fabricius – Kizhi Isl. (Poppius 1899), Zaonezhye (Silfverberg 1987) *Cryptocephalus octopunctatus (Scopoli) – Kizhi Isl. (Poppius 1899), Zaonezhye (Silfverberg 1987) Cryptocephalus pini (L.) – Zaonezhye (Silfverberg 1987) Cryptocephalus sericeus (L.) – Kizhi Isl. (Poppius 1899), Bol. Klim. Isl., Oyatevschina, Turastamozero, Vikshezero *Cryptocephalus sexpunctatus (L.) – Velikaya Guba (Poppius 1899), Zaonezhye (Silfverberg 1987) *Derocrepis ruipes (L.) – Kuzaranda (Poppius 1899) Donacia clavipes Fabricius – Podyelniki, Oyatevschina Donacia crassipes Fabricius –Kosmozero (Poppius 1899), Zaonezhye (Silfverberg 1987), Eglov Isl. Donacia impressa Paykull – Zaonezhye (Silfverberg 1987) Donacia obscura Gyllenhal – Dianova Gora (Poppius 1899), Zaonezhye (Silfverberg 1987) Donacia thalassina Germar – Zaonezhye (Silfverberg 1987) Donacia vulgaris Zschach – Velikaya Guba (Poppius 1899), Zaonezhye (Silfverberg 1987) Galeruca tanaceti L. – Eglov Isl., Podyelniki, Nizhnee Myagrozero Galerucella calmariensis L. – Kizhi Isl., Uzkaya Salma Galerucella grisescens Joannis – Vorobyi Galerucella lineola Fabricius – Kizhi Isl. Galerucella nymphaeae L. – Vorobyi, Eglov Isl., Khvost Isl., Rogachev Isl., Verkhnee Myagrozero, Vorobyi *Galerucella sagittariae (Gyllenhal) – Unitsa (Poppius 1899) *Gastrophysa polygoni (L.) – Shun’ga (Poppius 1899) *Gonioctena lavicornis (Suffrian) – Oleny Isl. (Poppius 1899) *Gonioctena pallida (L.) – Bol. Klim.Isl. (Poppius 1899) Gonioctena quinquepunctata F. – Podyelniki, Verkhnee Myagrozero Gonioctena viminalis (L. – Kizhi Isl., Shun’ga (Poppius 1899), Bol. Klim. Isl., Turastamozero *Hippuriphila modeeri (L.) – Kuzaranda, Unitsa (Poppius 1899) *Hydrothassa hannoveriana (Fabricius) – Velikaya Guba (Poppius 1899) Hydrothassa marginella L. – Podyelniki, Oyatevschina *Lema cyanella (L.) – Shun’ga (Poppius 1899), Zaonezhye (Silfverberg 1987) Lilioceris merdigera (L.) – Oyatevschina, Tambitsy Lochmaea caprea L. – Rogachev Isl., Tipinitsy *Lochmaea suturalis (Thomson) – Kizhi Isl. (Poppius 1899), Tipinitsy *Longitarsus holsaticus (L.) – Kosmozero, Unitsa (Poppius 1899) Reports of the Finnish Environment Institute 40 | 2014 291 *Longitarsus lycopi (Foudras) – Tolvuya (Poppius 1899) *Longitarsus pratensis (Panzer) (as L. pusillus Gyllenhal) – Shun’ga, Unitsa (Poppius 1899) *Lythraria salicariae (Paykull) – Kizhi Isl. (Poppius 1899) Neocrepidodera femorata (Gyllenhal) – Velikaya Guba (Poppius 1899), Tambitsy *Oulema erichsonii (Suffrian) – Kosmozero (Poppius 1899), Zaonezhye (Silfverberg 1987) *Oulema gallaeciana (Heyden – Shun’ga , Tolvuya (Poppius 1899), Zaonezhye (Silfverberg 1987) *Phaedon cochleariae (Fabricius) (as Hydrothassa egena (Gyllenhal) – Kizhi Isl., Oleny Isl. (Poppius 1899) Phratora atrovirens Cornelius – Vikshezero *Phratora vitellinae (L.) – Zaonezhye (Poppius 1899) Phyllobrotica quadrimaculata L. – Podyelniki Phyllotreta nemorum (L.) – Tolvuya (Poppius 1899) *Plagiodera versicolora (Laicharting) – Oleny Isl. (Poppius 1899) Plagiosterna aenea (L.) – Uzkaya Salma, Tambitsy Plateumaris afinis (Kunze) – Rogachev Isl., Zaonezhye (Silfverberg 1987) Plateumaris discolor – Zaonezhye (Silfverberg 1987) *Plateumaris rustica (Kunze) – Velikaya Guba (Poppius 1899) *Plateumaris sericea (L.) – Kizhi Isl., Velikaya Guba (Poppius 1899), Zaonezhye (Silfverberg 1987) *Psylliodes cucullata (Illiger) – Shun’ga , Tolvuya, Unitsa (Poppius 1899) *Psylliodes napi (Fabricius) – Shun’ga (Poppius 1899) Pyrrhalta viburni Paykull – Tipinitsy Smaragdina afinis (Illiger) – Zaonezhye (Silfverberg 1987) *Smaragdina aurita (L.) – Kizhi Isl., Tolvuya (Poppius 1899) Smaragdina lavicollis Charp. – Podyelniki *Smaragdina salicina (Scopoli) – Kosmozero (Poppius 1899) Anthribidae Dissoleucas niveirostris Fabricius – Turastamozero Platystomos albinus L. – Bol. Klim.Isl., Kizhi Isl. (Poppius 1899), Verkhnee Myagrozero Atellabidae Apoderus coryli (L.) – Kizhi Isl., Kuzaranda (Poppius 1899), Uzkaya Salma *Byctiscus betulae (L.) – Kizhi (Poppius 1899) Byctiscus populi L. – Velikaya Guba (Poppius 1899), Vikshezero Deporaus betulae L. – Kosmozero (Poppius 1899), Khvost Isl. Curculionidae *Amycterus marshami (Schönherr) – Shun’ga, Tolvuya (Poppius 1899) *Apion apricans Herbst – Kizhi Isl. (Poppius 1899) Apion cerdo Gerstaecker Bol. Klim. Isl., Kizhi Isl., Kosmozero, Shun’ga (Poppius 1899), Eglov Isl. *Apion ervi Kirby – Unitsa (Poppius 1899) *Apion frumentarium (L.) – Kizhi Isl. (Poppius 1899) *Apion gyllenhali Kirby– Kizhi Isl., Shun’ga (Poppius 1899) ? Apion opeticum Bach – Tipinitsy *Apion viciae (Paykull) – Shun’ga (Poppius 1899) *Apion violaceum Kirby – Kosmozero, Shun’ga , Tolvuya (Poppius 1899) *Apion virens Herbst – Kosmozero, Shun’ga , Tolvuya, Velikaya Guba (Poppius 1899) Auleutes epilobii (Paykull) – Kuzaranda (Poppius 1899), Tipinitsy *Bagous lutulentus (Gyllenhal) – Velikaya Guba (Poppius 1899) *Brachysomus echinatus (Bonsdorff) – Kizhi Isl. (Poppius 1899) 292 Reports of the Finnish Environment Institute 40 | 2014 *Ceutorhynchus rugulosus (Herbst) – Shun’ga, Unitsa (Poppius 1899) *Ceutorhynchus typhae (Herbst – Shun’ga (Poppius 1899) *Cionus tuberculosus (Scopoli) (as C. verbasci Fabricius) – Kizhi Isl. (Poppius 1899) Cleopomiarus distinctus Boheman – Rogachev Isl. Cryphalus saltuarius Weise – Bol. Klim. Isl. Cryptorhynchus lapathi L. – Khvost Isl. *Dorytomus minutus (Gyllenhal) – Kizhi Isl. (Poppius 1899) Dryocoetes alni (Georg) – Bol. Klim.Isl., Volkostrov Isl. *Eutrichapion facetum (Gyllenhal) (as Apion sundevallii Boheman) – Bol. Klim. Isl., Shun’ga, Unitsa *Grypus equiseti (Fabricius) – Shun’ga (Poppius 1899) *Hylastes angustatus (Herbst) – Kosmozero (Poppius 1899) Hylastes cunicularius Erichsen – Bol. Klim. Isl. Hylobius abietis (L.) Bol. Klim.Isl., Vegoruksy, Uzkaya Salma, Eglov Isl. Hylobius pinastri Gyllenhal – Lipovitsy, Tipinitsy Hylurgops palliatus (Gyllenhal) – Kosmozero, Velikaya Guba (Poppius 1899), Bol. Klim. Isl., Uzkaya Salma, Vegoruksy *Hypera arator (L.) (as H. polygoni L.) – Oleny Isl., Shun’ga (Poppius 1899) *Hypera nigrirostris (Fabricius) – Kosmozero, Shun’ga, Tolvuya (Poppius 1899) Hypera rumicis (L.) – Tolvuya (Poppius 1899), Verkhnee Myagrozero *Hypera suspiciosa (Herbst) – Kizhi Isl., Oleny Isl., Shun’ga, Unitsa (Poppius 1899) *Ips sexdentatus (Börner) – Kosmozero (Poppius 1899) Ips typographus (L.) – Kosmozero, velikaya Guba (Poppius 1899), Bol. Klim. Isl., Lipovitsy, Polya, Uzkaya Salma, Vegoruksy Limnobaris dolorosa Goeze – Eglov Isl., Khvost Isl. ?Limobius borealis (Paykull) – (as Hypera dissimilis Herbst – Oleny Isl., Shun’ga (Poppius 1899)) *Magdalis carbonarius (L.) – Kizhi Isl. (Poppius 1899) *Magdalis frontalis (Gyllenhal) – Velikaya Guba (Poppius 1899) *Magdalis ruicornis (L.)(as M. pruni L.) – Bol. Klim. Isl., Oleny Isl. (Poppius 1899) *Magdalis violacea (L.) – Kizhi Isl. (Poppius 1899) *Miarus campanulae (L.) – Tolvuya (Poppius 1899) *Orthotomicus laricis (Fabricius) – Kosmozero (Poppius 1899) Otiorhynchus ovatus (L.) – Kosmozero, Shun’ga, Tolvuya (Poppius 1899), Kizhi Isl. Otiorhynchus scaber (L.) – Kizhi Isl. (Poppius 1899), Tipinitsy, Vorobyi *Pelenomus comari (Herbst) – Zaonezhye (Poppius 1899) Phloeotribus spinulosus (Rey) – Kurgenitsy Phyllobius arborator Herbst – Kizhi Isl. Phyllobius maculicornis Germar – Kosmozero (Poppius 1899), Kizhi Isl., Rogachev Isl. *Phyllobius pomaceus Gyllenhal – Tolvuya (Poppius 1899) Pissodes pini L. – Eglov Isl. Pityogenes chalcographus L. – Kizhi *Polydrusus cervinus (L.) – Kizhi Isl., Oleny Isl. (Poppius 1899) Polydrusus fulvicornis (Fabricius) – Shun’ga (Poppius 1899), Eglov Isl., Podyelniki, Rogachev Isl., Turastamozero *Polydrusus micans (Fabricius) – Kizhi Isl., Velikaya Guba (Poppius 1899 Polygraphus poligraphus (L.) – Kosmozero (Poppius 1899), Bol. Klim. Isl. *Rhinoncus castor (Fabricius) – Kizhi Isl. (Poppius 1899) *Rhynchites cupreus (L.) – Kosmozero (Poppius 1899) Scolytus ratzeburgi Janson – Bol. Klim. Isl., Volkostrov Isl. ? *Scolytus scolytus (Fabricius) (as S. destructor Olivier) – Velikaya Guba (Poppius 1899) *Sitona lineatus (L.) – Kizhi Isl., Shun’ga (Poppius 1899 Reports of the Finnish Environment Institute 40 | 2014 293 Strophosoma capitatum DeGeer – Eglov Isl., Khvost Isl., Tipinitsy *Taeniapion urticarium (Herbst ) (as Apion vernale Fabricius) – Shun’ga (Poppius 1899) *Tachyerges stigma (Germar) – Kosmozero (Poppius 1899) *Tanymecus palliatus (Fabricius) – Kosmozero, Tolvuya (Poppius 1899) *Temnocerus nanus (Paykull) – Kizhi Isl. (Poppius 1899) *Tomicus minor (Hartig) – Bol. Klim.Isl., Kosmozero, Vegoruksy, Uzkaya Salma Tomicus piniperda (L.) –Velikaya Guba (Poppius 1899), Kosmozero, Bol. Klim. Isl., Uzkaya Salma, Vegoruksy Trypodendron lineatum Olivier – Bol. Klim. Isl., Volkostrov Isl. Trypodendron signatum (Fabricius) – Bol. Klim.Isl., Volkostrov Isl. *Tychius quinquepunctatus (L.) – Oleny Isl. (Poppius 1899) Xyleborus cryptographus (Ratz.) – Bol. Lelikovskiy Isl. Xylechinus pilosus (Ratz.) – Kurgenitsy LEPIDOPTERA Hepialidae Hepialis humuli L. – Vegoruksy. Phymatopus hecta L. – Nizhneje Myagrozero Pharmacis fusconebulosa Deg. – Nizhneje Myagrozero Adelidae Nemophora amatella Staudinger – Vikshezero Nemophora degeerella L. – Eglov Isl., Khvost Isl. Tineidae Scardia boletella Fabricius – Oyatevschina Yponomeutidae Yponomeuta evonymellus L. – Eglov Isl., Rogachev Isl. Argyresthia sorbiella (Treitschke) – Vegoruksy Plutellidae Plutella xylostella (L.) – Vegoruksy Coleophoridae Coleophora deauratella Lienig & Zeller – Vegoruksy Choreutidae Anthophila fabriciana L. – Vorobyi Gelechiididae Metzneria aprilella (Herr.-Schäff.) – Vegoruksy Helcystogramma rufescens (Haworth) – Vegoruksy Acompsia cinerella (Clerck) – Vegoruksy Cossidae Cossus cossus L. – Bol. Klim. Isl., Kazhma, Kosmozero Tortricidae Celypha lacunana Den. & Schiff. – Eglov Isl., Khvost Isl., Rogachev Isl., Vegoruksy Olethreutes arcuella – Eglov Isl., Khvost Isl., Rogachev Isl. Epinotia trigonella (L.) – Vegoruksy Thiodia citrana (Hbn.) – Vegoruksy Eucosma cana (Haworth) – Vegoruksy Lathronympha strigana (F.) – Eglov Isl., Vegoruksy Clepsis rogana – Khvost Isl., Rogachev Isl. Phiaris umbrosana – Rogachev Isl. Eana argentana – Rogachev Isl. Aphelia unitana Hübner – Kizhi Isl., Rogachev Isl. Dichrorampha petiverella L. – Rogachev Isl. Epermeniidae Epermenia illigerella Hb. – Khvost Isl. 294 Reports of the Finnish Environment Institute 40 | 2014 Pterophoridae Hellinsia didactylites (Ström) – Vegoruksy Hellinsia osteodactylus (Zeller) – Vegoruksy Gillmeria pallidactyla (Haworth) – Rogachev Isl. Pyralidae Eurrhypara hortulata L. – Rogachev Isl. Evergestis pallidata Hufn. – Kizhi Isl. ? Udea lutealis Hübner – Nizhneje Myagrozero Udea hamalis Thunb. – Lipovitsy Nymphula nitidulata Hufnagel – Podyelniki, Verkhnee Myagrozero Crambidae Crambus lathoniellus (Zincken) – Vegoruksy Chrysoteuchia culmella L. – Eglov Isl., Khvost Isl., Zygaenidae Adscita statices L. – Kizhi Isl., Vikshezero, Rogachev Isl. Zygaena lonicera Scheven – B. Klimenetsky Isl., Podyelniki, Rechnoi Isl. Zygaena osterodensis Reiss – B. Klimenetsky Isl., Podyelniki, Eglov Isl., Khvost Isl., Rogachev Isl. Zygaena viciae Scheven – Podyelniki Hesperidae Pyrgus alveus Hb. – Isl. B. Klimenetsky, Eglov Isl., Kosmozero (Kaisila 1947), Sennaya Guba, Shun‘ga (Kaisila 1947) Pyrgus malvae L. – Bol. Klim. Isl., Sennaya Guba, Sennaya Guba Carterocephalus palaemon Pallas – Bol. Klim. Isl., Eglov Isl.,Velikaya Guba (Kaisila 1947). Carterocephalus silvicola Mg. – Bol. Klim. Isl., Kizhi Isl. (Kaisila 1947), Sennaya Guba, Velikaya Guba (Kaisila 1947), Volkostrov Isl., Oyatevschina Thymelicus lineola Ochs. – Bol. Klim. Isl., Myagrozero, Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Sennaya Guba, Shun‘ga, Turastamozero, Verkhnee Myagrozero, Vorobyi Hesperia comma L. – Shun’ga (Kaisila 1947), Vorobyi Ochlodes sylvanus Esper – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kizhi Isl., Lelikovo, Myagrozero, Rogachev Isl., Sennaya Guba, Turastamozero, Uzkaya Salma, Vegoruksy Pieridae Leptidea sinapis L. – Kizhi Isl., Bol. Klim. Isl., Oyatevschina, Eglov Isl. , Sennaya Guba, Kosmozero Aporia crataegi L. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kizhi Isl., , Kuzaranda, Nizhneje Myagrozero, Oyatevschina, Isl. Rechnoi, Rogachev Isl., Sennaya Guba, Vorobyi. Pieris brassicae L. – Bol. Klim. Isl., Kizhi Isl. Pieris napi L. – Bol. Klim. Isl., Kizhi Isl., Lelikovo, Kosmozero, Sennaya Guba, Oyatevschina Pieris rapae L. – Bol. Klim. Isl., Oyatevschina, Sennaya Guba Pontia edusa F.– Kizhi Isl., Kurgenitsy Anthocharis cardamines L. – Bol. Klim. Isl., Eglov Isl., Kizhi Isl., Sennaya Guba, Uzkaya Salma, Oyatevschina, Gonepteryx rhamni L. –Bol. Klim. Isl., B.Lelikoskiy Isl., Kizhi Isl., Kosmozero, Lelikovo, Podyelniki, Sennaya Guba, Tambitsy, Verkhnee Myagrozero, Vorobyi Colias palaeno L. – Sennaya Guba, Turastamozero Papilionidae Papilio machaon L. – Bol. Klim. Isl., Kizhi Isl., Oyatevschina, Podyelniki, Sennaya Guba, Turastamozero, Vorobyi Parnassius mnemosyne (L.) – Kizhi Isl., Sennaya Guba, Shunevskiy Isl., Velikaya Niva, Volkostrov Isl., Vorobyi Reports of the Finnish Environment Institute 40 | 2014 295 Lycaenidae Lycaena virgaureae L. – Kizhi Isl., Bol. Klim. Isl., Kosmozero, Lelikovo, Nizhneye Myagrozero, Oyatevschina, Podyelniki, Sennaya Guba, Turastamozero, Vorobyi Lycaena hippothoe L. – Bol. Klim. Isl., Eglov Isl., Rogachev Isl., Sennaya Guba, Tolvuya (Kaisila 1947) Lycaena dispar Haworth – Lelikovo (Juho Paukkunen pers. comm.) Celastrina argiolus L. – Bol. Klim. Isl., Eglov Isl., Nizhneye Myagrozero, Sennaya Guba Glaucopsyche alexis Poda – Bol. Klim. Isl., Sennaya Guba Aricia artaxerxes F. – Bol. Klim. Isl., Sennaya Guba Aricia eumedon Esper – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Rogachev Isl., Sennaya Guba *Aricia nicias Meigen – Kosmozero (Kaisila 1947) Plebeius optilete Knoch – Podyelniki, Turastamozero Plebeius argus L. – Nizhneye Myagrozero, Sennaya Guba, Turastamozero Polyommatus amandus Schneider – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kuzaranda, Nizhneje Myagrozero, Podyelniki, Rechnoi Isl., Rogachev Isl., Sennaya Guba, Turastamozero Polyommatus icarus Rott. – Bol. Klim. Isl., Lelikovo, Sennaya Guba Polyommatus semiargus Rott. – Bol. Klim. Isl., Kizhi Isl., Nizhneye Myagrozero, Rogachev Isl., Sennaya Guba, Turastamozero, Isl. Volkostrov Callophrys rubi L. – Bol. Klim. Isl., Sennaya Guba Thecla betulae (L.) –Nikonova Guba Satyrium pruni L. – Bol. Klim. Isl., Eglov Isl., Kosmozero (Kaisila 1947), Tolvuya (Kaisila 1947), Velikaya Niva (Kaisila 1947), Uzkaya Salma Nymphalidae Aglais urticae L. – Bol. Klim. Isl., Kizhi Isl., Kosmozero, Lelikovo, Nizhneje Myagrozero, Podyelniki, Isl. Rechnoi, Sennaya Guba, Tambitsy, Turastamozero. Vanessa atalanta L. – Bol. Klim. Isl., Kosmozero, Lelikovo, Polya, Sennaya Guba, Vegoruksy Vanessa cardui L.– Bol. Klim. Isl., Sennaya Guba Nymphalis antiopa L.– Bol. Klim. Isl., B.Lelikoskiy Isl., Kosmozero, Oyatevschina, Sennaya Guba, Turastamozero Polygonia c-album L. – Bol. Klim. Isl., Kazhma, Kizhi Isl., Kosmozero, Kuzaranda, Podyelniki, Isl. Rechnoi, Sennaya Guba, Tambitsy, Turastamozero, Vorobyi Inachis io L.– Bol. Klim. Isl., B.Lelikoskiy Isl., Sennaya Guba, Turastamozero Araschnia levana L. – Bol. Klim. Isl., Eglov Isl., Kizhi Isl., Kosmozero, Lelikovo, Podyelniki, Sennaya Guba., Oyatevschina Limenitis populi L. – Bol. Klim. Isl., Oyatevschina, Sennaya Guba, Turastamozero Euphydryas maturna L. – Bol. Klim. Isl., Kizhi Isl., Sennaya Guba Argynnis niobe L. – Kosmozero, Tolvuya (Kaisila 1947) Argynnis adippe Den. & Schiff. – Bol. Klim. Isl., Kosmozero, Sennaya Guba, Tolvuya Argynnis aglaja L. – Bol. Klim. Isl., Kizhi Isl., Nizhneje Myagrozero, Podyelniki, Sennaya Guba, Turastamozero, Verkhnee Myagrozero, Vikshezero Argynnis paphia L. – Bol. Klim. Isl., Kosmozero, Myagrozero, Nizhneje Myagrozero, Podyelniki, Turastamozero, Vegoruksy, Verkhnee Myagrozero, Shun’ga Brenthis ino Rott. – Bol. Klim. Isl., Eglov Isl., Kizhi Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Sennaya Guba, Turastamozero Melitaea athalia Rott. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kizhi Isl., Rogachev Isl., Sennaya Guba, Turastamozero Boloria euphrosyne L. – Bol. Klim. Isl. Boloria selene Den. & Schiff. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kosmozero, Kuzaranda, Lelikovo, Podyelniki, Rogachev Isl., Sennaya Guba, Tipinitsy, Turastamozero, Volkostrov Isl., Oyatevschina. 296 Reports of the Finnish Environment Institute 40 | 2014 *Boloria titania Esper – Shun’ga, Vegoruksy (Kaisila 1947) Boloria aquilonaris Stich. – Tolvuya (Kaisila 1947), Uzkaya Salma Pararge aegeria L. –Bol. Klim. Isl., Boyarschina, Sennaya Guba Aphantopus hyperantus L. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kuzaranda, Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Sennaya Guba, Shun’ga, Turastamozero, Vegoruksy Coenonympha glycerion Borkh. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kuzaranda, Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Sennaya Guba, Turastamozero, Vegoruksy Maniola jurtina L. – Bol. Klim. Isl., Sennaya Guba, Turastamozero, Vegoruksy *Oenis jutta Hübner – Kizhi Isl., Velikaya Guba (Kaisila 1947) *Hyponephele lycaon Kühn – Shun’ga (Kaisila 1947) Lasiommata maera L. – Bol. Klim. Isl., Eglov Isl., Khvost Isl., Kuzaranda, Rogachev Isl., Sennaya Guba, Turastamozero Lasiommata petropolitana F. – Bol. Klim. Isl. *Erebia euryale Esper. – Lizhma (Kaisila 1947) Erebia ligea L. – Bol. Klim. Isl., Kosmozero, Oyatevschina, Turastamozero Geometridae *Baptria tibiale borealis Lankeila – Bol. Klim. Isl., Kizhi Isl. (Kaisila 1947) Abraxas sylvatus Scop. – Oyatevschina, Sennaya Guba, Volkostrov Isl. Antonechloris smaragdaria F. – Rogachev Isl. Thetidia smaragdaria (F.) – Rogachev Isl. Cabera pusaria L. – Vegoruksy Macaria alternata Den. & Schiff. – Rogachev Isl. Plemyria rubiginata (Den. & Schiff.) – Vorobyi Geometra papilionaria L. – Bol. Klim. Isl., Kosmozero. Scotopteryx chenopodiata L. – Kizhi Isl., Podyelniki, Turastamozero Dysstroma citrata (L.) – Oyatevschina, Kizhi Isl., Lelikovo, Vegoruksy Eulithis populata L. – Oyatevschina *Apeira syringaria L. – Kosmozero (Kaisila 1947) *Arichanna melanaria L. – Tolvuya (Kaisila 1947) *Anticollix sparsatus Treitschke – Tolvuya (Kaisila 1947) *Catarhoe cuculata Hufn. – Kosmozero, Velikaya Guba (Kaisila 1947) *Electrophaes corylata Thunb. – Kizhi Isl., Velikaya Guba (Kaisila 1947) *Spargania luctuata (Den. & Schiff.) – Bol. Klim. Isl., Kizhi Isl., Kuzaranda, Velikaya Guba (Kaisila 1947) *Antyclea derivata (Den. & Schiff.) – Velikaya Guba (Kaisila 1947) *Colostygia aptata Hbn. – Kizhi Isl., Kosmozero (Kaisila 1947) Hydriomena furcata Thunb. – Oyatevschina. Plemyria rubiginata Den. & Schiff. – Vorobyi Perizoma alchemillatum L. – Kizhi Isl. Perizoma didymatum L. – Oyatevschina Perizoma lavofasciata Thunb. – Khvost Isl. Odezia atrata L. – Eglov Isl., Khvost Isl., Polya, Rogachev Isl. Siona lineata Scop. – Eglov Isl., Khvost Isl., Rogachev Isl., Vegoruksy Itame brunneatum Thunb. – Oyatevschina Pseudopanthera macularia L. – Bol. Klim. Isl. Epirrhoe alternata (Müller) – Lelikovo, Sennaya Guba, Vorobyi Epirrhoe tartuensis Möls – Khvost Isl. Epirrhoe tristata L. – Rogachev Isl. Xanthorhoe montanata (Den. & Schiff.) – Rogachev Isl., Vegoruksy Scopula loslactata Haworth – Vegoruksy Reports of the Finnish Environment Institute 40 | 2014 297 Scopula immorata L. – Khvost Isl., Vegoruksy Scopula immutata L. – Khvost Isl. Idaea aversata L. – Vegoruksy Timandra griseata W. Petersen – Khvost Isl., Rogachev Isl., Vegoruksy Angerona prunaria (L.) – Rogachev Isl., Vegoruksy Chiasmia clathrata L. – Eglov Isl., Khvost Isl. Cosmorhoe ocellata L. – Khvost Isl. Crocallis elinguaria L. – Kizhi Isl. Chloroclysta citrata L. – Kizhi Isl. Sphingidae Hemaris tityus L. – Kizhi Isl. (Kaisila 1947), Vorobyi *Hemaris fuciformis L. – Kuzaranda (Kaisila 1947) Deilephila elpenor (L.) – Turastamozero, Velikaya Niva, Vorobyi *Deilephila porcellus L. – Kizhi Isl. (Kaisila 1947) *Smerinthus ocellatus L. – Kizhi Isl., Kosmozero (Kaisila 1947) Hyles gallii Rtmbrg – Velikaya Niva, Kazhma, Nizhnee Myagrozero, Kazhma. Lasiocampidae Gastropacha quercifolia L. – Vegoruksy Euthrix potatoria L. – Eglov Isl., Kizhi Isl., Tambitsy, Vegoruksy, Shunevsky Isl. Lasiocampa quercus L. – Shunevsky Isl. Notodontidae *Pterostoma palpinum Clerck – Bol. Klim. Isl., Kizhi Isl., Velikaya Guba (Kaisila 1947) Clostera anastomosis (L.) – Vegoruksy Ptilodon capucina L. – Tipinitsy Lymantriidae Orgyia antiqua L. – Zaonezhye Calliteara pudibunda (L.) – Turastamozero, Lambasruchey, Tambitsy Nolidae Nola aerugula Hübner – Vegoruksy Arctiidae *Thumatha senex (Hb.) –Tolvuya (Kaisila 1947) Eilema lurideolum (Zinck.) – Kizhi Isl. *Eilema lutarellum (L.) – Kosmozero (Kaisila 1947) *Eilema cereolum (Hb.) – Velikaya Niva (Kaisila 1947) Parasemia plantaginis (L.) – Zaonezhye Rhyparia purpurata (L.) – Eglov Isl., Isl., Kuzaranda, Paleostrov Isl., Rechnoi, Vegoruksy Cybosia mesomella (L.) – Eglov Isl., Rogachev Isl., Vegoruksy *Coscinia cribraria (L.) – Lizhma (Kaisila 1947) Diacrisia sannio (L.) – Eglov Isl., Rogachev Isl., Uzkaya Salma, Vegoruksy Spilosoma luteum (Hufnagel) – Khvost Isl., Oyatevschina Noctuidae Hypena proboscidalis L. – Kizhi Isl., Rogachev Isl. Euclidia glyphica L. – Eglov Isl., Oyatevschina Plusia putnami Grote – Kizhi Isl. Autographa excelsa Kretschmar – Kizhi Isl., Vorobyi *Autographa macrogamma Ev. – Kosmozero, Tolvuya (Kaisila 1947) Autographa bractea (Den. & Schiff.) – Vorobyi Acronicta rumicis L. – Vorobyi, Turastamozero Acronicta auricoma (Den. & Schiff.) – Podyelniki, Vorobyi Syngrapha interrogationis L. – Kizhi Isl. *Syngrapha microgamma Hbn. – Velikaya Guba, Velikaya Niva (Kaisila 1947) Abrostola triplasia L. – Kizhi Isl. 298 Reports of the Finnish Environment Institute 40 | 2014 Oligia strigilis L. – Kizhi Isl. Cerapteryx graminis L. – Kizhi Isl. Mythimna impura Hbn. – Kizhi Isl. Actinotia polyodon Cl. – Kizhi Isl. Phytometra viridaria Clerck – Kizhi Isl. (Kaisila 1947) Rivula sericealis Scop. – Khvost Isl., Kosmozero (Kaisila 1947), Vegoruksy, Velikaya Guba (Kaisila 1947) *Anarta myrtilli L. – Kizhi Isl. (Kaisila 1947) *Athetis pallustris Hbn. – Bol. Klim. Isl. (Kaisila 1947) *Platyperigea montana (Bremer) – Shun’ga (Kaisila 1947) *Cucullia gnaphalii Hbn. – Kosmozero (Kaisila 1947) *Cucullia umbratica L. – Kosmozero (Kaisila 1947) *Panemeria tenebrata Scop. – Zaonezhye (Kaisila 1947) *Hadena bicruris Hufnagel – Kosmozero (Kaisila 1947) *Papestra biren Goeze – Kosmozero (Kaisila 1947) *Discestra trifolii Hufnagel – Velikaya Guba (Kaisila 1947) *Mamestra brassicae L. – Kuzaranda (Kaisila 1947) *Spaelotis ravida (Den. & Schiff.) – Shun’ga (Kaisila 1947) Chersotis cuprea Den. & Schiff. – Vorobyi Xestia baja Den. & Schiff. – Nizhneje Myagrozero *Xestia c-nigrum L. – Kosmozero (Kaisila 1947) *Xestia cincera Herrich-Schaeffer – Velikaya Guba (Kaisila 1947) Xanthia icteritia Hufnagel – Turastamozero Polymixis gemmea Treitschke – Vegoruksy Hoplodrina blanda Den. & Schiff. – Vegoruksy Rusina ferruginea Esper – Vegoruksy Amphipoea crinanensis Burrows – Vegoruksy Lasionycta imbecilla (F.) – Nizhneje Myagrozero, Tolvuya (Kaisila 1947), Vegoruksy Helotropha leucostigma Hübner – Velikaya Niva Catocala fraxini – Lipovitsy, Polya, Vegoruksy Melanchra pisi (L.) – Vorobyi Melanchra persicariae L. – Tambitsy Staurophora celsia L. – Turastamozero,Vegoruksy Polypogon tentacularia L. – Khvost Isl., Rogachev Isl., Vegoruksy Protodeltote pygarga Hufnagel – Eglov Isl., Khvost Isl., Vegoruksy Deltote uncula Clerck – Eglov Isl. Allophyes oxyacanthae L. – Vegoruksy HYMENOPTERA Argidae Arge nigripes Retz. – Kurgenitsy, Turastamozero, Eglov Isl., Rogachev Isl., Sennaya Guba Arge pagana Pz. – Kurgenitsy, Podyelniki, Turastamozero, Nizhnee Myagrozero Arge ustulata L. – Vorobyi, Uzkaya Salma, Turastamozero, Nizhnee Myagrozero, Eglov Isl. Aprosthema hyalinopterum Conde – Sennaya Guba Pamphilidae Pamphilius hortorum Klug – Rogachev Isl. Cimbicidae Abia candens Konow – Velikaya Niva, Kosmozero (Kontuniemi 1965) Abia (Zaraea) fasciata L. – Kurgenitsy Reports of the Finnish Environment Institute 40 | 2014 299 Cimbex connata Schr. – Vorobyi Cimbex femorata L. – Vorobyi, Myagrozero, Nizhnee Myagrozero Cimbex lutea L. – Lydskoi Isl. Corynis obscura (F.) – Lelikovo, Sennaya Guba *Trichiosoma aenescens Guss. – Oyatevschina, Kizhi Isl. (Kontuniemi 1965) Trichiosoma sylvaticum Leach – Vorobyi Diprionidae *Monoctenus obscuratus Htg. – Podyelniki, Kizhi Isl. (Kontuniemi 1965) *Macrodiprion nemoralis Ensl. – Velikaya Guba (Kontuniemi 1965) Neodiprion sertifer Geoffr. – Vorobyi Tenthredinidae *Dolerus elderi Kincaid – Shun’ga (Kontuniemi 1965) *Brachythops lavens (Klug) – Kizhi Isl. (Kontuniemi 1965) *Brachythops wuestneii (Konow) – Kizhi Isl. (Kontuniemi 1965) *Heterarthrus nemoratus (Fallen) – Kizhi Isl. (Kontuniemi 1965) *Hoplocampa alpina Zett. – Kizhi Isl. (Kontuniemi 1965) *Nematus (Pteronidea) capreae (L.) – Shun’ga (Kontuniemi 1965) *Athalia glabricollis Thoms. – Tolvuya (Kontuniemi 1965) Cladius pectinicornis Geoffr. – Vorobyi *Eriocampa dorpatica Konow – Velikaya Niva (Kontuniemi 1965) Siobla ruicornis (Cameron) – Tipinitsy Fenusa pusilla Lep. – Shun’ga (Kontuniemi 1965, Viramo, 1969) *Tenthredo rossii (Panzer) – Shun’ga, Velikaya Niva (Kontuniemi 1965) Cephidae Cephus cultratus Evers. – Kizhi Isl. (Kontuniemi 1965), Eglov Isl., Khvost Isl., Rogachev Isl., Lyudskoi Isl., Sennaya Guba Cephus fumipennis Evers. – Lelikovo, Ernitsky Isl. Cephus nigrinus Thoms. – Eglov Isl., Rogachev Isl., Lyudskoi Isl. Calameuta iliformis (Evers.) – Lyudskoi Isl., Sennaya Guba, Lelikovo Xiphydriidae Xiphydria camelus L. – Vorobyi, Kurgenitsy, Myagrozero, Oyatevschina Xiphydria picta Konow – Kizhi Isl. Siricidae Urocerus gigas L. – Oyatevschina, Nizhnee Myagrozero Sirex juvencus L. – Kizhi Isl. Bethylidae Bethylus fuscicornis (Jurine) – Eglov Isl. Dryinidae Lonchodryinus ruicornis-complex – Vorobyi, Velikaya Niva Mutillidae Mutilla europaea L. – Bol. Klim. Isl., B.Lelikoskiy Isl., Kuzaranda, Oyatevschina, Turastamozero, Nizhnee Myagrozero Chrysididae Chrysis angustula Schenck – Oyatevschina, Kizhi Isl., Vorobyi, Turastamozero Chrysis impressa Schenck – Vorobyi, Turastamozero Chrysis solida Haupt – Kurgenitsy Chrysis ruddii Shuckard – Kizhi Isl. Chrysura hirsuta (Gerstaecker) – Vorobyi *Pseudomalus auratus (L.) – Tolvuya (Hellén 1919) Formicidae Myrmica lobicornis Nyl. – Sennaya Guba Myrmica lonae Finzi – Sennaya Guba 300 Reports of the Finnish Environment Institute 40 | 2014 Myrmica rubra L. – Kizhi Isl., Vorobyi, Sennaya Guba Myrmica ruginodis Nyl. – Vorobyi Myrmica rugulosa Nyl. – Sennaya Guba Myrmica scabrinodis Nyl. – Sennaya Guba Lasius niger (L.) – Sennaya Guba Formica fusca L.– Sennaya Guba Formica rufa coll. – Sennaya Guba Formica sanguinea Latr. – Sennaya Guba Camponotus herculeanus L. – Vorobyi Pompilidae Dipogon vechti Day – Myagrozero, Nizhnee Myagrozero Dipogon bifasiatus (Geoffr.) – Velikaya Guba (Wolf 1967),Turastamozero, Auplopus carbonarius (Scop.) – Turastamozero, Nizhnee Myagrozero Agenioideus cinctellus (Spin.) – Vorobyi, Podyelniki, Myagrozero, Nizhnee Myagrozero, Eglov Isl. Arachnospila opinata (Tourn.) – Vorobyi, Myagrozero Anoplius nigerrimus (Scop.) – Podyelniki, Myagrozero, Nizhnee Myagrozero, Lelikovo Vespidae Eumenes coarctatus (L.) – Shun’ga Eumenes coronatus (Panz.) – Vorobyi, Shun’ga, Turastamozero Eumenes pedunculatus (Panz.) – Vorobyi, Nizhnee Myagrozero Discoelius dufourii Lep. – Kurgenitsy, Turastamozero Ancistrocerus antilope (Panz.) – Vorobyi, Turastamozero, Nizhnee Myagrozero Ancistrocerus claripennis Thoms. – Shun’ga (Pekkarinen & Huldén 1991), Turastamozero, Nizhnee Myagrozero Ancistrocerus parietinus (L.) – Rogachev Isl., Shun’ga, Podyelniki Ancistrocerus parietum (L.) – Kizhi Isl., Ladmozero, Nizhnee Myagrozero Ancistrocerus scoticus Curtis – Turastamozero Ancistrocerus trifasciatus Mull. – Kizhi Isl., Turastamozero, Podyelniki, Kosmozero, Eglov Isl. Symmorphus angustatus Zett. – Turastamozero, Ladmozero, Nizhnee Myagrozero Symmorphus allobrogus (Saussure) – Tolvuya (Pekkarinen & Huldén 1991), Kizhi Isl., Turastamozero, Vikshezero Symmorphus bifasciatus (L.) – Vorobyi, Kurgenitsy, Kosmozero, Turastamozero, Shun’ga, Rogachev Isl. Gymnomerus laevipes (Schuck.) – Vorobyi, Lelikovo Stenodynerus picticrus Thoms. – Nizhnee Myagrozero Euodynerus quadrifasciatus (F.) – Vorobyi Vespa crabro L. – Vorobyi, Podyelniki, Turastamozero, Nizhnee Myagrozero, Myagrozero Vespula rufa L. – Kizhi Isl., Turastamozero Vespula vulgaris L. – Kizhi Isl., Boyarschina, Sennaya Guba, Turastamozero Dolichovespula media Retz. – Bol’shoiu Lelikoskiy Isl., Eglov Isl., Polya, Uzkaya Salma, Turastamozero Dolichovespula norwegica F. – Kizhi Isl., Vorobyi, Vikshezero, Podyelniki, Polya, Uzkaya Salma, Turastamozero, Myagrozero Dolichovespula saxonica F. – Myagrozero, Turastamozero, Eglov Isl., Rogachev Isl. Dolichovespula sylvestris Scop. – Podyelniki, Turastamozero Sphecidae Ammophila sabulosa L. – Kurgenitsy, Vorobyi Crabronidae Trypoxylon attenuatum Smith – Vegoruksy, Lyudskoi Isl., Lelikovo Trypoxylon igulus (L.) – Podyelniki Reports of the Finnish Environment Institute 40 | 2014 301 Pemphredon inornata Say – Eglov Isl., Pemphredon lugubris (F.) – Eglov Isl., Podyelniki Pemphredon morio v.d.Lind. – Podyelniki, Nizhnee Myagrozero Pemphredon wesmaeli A.Mor. – Rogachev Isl. Mimumesa dahlbomi (Wesm.) – Kurgenitsy Crabro peltarius (Schreber) – Rechnoi Isl. Ectemnius cavifrons Thoms. – Kizhi Isl., Volkostrov Isl. Ectemnius continuus F. – Kurgenitsy, Myagrozero, Turastamozero Ectemnius dives Lep. et Br. – Podyelniki Ectemnius fossorius L. – Vorobyi, Kurgenitsy, Volkostrov Isl., Bolshoi Lelikoskiy Isl., Turastamozero, Podyelniki, Zubovo, Eglov Isl., Ladmozero, Myagrozero, Nizhnee Myagrozero Ectemnius lapidarius Panz. – Kurgenitsy Ectemnius ruicornis Zett. – Nizhnee Myagrozero, Kurgenitsy, Turastamozero Ectemnius spinipes (A. Mor.) – Nizhnee Myagrozero, Turastamozero Lestica clypeata (Schreber) – Podyelniki Crossocerus assimilis Smith – Kizhi Isl. Crossocerus dimidiatus (F.) – Kurgenitsy Crossocerus heydeni Koehl. – Vorobyi, Podyelniki Crossocerus vagabundus Pz. – Eglov Isl. Spilomena enslini Blüthgen – Podyelniki, Myagrozero Mellinus arvensis (L.) – Vorobyi Oxybelus uniglumis – Ladmozero Nysson interruptus (F.) – Vorobyi Nysson niger Chevrier – Nizhnee Myagrozero Nysson spinosus – Nizhnee Myagrozero ?Passaloecus borealis Dahlbom – Nizhnee Myagrozero ?Passaloecus gracilis (Curtis) – Vorobyi Passaloecus insignis v.d.Lind. – Vorobyi, Ernitsky Isl., Nizhnee Myagrozero Argogorytes fargei Shuckard – Vorobyi Argogorytes mystaceus L. – Nizhnee Myagrozero, Eglov Isl. Gorytes quadrifasciatus (F.) – Vorobyi, Kurgenitsy, Yu. Oleny Isl., Podyelniki Rhopalum clavipes L. – Turastamozero Rhopalum coarctatum Scop. – Kurgenitsy, Nizhnee Myagrozero, Eglov Isl., Rogachev Isl. Tachysphex pompiliformis (Panzer) – Volkostrov Isl. Apidae Hylaeus annulatus (L.) – Kizhi Isl., Rogachev Isl., Sennaya Guba Hylaeus bisinuatus Först. – Kizhi Isl., Kurgenitsy Hylaeus communis Nyl. – Kizhi Isl., Kurgenitsy *Hylaeus confusus Nyl. – Sennaya Guba, Tolvuya (Söderman & Leinonen 2003) Hylaeus gibbus Sounders – Rogachev Isl. Hylaeus nigritus (F.) – Vorobyi Lasioglossum albipes (F.) – Sennaya Guba *Lasioglossum fratellum (Perez) – Sennaya Guba (Söderman & Leinonen 2003) Lasioglossum leucopus (Kirby) – Sennaya Guba Halictus rubicundus Christ – Kizhi Isl. *Halictus tumulorum (L.) – Sennaya Guba, Tolvuya (Söderman & Leinonen 2003) *Nomada panzeri Lep. – Sennaya Guba (Söderman & Leinonen 2003) *Andrena cineraria L. – Sennaya Guba (Söderman & Leinonen 2003) Andrena intermedia Thoms. – Kosmozero *Andrena haemorrhoa F. – Sennaya Guba (Söderman & Leinonen 2003) *Andrena pilipes F. – Sennaya Guba (Söderman & Leinonen 2003) 302 Reports of the Finnish Environment Institute 40 | 2014 *Andrena ruicrus Nyl. – Tolvuya (Söderman & Leinonen 2003) *Andrena semilaevis Perez – Tolvuya (Söderman & Leinonen 2003) *Andrena subopaca Nyl. – Sennaya Guba (Söderman & Leinonen 2003) *Andrena tarsata Nyl. – Tolvuya (Söderman & Leinonen 2003) *Dufourea dentiventris (Nyl.) – Tolvuya (Söderman & Leinonen 2003) *Melitta haemorrhoidalis F. – Tolvuya (Söderman & Leinonen 2003) *Anthophora furcata Pz. – Tolvuya (Söderman & Leinonen 2003) Osmia nigriventris Zett. – Vorobyi Osmia pilicornis F.Smith – Vorobyi Megachile lagopoda L. – Nizhnee Myagrozero *Megachile lapponica Thoms. – Kuzaranda (Niemelä 1936) *Megachile versicolor F.Smith – Tolvuya (Söderman & Leinonen 2003) *Megachile willughbiella (Kirby) – Turastamozero, Shun’ga (Niemelä 1936) Macropis fulvipes (F.) – Myagrozero Bombus consobrinus Dahlb. – Oyatevschina *Bombus distinguendus F.Mor. – Kizhi Isl., Tolvuya (Söderman & Leinonen 2003) Bombus hypnorum L. – Sennaya Guba, Oyatevschina, Lipovitsy, Polya Bombus humilis Ill. – Kizhi Isl., Sennaya Guba, Rogachev Isl. Bombus jonellus Kirby – Eglov Isl., Oyatevschina Bombus lapidarius L. – Kizhi Isl., Vorobyi, Oyatevschina, Podyelniki, Sennaya Guba, Rogachev Isl. Bombus lucorum L. – Kizhi Isl., Vorobyi, Sennaya Guba, Nizhnee Myagrozero, Turastamozero, B.Lelikoskiy Isl., Lipovitsy, Polya, Uzkaya Salma, Tambitsy, Eglov Isl. Bombus pascuorum Scop. – Vorobyi, Oyatevschina, Nizhnee Myagrozero, Podyelniki, Turastamozero, Sennaya Guba, Lipovitsy, Eglov Isl. Bombus pratorum Scop. – Kizhi Isl., Oyatevschina, Podyelniki, Nizhnee Myagrozero, Turastamozero, Polya Bombus ruderarius Muller – Kizhi Isl. Bombus schrencki Morawitz, – Polya, Tambitsy, Turastamozero Bombus semenoviellus Skorikov – Lelikovo Bombus solstitialis Pz. – Vorobyi *Bombus soroeensis (F.) – Sennaya Guba, Tolvuya (Söderman & Leinonen 2003) Bombus sporadicus Nyl. – Polya, Lipovitsy, Uzkaya Salma, Turastamozero Bombus veteranus F. – Kizhi Isl., Vorobyi, Oyatevschina, Lelikovo, Sennaya Guba, Rogachev Isl. Bombus Psithyrus campestris Pz. – Oyatevschina Bombus Psithyrus bohemicus (Seidl.) – Sennaya Guba *Bombus Psithyrus quadricolor globosus Ev. – Sennaya Guba, Tolvuya (Pekkarinen et al. 1981) Bombus Psithyrus rupestris F. – Kizhi Isl., Sennaya Guba Bombus Psithyrus sylvestris (Lep.) – Sennaya Guba Gasteruptiidae Gasteruption assectator L. – Kizhi Isl. Gasteruption jaculator L. – Kizhi Isl. Evaniidae Brachygaster minuta Ol. – Lipovitsy, Bol. Lelikoskiy Isl., Nizhnee Myagrozero, Turastamozero, Uzkaya Salma Diapriidae *Zygota nigra (Thoms.) – Velikaya Guba (Hellén 1964) Heloridae Helorus striolatus Cameron – Myagrozero Proctotrupidae Disogmus areolator Hal. – Podyelniki Reports of the Finnish Environment Institute 40 | 2014 303 Phaneroserphus calcar (Hal.) – Eglov Isl. Proctotrupes gravidator L. – Vegoruksy Exallonyx (Eocodrus) sp. – Oyatevschina Scelionidae Sparasion ruipes Ruthe – Kizhi Isl. Aphidiidae Pauesia unilachni (Gahan) – Turastamozero Aphidius cingulatus (Ruthe) – Turastamozero Aphidius urticae Haliday – Lipovitsy Aphidius sp. – Turastamozero Lipolexis gracilis Först. – Turastamozero *Trioxys (Binodoxys) centaureae (Hal.) – Shun’ga (Mackauer 1968) Braconidae Chorebus trjapitzini Tobias – Kizhi Isl. Rogas circumscriptus Nees – Eglov Isl. Rogas geniculator Nees – Eglov Isl. Rogas medianus Thoms. – Podyelniki *Proterops nigripennis Wesm. – Tolvuya (Hellén 1958) Ichneumonidae Hybrizon buccatus Breb. – Vorobyi, Turastamozero, Nizhnee Myagrozero Endromopoda arundinator (F.) – Lelikovo, Ernitsky Isl. Endromopoda detrita (Holmgr.) – Lelikovo, Turastamozero, Eglov Isl., Rogachev Isl. Endromopoda phragmitidis (Perkins) – Ernitsky Isl. Endromopoda nigricoxis (Ulbricht) – Velikaya Niva Scambus inanis (Schrank) – Myagrozero Scambus nigricans Thoms. – Oyatevschina Gregopimpla inquisitor (Scop.) – Rogachev Isl. Ephialtes manifestator (L.) – Kizhi Isl. ?Dolichomitus dux Tscheck – Lipovitsy Perithous albicinctus (Grav.) – Turastamozero Apechtis capulifera (Kriecb.) – Turastamozero Apechtis compunctor L. – Vorobyi, Turastamozero, Shun’ga, Nizhnee Myagrozero, Eglov Isl., Rogachev Isl. Apechtis quadridentata Thoms. – Vorobyi, Turastamozero, Polya, Tipinitsy, Tambitsy Pimpla arctica Zett. – Kizhi Isl., Uzkaya Salma l., Turastamozero Pimpla contemplator (Müll.) – Velikaya Niva, Shun’ga Pimpla insignatoria (Grav.) – Kizhi Isl., Vorobyi, Kosmozero, Oyatevschina, Sennaya Guba, Podyelniki, Turastamozero, Uzkaya Salma Pimpla melanacrias Perkins – Kizhi Isl., Uzkaya Salma Pimpla ruipes (Miller) – Vorobyi, Kurgenitsy, Oyatevschina, Sennaya Guba,Turastamozero, Nizhnee Myagrozero, Eglov Isl., Rogachev Isl. Pimpla turionellae L. – Velikaya Niva, Vorobyi Itoplectis alternans (Grav.) – Oyatevschina, Turastamozero Acropimpla pictipes (Grav.) – Tolvuya Iseropus stercorator F. – Kizhi Isl., Vorobyi Zaglyptus multicolor Grav. – Vorobyi, Tipinitsy Zaglyptus varipes (Grav.) – Vorobyi, Sennaya Guba, Podyelniki, Uzkaya Salma ?Clistopyga canadensis Prov. – Vorobyi, Turastamozero Schizopyga lavifrons Holmgr. – Vorobyi Schizopyga frigida Cresson – Kosmozero Acrodactyla degener (Hal.) – Lipovitsy, Turastamozero Acrodactyla quadrisculpta (Grav.) – Lipovitsy, Turastamozero 304 Reports of the Finnish Environment Institute 40 | 2014 Polysphincta ruipes Grav. – Kurgenitsy, Yu. Oleny Isl., Sennaya Guba, Oyatevschina Zatypota albicoxa Walk. – Tambitsy Delomerista sp. – Oyatevschina Poemenia hectica Grav. – Podyelniki, Kazhma Megarhyssa rixator (Shellenberg) – Kizhi Isl. Rhyssella approximator (F.) – Kizhi Isl., Myagrozero, Uzkaya Salma Diplazon deletus (Thoms.) – Podyelniki Diplazon laetatorius F., Yu. Oleny Isl., Nizhnee Myagrozero, Podyelniki, Khvost Isl., Rogachev Isl., Tipinitsy Diplazon tetragonus Thunb. – Vorobyi Diplazon tibiatorius (Thunb.) – Velikaya Niva Diplazon scutatorius Teunissen – Eglov Isl. Homotropus megaspis Thoms. – Eglov Isl. Homotropus nigritarsus (Grav.) – Eglov Isl. Promethes sulcator (Grav.) – Kurgenitsy, Eglov Isl. Syrphophilus bizonarius Grav. – Kizhi Isl., Sennaya Guba Sussaba cognata (Holmgr.) – Lelikovo, Tolvuya Cylloceria caligata (Grav.) – Oyatevschina Cylloceria melancholica (Grav.) – Bol. Lelikoskiy Isl., Myagrozero, Turastamozero, Uzkaya Salma, Polya Rossemia longithorax Humala – Polya Orthocentrus patulus Holmgr. – Turastamozero Orthocentrus sannio Holmgr. – Turastamozero Orthocentrus spurius Grav. – Podyelniki, Volkostrov Isl., Oyatevschina, Turastamozero Orthocentrus winnertzii Först. – Myal› Isl., Turastamozero, Podyelniki Plectiscus impurator – Nizhnee Myagrozero, Uzkaya Salma, Turastamozero Picrostigeus recticauda (Thoms.) – Turastamozero, Bol. Lelikoskiy Isl. Stenomacrus celer (Holmgr.) – Bol. Klim. Isl., Polya Nerateles compressus – Turastamozero Gnathochorisis crassulus (Thoms.) – Oyatevschina, Podyelniki, Lipovitsy, Uzkaya Salma, Turastamozero Gnathochorisis dentifer Thoms. – Turastamozero, Kopanets lake. Aperileptus albipalpus (Grav.) – Turastamozero, Nizhnee Myagrozero Aperileptus infuscatus Först. – Turastamozero Aperileptus vanus Först. – Turastamozero Aperileptus cf. vanus Först. – Lipovitsy Eusterinx argutula Först. – Uzkaya Salma, Turastamozero, Tipinitsy Eusterinx inaequalis Först. – Nizhnee Myagrozero Eusterinx tenuicincta Först. – Vorobyi Symplecis bicingulata Grav. – Turastamozero Symplecis cf. clipeator Lundbeck – Vorobyi Hemiphanes erratum Humala – Tipinitsy Megastylus cruentator Schiødte – Podyelniki Megastylus orbitator Schiødte – Volkostrov Isl., Podyelniki, Uzkaya Salma, Turastamozero Megastylus pectoralis – Lipovitsy Helictes borealis Holmgr. – Turastamozero, Vorobyi Helictes erythrostoma Gmelin – Vorobyi Proclitus ardentis Rossem – Myagrozero, Turastamozero Proclitus comes Hal. – Lipovitsy, Turastamozero Proclitus praetor Hal. – Vorobyi, Eglov Isl. Nizhnee Myagrozero, Turastamozero Dialipsis exilis Först. – Turastamozero Reports of the Finnish Environment Institute 40 | 2014 305 Plectiscidea aquilonia Humala – Turastamozero Plectiscidea collaris Grav. – Lipovitsy, Turastamozero, Tipinitsy Plectiscidea communis Först. – Lipovitsy, Tipinitsy Plectiscidea posticata Först. – Myagrozero, Turastamozero, Tipinitsy Plectiscidea zonata (Grav.) – Velikaya Niva Pantisarthrus lubricus Först. – Turastamozero Pantisarthrus luridus Först. – Turastamozero Lycorina triangulifera Holmgr. – Sennaya Guba Coleocentrus caligatus Grav. – Eglov Isl. Coleocentrus exareolatus Kriechb. – Lipovitsy Coleocentrus excitator Poda – Kosmozero, Vikshezero Arotes albicinctus (Grav.) – Myagrozero Ischnocerus rusticus Geoffr. – Kizhi Isl., Vorobyi, Podyelniki Odontocolon dentipes Gmel. – Vorobyi *Gelis agilis (F.) – Velikaya Niva (Hellén 1970) *Gelis discedens (Först.) – Velikaya Niva (Hellén 1970) Ecthrus reluctator L. – Velikaya Niva Theroscopus hemipterus (F.) – Turastamozero Mesoleptus distinctus (Först.) – Eglov Isl. Glyphicnemis proligator (F.) – Tolvuya Pleolophus basizonus (Grav.) – Uzkaya Salma Schenkia graminicola (Grav.) – Velikaya Niva,Velikaya Niva Cubocephalus femoralis (Thoms.) – Velikaya Niva Cubocephalus associator Thunb. – Tolvuya, Velikaya Niva, Oyatevschina Megaplectes monticola (Grav.) – Unitsa Sphecophaga vesparum Curtis – Vorobyi Acroricnus stylator Thunb. – Vorobyi ?Aptesis improba (Grav.) – Tolvuya Ischnus migrator (F.) – Vorobyi, Velikaya Niva Glypta caudata Thoms. – Kizhi Isl. Glypta ceratites Grav. – Eglov Isl., Podyelniki Glypta cylindrator F. – Vorobyi, Turastamozero, Podyelniki, Oyatevschina, Eglov Isl., Rogachev Isl. Glypta extincta Ratz. – Velikaya Niva Glypta heterocera Thoms. – Kizhi Isl. Glypta mensurator F. – Turastamozero, Nizhnee Myagrozero Lissonota lineolaris (Gmel.) – Kurgenitsy, Yu. Oleny Isl., Oyatevschina, Rogachev Isl. Lissonota nitida (Grav.) – Velikaya Niva Lissonota punctiventris Thoms. – Velikaya Niva Alloplasta piceator (Thunb.) – Kizhi Isl., Eglov Isl. Cryptopimpla caligata (Grav.) – Vorobyi, Kosmozero Cryptopimpla errabunda (Grav.) – Podyelniki, Velikaya Niva Exetastes laevigator (Villers) – Shun’ga Adelognathus brevicornis Holmgr. – Lydskoi Isl., Sennaya Guba ?Adelognathus dealbatus Kasp. – Nizhnee Myagrozero Adelognathus dorsalis (Grav.) – Vorobyi, Eglov Isl., Podyelniki Adelognathus pilosus Thoms. – Eglov Isl. Idiogramma euryops Schmied. – Velikaya Niva Phytodietus gelitorius Thunb. – Vorobyi, Turastamozero Dyspetes luteomarginatus Hab. – Tipinitsy, Turastamozero Cosmoconus ceratophorus Thoms. – Podyelniki Cosmoconus elongator F. – Zubovo, Nizhnee Myagrozero 306 Reports of the Finnish Environment Institute 40 | 2014 Cosmoconus hinzi Kasp. – Vorobyi, Kosmozero Cosmoconus nigriventris Kasp. – Vorobyi, Podyelniki Polyblastus nanus Kasp. – Kurgenitsy Polyblastus pinguis Grav. – Vorobyi Polyblastus subalpinus Holmgr. – Turastamozero Polyblastus tener Haberm. – Lyudskoi Isl. Polyblastus varitarsus (Grav.) – Eglov Isl., Polya, Tipinitsy, B.Lelikoskiy Isl., Myal Isl. Polyblastus wahlbergi Holmgr. – Turastamozero Ctenochira gilvipes (Holmgr.) – Eglov Isl. Ctenochira marginata Holmgr. – B.Lelikoskiy Isl., Kopanets lake Ctenochira propinqua Grav. – Vorobyi, B.Lelikoskiy Isl., Sennaya Guba Ctenochira xanthopyga (Holmgr.) – Eglov Isl. Tryphon bidentatus Stephens – Vorobyi, Kurgenitsy, Lelikovo Tryphon exclamationis Grav. – Kurgenitsy Tryphon obtusator (Thunb.) – Kizhi Isl., Eglov Isl., Ernitsky Isl., Lyudskoi Isl. Tryphon thomsoni Roman – Kurgenitsy Erromenus plebejus (Woldst.) – Lelikovo Cycasis rubiginosa Grav. – Vorobyi Kristotomus laetus Grav. – Vorobyi Exyston sponsorius (F.) – Vorobyi, Oyatevschina Eridolius auriluus (Hal.) – Kurgenitsy Eridolius ruilabris (Holmgr.) – Oyatevschina Eridolius rufonotatus (Holmgr.) – Oyatevschina Eridolius schiodtei Holmgr. – Kosmozero Smicroplectrus excisus Kerrich – Lelikovo Smicroplectrus perkinsi Kerrich – Vorobyi Exenterus amictorius Panz. – Vorobyi Excavarus apiarius (Grav.) – Vorobyi Ctenopelma lapponicum Holmgr. – Rogachev Isl. Ctenopelma nigrum Holmgr. – Velikaya Niva (Hellén 1948) Ctenopelma tomentosum Desv. – Oyatevschina Xenoschesis ustulata (Desv.) – Podyelniki, Lipovitsy, Velikaya Niva Pion fortipes Grav. – Vorobyi, Kizhi Isl., Rogachev Isl. Pion nigripes Schiødte =crassipes Holmgr. – Kizhi Isl. Scolobates auriculatus F. – Lipovitsy Opheltes glaucopterus L. – Kurgenitsy, Vorobyi, Lipovitsy, Vegoruksy Perilissus rufoniger (Grav.) – Oyatevschina Perilissus variator (Müll.) – Vorobyi, Rogachev Isl. *Phobetes leptocerus (Grav.) – Velikaya Niva (Hellén1961) Hypamblys albopictus (Grav.) – Velikaya Niva Rhaestus lativentris Holmgr. – Vorobyi Rhaestus ophthalmicus Holmgr. – Vorobyi Rhaestus ruipes Holmgr. – Vorobyi ?Alexeter multicolor (Grav.) – Kosmozero Sympherta jactator (Thunb.) – Podyelniki Sympherta obligator (Thunb.) – Vorobyi, Velikaya Niva Mesoleius aulicus Grav. – Polya Anisotacrus bipunctatus (Grav.) – Oyatevschina Hadrodactylus tiphae (Geoffr.) – Tolvuya, Kizhi Isl. Oxytorus luridator (Grav.) – Vorobyi, Turastamozero, Nizhnee Myagrozero, Myagrozero Collyria trichophthalma Thoms. – Lelikovo, Sennaya Guba, Ernitsky Isl., Eglov Isl., Rogachev Isl. Reports of the Finnish Environment Institute 40 | 2014 307 Probles microcephalus Grav. – Kurgenitsy Tersilochus caudatus (Holmgr.) – Vorobyi Barycnemis bellator (Müll.) – Vorobyi Charops cantator (DeGeer) – Eglov Isl. Casinaria sp. – Podyelniki Tranosemella coxalis Brischke – Kurgenitsy *Dusona stenogaster (Först.) – Velikaya Niva (Hellén 1962) *Dusona stragifex (Först.) – Velikaya Niva (Hellén 1937) ?Diadegma rectiicator Aubert – Kosmozero *Enicospilus undulatus (Grav.) – Kizhi Isl. (Hellén 1926) Cidaphus areolatus Boie – Podyelniki Therion circumlexum L. – Turastamozero Heteropelma amictum (F.) – Tipinitsy Aphanistes ruicornis Grav. – Vorobyi, Eglov Isl. Camposcopus canaliculatus Ratz. – B.Lelikoskiy Isl. Agrypon lexorium Thunb. – Velikaya Niva, Podyelniki, Turastamozero Chorinaeus brevicalcar Thoms. – Podyelniki Exochus prosopius Grav. – Sennaya Guba Triclistus pallipes Holmgr. – Eglov Isl. Alomya debellator F. – Kizhi Isl., Turastamozero, Kosmozero, Podyelniki, Eglov Isl., Rogachev Isl. Alomya pygmaea Heinrich – Kurgenitsy, Vorobyi, Sennaya Guba, Radkol‘e, Tolvuya (Hellén 1951), Eglov Isl., Rogachev Isl. Misetus oculatus Wesm. – Vorobyi, Turastamozero, Uzkaya Salma, Polya Heterischnus debilis Grav. – Podyelniki Platylabus vibratorius Thunb. – Vorobyi Platylabus heteromallus (Berthouemieu) – Vikshezero Pseudoplatylabus violentus (Grav.) – Kurgenitsy Acolobus albimanus (Grav.) – Megostrov Isl. Protichneumon similatorius (F.) – Kizhi Isl., Vorobyi, Oyatevschina Aoplus castaneus (Grav.) – Vorobyi Cratichneumon jocularis (Wesm.) – Ernitsky Isl. Cratichneumon ruifrons (Grav.) – Eglov Isl. Cratichneumon sicarius (Grav.) – Kizhi Isl. Cratichneumon viator (Scop.) – Kizhi Isl., Velikaya Guba, Oyatevschina, Vorobyi, Eglov Isl. Ctenichneumon divisorius (Grav.) – Vorobyi Ctenichneumon inspector (Wesm.) – Vorobyi Syspasis scutellator (Grav.) – Vikshezero, Eglov Isl. *Hoplismenus bidentatus (Gmel.) – Kizhi Isl. (Hellén 1936) Homotherus locutor (Thunb.) – Ernitsky Isl. Homotherus varipes (Grav.) – Vorobyi *Hybophorellus injucundus (Wesm.) – Velikaya Niva (Hellén 1951) Anisopygus pseudonymus (Wesm.) – Rogachev Isl. Hepiopelmus melanogaster (Gmelin) – Vorobyi Ichneumon balteatus Wesm. – Kurgenitsy Ichneumon caedator Grav. – Lambaznik Isl. Ichneumon cessator Müller – Velikaya Niva Ichneumon gracilicornis Grav. – Vorobyi, Myal Isl. Ichneumon oblongus Schrank – Vikshezero Ichneumon primatorius Först. – Eglov Isl. *Eurylabus tristis (Grav.) – Shun’ga (Hellén 1951) Amblyjoppa proteus Christ – Vorobyi, Bol. Lelikoskiy Isl., Turastamozero 308 Reports of the Finnish Environment Institute 40 | 2014 Limerodops elongatus (Brischke) – Vikshezero, Kizhi Isl. Sycaonia foersteri (Wesm.) – Ernitsky Isl. Virgichneumon albosignatus (Grav.) – Vorobyi *Virgichneumon faunus (Grav.) – Kuzaranda (Ranin 1979) Vulgichneumon deceptor (Scop.) – Ernitsky Isl. Vulgichneumon suavis (Grav.) – Ernitsky Isl., Lelikovo DIPTERA Trichoceridae Trichocera rufescens Edwards – Polya, Tambitsy, Tipinitsy Pediciidae Ula bolitophila Loew – Velikaya Niva Ula sylvatica Meigen – Polya, Tipinitsy Pedicia rivosa L. – Lipovitsy, Tambitsy, Tipinitsy, Turastamozero Tricyphona unicolor Schummel – Ernitskiy Isl., Kizhi Isl., Lelikovo Limoniidae Elephantomyia krivosheinae Savtshenko – Myal’ Isl. Helius longirostris Meigen – Ernitskiy Isl., Klimenicy, Lelikovo, Polya, Sennaya Guba, Shunevskiy Isl., Uzkaya Salma, Vikshezero Austrolimnophila unica Osten-Sacken – Paleostrov Isl., Tolvuya Idioptera linnei Oosterbroek – Kizhi Isl., Vikshezero Idioptera pulchella Meigen – Vikshezero, Volkostrov Isl. Limnophila pictipennis Meigen – Lelikovo Neolimnomyia nemoralis Meigen – Lipovitsy, Lyudskoi Isl., Paleostrov Isl., Rogachev Isl., Sennaya Guba Euphylidorea phaeostigma Schummel – Podyelniki, Polya Phylidorea abdominalis Staeger – Verkhnee Myagrozero Phylidorea ferruginea Meigen – Ernitskiy Isl., Vorobyi Phylidorea fulvonervosa Schummel – Bol. Lelikovskiy Isl. Phylidorea longicornis Schummel – Klimenicy, Lipovitsy, Shunevskiy Isl., Verkhnee Myagrozero, Vikshezero Phylidorea squalens Zetterstedt – Lipovitsy, Verkhnee Myagrozero Pilaria discicollis Meigen – Klimenicy, Kurgenitsy, Podyelniki Erioptera lutea Meigen – Vegoruksy Erioptera nielseni de Meijere – Uzkaya Salma Molophilus ater Meigen – Tolvuya Molophilus bihamatus de Meijere – Klimenicy Molophilus lavus Goetghebuer – Lipovitsy Molophilus griseus Meigen – Kurgenitsy Molophilus medius de Meijere – Lipovitsy Molophilus ochraceus Meigen – Vikshezero Ormosia depilata Edwards – Kizhi Isl., Lelikovo Ormosia ruicauda Zetterstedt – Bol. Lelikovskiy Isl., Klimenicy, Vikshezero Ormosia staegeriana Alexander – Klimenicy, Lipovitsy Rhypholophus varius Meigen – Lipovitsy Gnophomyia viridipennis Gimmerthal – Bol. Lelikovskiy Isl., Kopanets lake, Lipovitsy Neolimonia dumetorum Meigen – Bol. Lelikovskiy Isl., Myagrozero Dicranomyia distendens Lundström – Eglov Isl. Dicranomyia modesta Meigen – Klimenicy, Paleostrov Isl., Polya, Vavlok Isl. Discobola annulata L. – Turastamozero Discobola caesarea Osten-Sacken – Bol. Lelikovskiy Isl. Limonia badia Walker – Polya, Tipinitsy Reports of the Finnish Environment Institute 40 | 2014 309 Limonia lavipes Fabricius – Klimenicy, Shunevskiy Isl., Vorobyi Limonia macrostigma Schummel – Turastamozero, Yu. Oleny Isl. Limonia phragmitidis Schrank – Verkhnee Myagrozero Limonia sylvicola Schummel – Lipovitsy Limonia trivittata Schummel – Kurgenitsy, Volkostrov Isl. Metalimnobia bifasciata Schrank – Bol. Lelikovskiy Isl., Khvost Isl., Lipovitsy, Polya, Turastamozero, Uzkaya Salma, Vorobyi, Yu. Oleny Isl. Metalimnobia quadrimaculata L. – Turastamozero, Verkhnee Myagrozero, Vorobyi Metalimnobia quadrinotata Meigen – Bol. Lelikovskiy Isl., Turastamozero, Verkhnee Myagrozero, Yu. Oleny Isl. Metalimnobia zetterstedti Tjeder – Lipovitsy Rhipidia maculata Meigen – Klimenicy Rhipidia uniseriata Schiner – Lyudskoi Isl. Cylindrotomidae Cylindrotoma distinctissima Meigen – Polya, Vorobyi Diogma glabrata Meigen – Lipovitsy Tipulidae Tipula afinis Schummel – Eglov Isl., Paleostrov Isl. Tipula autumnalis Loew – Vorobyi Tipula circumdata Siebke – Tambitsy Tipula confusa Van der Wulp – Vorobyi Tipula fascipennis Meigen – Kazhma, Vavlok Isl. Tipula fulvipennis fulvipennis DeGeer – Klimenicy Tipula humilis Staeger – Bol. Lelikovskiy Isl., Kizhi Isl., Kosmozero, Podyelniki Tipula irrorata Macquart – Ernitskiy Isl., Tolvuya Tipula laetabilis Zetterstedt – Podyelniki Tipula limitata Schummel – Kosmozero Tipula luna Westhoff – Eglov Isl. Tipula nubeculosa Meigen – Oyatevschina Tipula paludosa Meigen – Vegoruksy Tipula pruinosa pruinosa Wiedemann – Vikshezero Tipula pseudovariipennis Czizek – Kizhi Isl. Tipula scripta Meigen – Bol. Lelikovskiy Isl., Lipovitsy Tipula variicornis Schummel – Lipovitsy, Polya, Vorobyi Tipula varipennis Meigen – Kizhi Isl., Tolvuya, Vorobyi Prionocera turcica Fabricius – Kizhi Isl., Klimenicy Nephrotoma analis Schummel – Vikshezero Nephrotoma cornicina L. – Kosmozero Nephrotoma pratensis L. – Shun’ga Dictenidia bimaculata L. – Rogachev Isl., Turastamozero, Verkhnee Myagrozero Tanyptera atrata L. – Vorobyi Ptychopteridae Ptychoptera minuta Tonnoir – Klimenicy Psychodidae Clytocerus ocellaris Meigen – Vorobyi Dixidae Dixella aestivalis Meigen – Khvost Isl., Vikshezero Dixella borealis Martini – Tambitsy Dixella hyperborea Bergroth – Shunevskiy Isl. Culicidae Anopheles maculipennis Meigen – Kizhi Isl. Culiseta alaskaensis Ludlow – Shunevskiy Isl. 310 Reports of the Finnish Environment Institute 40 | 2014 Culiseta fumipennis Stephens – Lipovitsy, Polya, Uzkaya Salma Culiseta ochroptera Peus – Vorobyi Coquillettidia richiardii Ficalbi – Uzkaya Salma ? Aedes annulipes Meigen – Vikshezero Aedes behningi Martini – Ernitskiy Isl. Aedes cataphyla Dyar – Ernitskiy Isl., Lelikovo, Sennaya Guba Aedes cinereus Meigen – Verkhnee Myagrozero, Vikshezero Aedes communis DeGeer – Ernitskiy Isl. Aedes diantaeus Howard, Dyar et Knab – Ernitskiy Isl., Lipovitsy, Shunevskiy Isl., Vikshezero Aedes excrucians Walker – Ernitskiy Isl., Lelikovo, Shunevskiy Isl., Vikshezero Aedes intrudens Dyar – Lyudskoi Isl Aedes pionips Dyar – Eglov Isl., Vikshezero Aedes punctor Kirby – Polya, Vikshezero Culex territans Walker – Polya, Verkhnee Myagrozero Ceratopogonidae Clinohelea unimaculata Macquart – Klimenicy Anisopodidae Sylvicola cinctus Fabricius – Turastamozero Sylvicola punctatus Fabricius – Vorobyi Scatopsidae Apiloscatopse lavicollis Meigen – Tipinitsy Bibionidae Dilophus femoratus Meigen – Eglov Isl., Kuzaranda, Paleostrov Isl., Rogachev Isl., Vikshezero Bibio clavipes Meigen – Myagrozero Bibio nigriventris Haliday – Eglov Isl., Ernitskiy Isl., Kainos Isl., Klimenicy, Kuivakhda Isl., Lelikovo, Lipovitsy, Lyudskoi Isl., Myal’ Isl., Paleostrov Isl., Polya, Sennaya Guba, Tipinitsy, Vikshezero, Yu. Oleny Isl. Bibio pomonae Fabricius – Vorobyi Ditomyiidae Symmerus nobilis Lackschewitz – Kosmozero Diadocidiidae Diadocidia ferruginosa Meigen – Bol. Lelikovskiy Isl., Kizhi Isl., Lyudskoi Isl., Myal’ Isl., Polya, Shunevskiy Isl., Tambitsy, Tipinitsy, Turastamozero, Vavlok Isl., Verkhnee Myagrozero, Vikshezero, Vorobyi Diadocidia spinosula Tollet – Lyudskoi Isl., Tipinitsy Mycetophilidae Mycomya afinis Staeger – Tambitsy, Tipinitsy, Turastamozero Mycomya annulata Meigen – Klimenicy, Lipovitsy, Myagrozero, Polya, Tambitsy, Tipinitsy, Turastamozero Mycomya brunnea Dziedzicki – Tipinitsy Mycomya cinerascens Macquart – Myal’ Isl., Tipinitsy Mycomya collini Edwards – Paleostrov Isl. Mycomya egregia Dziedzicki – Lyudskoi Isl. Mycomya festivalis Väisänen – Klimenicy Mycomya imbriata Meigen – Turastamozero Mycomya lavicollis Zetterstedt – Podyelniki, Uzkaya Salma Mycomya griseovittata Zetterstedt – Vorobyi Mycomya nigricornis Zetterstedt – Myagrozero, Vorobyi Mycomya nitida Zetterstedt – Klimenicy, Kuivakhda Isl., Lelikovo, Lyudskoi Isl., Paleostrov Isl., Velikaya Niva, Vikshezero, Yu. Oleny Isl. Reports of the Finnish Environment Institute 40 | 2014 311 Mycomya paradentata Väisänen – Polya, Tambitsy, Tipinitsy, Turastamozero Mycomya parva Dziedzicki – Lyudskoi Isl. Mycomya penicillata Dziedzicki – Myagrozero, Turastamozero, Vorobyi Mycomya permixta Väisänen – Lipovitsy, Myagrozero, Polya, Tambitsy, Tipinitsy, Turastamozero Mycomya prominens Lundström – Paleostrov Isl. Mycomya pseudoapicalis Landrock – Klimenicy Mycomya ruicollis Zetterstedt – Klimenicy, Vikshezero Mycomya shermani Garrett – Myagrozero, Polya, Tambitsy, Tipinitsy Mycomya siebecki Landrock – Tambitsy, Tipinitsy Mycomya sp4 (cf. penicillata) – Turastamozero Mycomya trilineata Zetterstedt – Bol. Lelikovskiy Isl., Kurgenitsy, Podyelniki, Turastamozero, Verkhnee Myagrozero, Volkostrov Isl. Mycomya trivittata Zetterstedt – Klimenicy, Lyudskoi Isl., Paleostrov Isl., Tipinitsy, Vikshezero Mycomya wankowiczii Dziedzicki – Lyudskoi Isl., Turastamozero, Yu. Oleny Isl. Mycomya winnertzi Dziedzicki – Paleostrov Isl. Neoempheria pictipennis Haliday – Tipinitsy Neoempheria tuomikoskii Väisänen – Vikshezero Acnemia angusta A. Zaitzev – Kopanets lake, Vikshezero Acnemia nitidicollis Meigen – Bol. Lelikovskiy Isl., Kopanets lake, Kosmozero, Kurgenitsy, Lyudskoi Isl., Oyatevschina, Podyelniki, Polya, Turastamozero, Uzkaya Salma, Velikaya Niva, Vorobyi, Voynavolok Allocotocera pulchella Curtis – Eglov Isl., Klimenicy, Oyatevschina, Turastamozero, Uzkaya Salma Leptomorphus subforcipatus A. Zaitzev & Ševcík – Vorobyi Leptomorphus walkeri Curtis – Kopanets lake Megalopelma nigroclavatum Strobl – Lyudskoi Isl. Monoclona ruilatera Walker – Bol. Lelikovskiy Isl., Kizhi Isl., Kurgenitsy, Oyatevschina, Turastamozero, Vikshezero, Volkostrov Isl. Neuratelia nemoralis Meigen – Lelikovo, Velikaya Niva Phthinia humilis Winnertz – Turastamozero Polylepta borealis Lundström – Kopanets lake Polylepta guttiventris Zetterstedt – Klimenicy, Lipovitsy, Polya, Shunevskiy Isl., Tambitsy, Tipinitsy, Turastamozero, Volkostrov Isl., Yu. Oleny Isl. Sciophila fenestella Curtis – Lyudskoi Isl., Oyatevschina, Podyelniki, Uzkaya Salma, Vikshezero, Vorobyi Sciophila geniculata Zetterstedt – Klimenicy, Oyatevschina Sciophila hirta Meigen – Podyelniki Sciophila nigronitida Landrock – Kizhi Isl., Vorobyi Sciophila persubtilis Polevoi – Oyatevschina, Turastamozero Sciophila thoracica Staeger – Eglov Isl., Ernitskiy Isl., Turastamozero, Vorobyi Syntemna nitidula Edwards – Ernitskiy Isl. Syntemna relicta Lundström – Vikshezero Syntemna setigera Lundström – Lyudskoi Isl. Syntemna stylatoides A. Zaitzev – Lyudskoi Isl., Vorobyi Apolephthisa subincana Curtis – Lyudskoi Isl., Podyelniki, Turastamozero, Velikaya Niva Boletina basalis Meigen – Ernitskiy Isl., Kizhi Isl., Kuivakhda Isl., Lyudskoi Isl., Myal’ Isl., Oyatevschina, Tolvuya, Velikaya Niva, Vorobyi Boletina cincticornis Walker – Kizhi Isl., Oyatevschina, Velikaya Niva, Vorobyi Boletina dissipata Plassmann – Klimenicy Boletina edwardsi Chandler – Turastamozero 312 Reports of the Finnish Environment Institute 40 | 2014 Boletina gripha Dziedzicki – Klimenicy, Lyudskoi Isl., Oyatevschina, Tipinitsy, Tolvuya, Turastamozero, Velikaya Niva, Verkhnee Myagrozero, Vikshezero, Volkostrov Isl., Vorobyi Boletina griphoides Edwards – Oyatevschina, Turastamozero ? Boletina gusakovae A. Zaitzev – Tambitsy, Tipinitsy, Turastamozero Boletina kivachiana Polevoi & Hedmark – Turastamozero Boletina lundstroemi Landrock – Turastamozero Boletina moravica Landrock – Turastamozero, Verkhnee Myagrozero Boletina nigricans Dziedzicki – Kizhi Isl., Klimenicy, Oyatevschina Boletina nigrofusca Dziedzicki – Klimenicy Boletina nitida Grzegorzek – Kainos Isl., Turastamozero Boletina pinusia Maximova – Ernitskiy Isl. Boletina populina Polevoi – Klimenicy, Oyatevschina, Turastamozero, Velikaya Niva, Vorobyi Boletina sciarina Staeger – Kizhi Isl., Turastamozero Boletina silvatica Dziedzicki – Turastamozero Boletina subtriangularis Polevoi & Hedmark – Turastamozero Boletina takagii Sasakava et Kimura – Turastamozero Boletina triangularis Polevoi – Oyatevschina Boletina trivittata Meigen – Klimenicy, Lipovitsy, Myagrozero, Polya, Tambitsy, Tipinitsy Boletina villosa Landrock – Tambitsy Coelosia tenella Zetterstedt – Bol. Lelikovskiy Isl., Turastamozero Coelosia truncata Lundström – Vorobyi Dziedzickia marginata Dziedzicki – Myagrozero Gnoriste apicalis Meigen – Kizhi Isl. Gnoriste bilineata Zetterstedt – Klimenicy Grzegorzeckia collaris Meigen – Oyatevschina Palaeodocosia vittata Coquillett – Bol. Lelikovskiy Isl., Lipovitsy, Tipinitsy Saigusaia laviventris Strobl – Kopanets lake, Lipovitsy Synapha fasciata Meigen – Eglov Isl., Ernitskiy Isl., Khvost Isl. Synapha vitripennis Meigen – Kainos Isl., Lipovitsy Docosia gilvipes Walker – Lyudskoi Isl. Ectrepesthoneura colyeri Chandler – Myagrozero, Uzkaya Salma, Vikshezero, Vorobyi Ectrepesthoneura hirta Winnertz – Eglov Isl., Kizhi Isl., Lyudskoi Isl., Oyatevschina, Podyelniki, Vikshezero, Vorobyi Ectrepesthoneura ovata Ostroverkhova – Uzkaya Salma Ectrepesthoneura pubescens Zetterstedt – Oyatevschina, Velikaya Niva, Vikshezero, Vorobyi Ectrepesthoneura referta Plassmann – Velikaya Niva Leia bilineata Winnertz – Volkostrov Isl. Leia cylindrica Winnertz – Vorobyi Leia picta Meigen – Polya Leia subfasciata Meigen – Ernitskiy Isl., Lipovitsy, Lyudskoi Isl., Oyatevschina, Vikshezero Leia winthemi Lehmann – Uzkaya Salma, Volkostrov Isl. Rondaniella dimidiata Meigen – Turastamozero Tetragoneura sylvatica Curtis – Eglov Isl. Dynatosoma fuscicorne Meigen – Kopanets lake, Podyelniki, Turastamozero Dynatosoma nigromaculatum Lundström – Turastamozero Dynatosoma reciprocum Walker – Vikshezero Dynatosoma thoracicum (s. Zaitzev) – Paleostrov Isl., Uzkaya Salma Epicypta aterrima Zetterstedt – Ernitskiy Isl., Verkhnee Myagrozero Mycetophila abiecta Laštovka – Bol. Lelikovskiy Isl., Vikshezero Reports of the Finnish Environment Institute 40 | 2014 313 Mycetophila alea Laffoon – Tambitsy, Tipinitsy, Turastamozero, Vorobyi Mycetophila attonsa Laffoon – Yu. Oleny Isl. Mycetophila blanda Winnertz – Myagrozero, Tipinitsy, Vorobyi Mycetophila brevitarsata Laštovka – Uzkaya Salma Mycetophila conluens Dziedzicki – Turastamozero, Vorobyi Mycetophila curviseta Lundström – Uzkaya Salma Mycetophila delexa Chandler – Lipovitsy, Turastamozero Mycetophila estonica Kurina – Tipinitsy Mycetophila fungorum DeGeer – Bol. Lelikovskiy Isl., Klimenicy, Kosmozero, Kurgenitsy, Paleostrov Isl., Polya, Tipinitsy, Turastamozero, Vikshezero, Vorobyi Mycetophila gemerensis Ševčík & Kurina – Vorobyi Mycetophila gibbula Edwards – Turastamozero, Yu. Oleny Isl. Mycetophila hetschkoi Landrock – Lipovitsy, Turastamozero Mycetophila ichneumonea Say – Bol. Lelikovskiy Isl., Klimenicy, Kosmozero, Lipovitsy, Paleostrov Isl., Podyelniki, Tambitsy, Tipinitsy, Turastamozero, Verkhnee Myagrozero, Volkostrov Isl., Vorobyi Mycetophila laeta Walker – Tipinitsy Mycetophila lubomirskii Dziedzicki – Tambitsy Mycetophila luctuosa Meigen – Klimenicy, Lipovitsy, Myagrozero, Tambitsy, Turastamozero, Vavlok Isl., Yu. Oleny Isl. Mycetophila magnicauda Strobl – Turastamozero Mycetophila morosa Winnertz – Turastamozero Mycetophila nigrofusca Dziedzicki – Kopanets lake, Turastamozero Mycetophila ocellus Walker – Klimenicy, Turastamozero, Verkhnee Myagrozero Mycetophila perpallida Chandler – Myagrozero, Paleostrov Isl., Polya, Tipinitsy, Turastamozero Mycetophila schnabli Dziedzicki – Lipovitsy, Polya, Tipinitsy Mycetophila signata Meigen – Lipovitsy Mycetophila signatoides Dziedzicki – Lyudskoi Isl., Myagrozero, Polya, Tambitsy, Tipinitsy Mycetophila sordida Van der Wulp – Tambitsy Mycetophila stolida Walker – Lyudskoi Isl. Mycetophila stricklandi Laffoon – Bol. Lelikovskiy Isl., Turastamozero Mycetophila strigata Staeger – Vorobyi Mycetophila strigatoides Landrock – Nizhneje Myagrozero, Turastamozero, Vikshezero Mycetophila strobli Laštovka – Klimenicy, Kosmozero, Lyudskoi Isl., Tipinitsy, Turastamozero, Vikshezero Mycetophila stylata Dziedzicki – Bol. Lelikovskiy Isl. Mycetophila sublunata A. Zaitzev – Klimenicy, Paleostrov Isl., Tipinitsy, Verkhnee Myagrozero Mycetophila subsigillata A. Zaitzev – Bol. Lelikovskiy Isl., Paleostrov Isl., Tambitsy, Tipinitsy, Turastamozero Mycetophila triangulata Dziedzicki – Vorobyi Mycetophila trinotata Staeger – Kurgenitsy, Turastamozero, Vorobyi Mycetophila uschaica Subbotina & Maksimova – Polya Phronia braueri Dziedzicki – Turastamozero, Volkostrov Isl. Phronia caliginosa Dziedzicki – Polya, Tambitsy Phronia cinerascens Winnertz – Turastamozero, Vikshezero Phronia disgrega Dziedzicki – Lyudskoi Isl., Myagrozero, Vikshezero Phronia egregia Dziedzicki – Tipinitsy, Turastamozero Phronia exigua Zetterstedt – Turastamozero Phronia lavipes Winnertz – Tambitsy 314 Reports of the Finnish Environment Institute 40 | 2014 Phronia forcipata Winnertz – Bol. Lelikovskiy Isl., Lyudskoi Isl., Oyatevschina, Volkostrov Isl Phronia forcipula Winnertz – Klimenicy Phronia gagnei Chandler – Bol. Lelikovskiy Isl., Klimenicy Phronia maculata Dziedzicki – Lipovitsy, Tipinitsy, Uzkaya Salma Phronia nigricornis Zetterstedt – Uzkaya Salma Phronia nigripalpis Lundström – Kizhi Isl., Kopanets lake, Vikshezero, Volkostrov Isl., Vorobyi Phronia nitidiventris Van der Wulp – Tambitsy, Turastamozero Phronia notata Dziedzicki – Turastamozero Phronia persimilis Hackman – Khvost Isl., Turastamozero, Vikshezero Phronia siebeckii Dziedzicki – Uzkaya Salma Phronia signata Winnertz – Tambitsy Phronia strenua Winnertz – Bol. Lelikovskiy Isl., Klimenicy, Lelikovo, Shunevskiy Isl., Turastamozero, Volkostrov Isl., Vorobyi Phronia taczanowskii Dziedzicki – Turastamozero Phronia tenuis Winnertz – Polya, Tambitsy, Yu. Oleny Isl. Phronia vitrea Plassmann – Polya Phronia willistoni Dziedzicki – Bol. Lelikovskiy Isl. Platurocypta punctum Stannius – Bol. Lelikovskiy Isl., Klimenicy, Lyudskoi Isl., Turastamozero, Vorobyi Platurocypta testata Edwards – Bol. Lelikovskiy Isl., Kizhi Isl., Kosmozero, Kurgenitsy, Tipinitsy, Turastamozero, Vorobyi, Yu. Oleny Isl. Sceptonia concolor Winnertz – Lipovitsy Sceptonia costata Van der Wulp – Myagrozero, Turastamozero Sceptonia demeijerei Bechev – Vorobyi Sceptonia lavipuncta Edwards – Ernitskiy Isl. Sceptonia fumipes Edwards – Turastamozero, Vorobyi Sceptonia fuscipalpis Edwards – Tambitsy, Turastamozero, Vikshezero Sceptonia hamata Ševčík – Bol. Lelikovskiy Isl., Turastamozero Sceptonia longisetosa Ševčík – Oyatevschina Sceptonia membranacea Edwards – Klimenicy, Polya Sceptonia nigra Meigen – Bol. Lelikovskiy Isl., Ernitskiy Isl., Kuivakhda Isl., Turastamozero, Volkostrov Isl., Vorobyi, Yu. Oleny Isl. Sceptonia pilosa Bukowski – Bol. Lelikovskiy Isl., Kuivakhda Isl., Lyudskoi Isl., Turastamozero Sceptonia regni Chandler – Turastamozero Trichonta atricauda Zetterstedt – Vikshezero Trichonta concinna Gagné – Tambitsy Trichonta conjungens Lundström – Tipinitsy Trichonta excisa Lundström – Volkostrov Isl. Trichonta hamata Mik – Yu. Oleny Isl. Trichonta subfusca Lundström – Turastamozero Trichonta vulcani Dziedzicki – Lipovitsy Trichonta vulgaris Loew – Turastamozero Zygomyia angusta Plassmann – Lyudskoi Isl. Zygomyia kiddi Chandler – Oyatevschina Zygomyia notata Stannius – Oyatevschina, Paleostrov Isl., Vorobyi Zygomyia pseudohumeralis Caspers – Bol. Lelikovskiy Isl., Oyatevschina, Podyelniki, Shunevskiy Isl., Tipinitsy, Turastamozero, Uzkaya Salma, Volkostrov Isl., Vorobyi Zygomyia semifusca Meigen – Turastamozero Zygomyia valida Winnertz – Kurgenitsy, Turastamozero, Vorobyi Reports of the Finnish Environment Institute 40 | 2014 315 Zygomyia zaitzevi Chandler – Bol. Lelikovskiy Isl., Klimenicy, Vorobyi Allodia alternans Zetterstedt – Klimenicy, Turastamozero Allodia anglofennica Edwards – Kizhi Isl., Lipovitsy, Polya, Tambitsy, Verkhnee Myagrozero Allodia czernyi Landrock – Tambitsy Allodia foliifera Strobl – Turastamozero Allodia lugens Wiedemann – Myal’ Isl., Tipinitsy Allodia ornaticollis Meigen – Kurgenitsy Allodia pyxidiiformis A. Zaitzev – Turastamozero Allodiopsis domestica Meigen – Klimenicy, Tambitsy Allodiopsis gracai ŠeЯčík & Papp – Klimenicy Allodiopsis rustica Edwards – Polya, Tipinitsy, Verkhnee Myagrozero Notolopha cristata Staeger – Klimenicy, Lipovitsy, Tambitsy, Tipinitsy, Verkhnee Myagrozero Myrosia maculosa Meigen – Tipinitsy Synplasta karelica A. Zaitzev – Turastamozero Synplasta pseudingeniosa A. Zaitzev – Tambitsy Synplasta sintenisi Lackschewitz – Myal’ Isl. Anatella lavomaculata Edwards – Volkostrov Isl. Brachypeza armata Winnertz – Kopanets lake Brachypeza bisignata Winnertz – Lyudskoi Isl., Nizhneje Myagrozero Brevicornu bellum Johansen – Turastamozero Brevicornu fasciculatum Lackschewitz – Kizhi Isl., Lyudskoi Isl., Turastamozero, Volkostrov Isl. Brevicornu fuscipenne Staeger – Klimenicy, Turastamozero, Vorobyi Brevicornu griseicolle Staeger – Kosmozero, Turastamozero, Volkostrov Isl., Vorobyi Brevicornu griseolum Zetterstedt – Bol. Lelikovskiy Isl. Brevicornu improvisum A. Zaitzev – Turastamozero Brevicornu nigrofuscum Lundström – Turastamozero Brevicornu parafennicum A. Zaitzev – Turastamozero, Vorobyi Brevicornu serenum Winnertz – Bol. Lelikovskiy Isl., Kopanets lake, Turastamozero Brevicornu sericoma Meigen – Bol. Lelikovskiy Isl., Kizhi Isl., Vavlok Isl. Cordyla brevicornis Staeger – Klimenicy, Paleostrov Isl., Polya, Turastamozero, Vorobyi Cordyla crassicornis Meigen – Lipovitsy, Polya, Tambitsy, Tipinitsy, Turastamozero Cordyla fasciata Meigen – Turastamozero Cordyla issa Edwards – Vorobyi Cordyla laviceps Staeger – Myagrozero, Turastamozero, Uzkaya Salma, Vorobyi Cordyla insons Laštovka et Matile – Lipovitsy, Turastamozero, Vorobyi Cordyla nitens (s. Zaitzev) Winnertz – Tipinitsy, Turastamozero Cordyla nitidula Edwards – Oyatevschina Cordyla parvipalpis Edwards – Turastamozero, Uzkaya Salma Cordyla pseudomurina (in prep.) – Lipovitsy Cordyla pusilla Edwards – Kizhi Isl., Lyudskoi Isl., Polya, Tambitsy, Turastamozero, Vorobyi Cordyla semilava Staeger – Turastamozero Exechia cincta Winnertz – Tipinitsy Exechia coninis Winnertz – Turastamozero, Yu. Oleny Isl. Exechia contaminata Winnertz – Klimenicy, Paleostrov Isl., Polya, Tambitsy, Tipinitsy Exechia dizona Edwards – Tambitsy, Tipinitsy Exechia dorsalis Staeger – Myagrozero, Polya, Tambitsy, Turastamozero, Velikaya Niva Exechia exigua Lundström – Paleostrov Isl., Tipinitsy, Turastamozero ? Exechia macula Chandler – Kurgenitsy 316 Reports of the Finnish Environment Institute 40 | 2014 Exechia nigroscutellata Landrock – Klimenicy, Paleostrov Isl. Exechia parva Lundström – Tambitsy, Turastamozero, Verkhnee Myagrozero Exechia parvula Zetterstedt – Polya, Tipinitsy Exechia pectinivalva Stackelberg – Vorobyi Exechia pseudocincta Strobl – Klimenicy, Tambitsy Exechia repanda Johansen – Turastamozero, Volkostrov Isl. Exechia separata Lundström – Polya, Tipinitsy Exechia seriata Meigen – Klimenicy Exechia spinuligera Lundström – Vorobyi Exechia subfrigida Laštovka & Matile – Polya Exechia unifasciata Lackschewitz – Polya Exechiopsis aemula Plassmann – Turastamozero Exechiopsis crucigera Lundström – Yu. Oleny Isl. Exechiopsis davatchii Matile – Turastamozero Exechiopsis lackschewitziana Stackelberg – Lipovitsy, Tambitsy Exechiopsis praedita Plassmann – Oyatevschina Exechiopsis subulata Winnertz – Verkhnee Myagrozero Pseudobrachypeza helvetica Walker – Polya, Tambitsy, Tipinitsy Pseudorymosia fovea Dziedzicki – Turastamozero Rymosia fasciata Meigen – Turastamozero Rymosia setiger Dziedzicki – Tipinitsy Rymosia signatipes Van der Wulp – Kurgenitsy, Lipovitsy Tarnania fenestralis Meigen – Klimenicy Tarnania tarnanii Dziedzicki – Klimenicy, Lipovitsy, Polya, Tambitsy, Tipinitsy, Turastamozero Bolitophilidae Bolitophila dubia Siebke – Velikaya Niva Bolitophila modesta Lackschewitz – Lipovitsy, Tambitsy, Velikaya Niva Bolitophila nigrolineata Landrock – Polya, Tambitsy, Volkostrov Isl. Bolitophila occlusa Edwards – Klimenicy, Polya Bolitophila saundersi Curtis – Velikaya Niva Keroplatidae Macrocera angulata Meigen – Ernitskiy Isl., Klimenicy, Kuivakhda Isl., Lelikovo, Myal’ Isl. Macrocera centralis Meigen – Klimenicy, Tipinitsy Macrocera fasciata Meigen – Podyelniki Macrocera fascipennis Staeger – Rogachev Isl. Macrocera lutea Meigen – Tipinitsy, Yu. Oleny Isl. Macrocera maculata Meigen – Vikshezero Macrocera parva Lundström – Klimenicy Macrocera phalerata Meigen – Vavlok Isl., Vikshezero Macrocera pilosa Landrock – Velikaya Niva Macrocera stigma Curtis – Klimenicy, Shunevskiy Isl., Vavlok Isl. Macrocera stigmoides Edwards – Podyelniki, Polya Macrocera vittata Meigen – Turastamozero Rocetelion humerale Zetterstedt – Klimenicy Isoneuromyia semirufa Meigen – Podyelniki Keroplatus tipuloides Bosc – Oyatevschina Macrorrhyncha lava Winnertz – Podyelniki, Volkostrov Isl., Vorobyi Neoplatyura lava Macquart – Bol. Lelikovskiy Isl., Kopanets lake, Podyelniki, Uzkaya Salma Orfelia bicolor Macquart – Podyelniki, Turastamozero, Vorobyi Orfelia falcata A. Zaitzev – Lyudskoi Isl. Reports of the Finnish Environment Institute 40 | 2014 317 Orfelia fasciata Meigen – Paleostrov Isl., Vavlok Isl. Orfelia ochracea Meigen – Lipovitsy Pyratula zonata Zetterstedt – Ernitskiy Isl., Kuivakhda Isl., Lelikovo, Lyudskoi Isl., Paleostrov Isl., Sennaya Guba, Vikshezero, Yu. Oleny Isl. Urytalpa dorsalis Staeger – Ernitskiy Isl. Bombyliidae Anthrax anthrax Schrank – Kizhi Isl., Oyatevschina ? Villa paniscus Rossi – Kurgenitsy, Podyelniki, Vorobyi Asilidae Dioctria hyalipennis Fabricius – Eglov Isl., Verkhnee Myagrozero Cyrtopogon lateralis Fallén – Uzkaya Salma Leptogaster cylindrica DeGeer – Vegoruksy Laphria lava L. – Klimenicy, Nizhneje Myagrozero Choerades gilva L. – Kazhma Choerades tenebraus Esipenko – Verkhnee Myagrozero Neoitamus socius Loew – Oyatevschina, Podyelniki, Uzkaya Salma Machimus atricapilus Fallén – Kurgenitsy, Podyelniki, Vorobyi Scenopinidae Scenopinus vitripennis Meigen – Kizhi Isl. Therevidae ? Thereva inornata Verrall – Lipovitsy, Shun’ga Thereva microcephala Loew – Uzkaya Salma Rhagionidae Rhagio annulatus DeGeer – Kainos Isl. Rhagio lineola Fabricius – Bol. Lelikovskiy Isl., Eglov Isl., Kosmozero, Kurgenitsy, Lipovitsy, Myagrozero, Oyatevschina, Podyelniki, Polya, Turastamozero, Vavlok Isl. Rhagio maculatus DeGeer – Eglov Isl., Kainos Isl., Lipovitsy, Polya, Vorobyi, Yu. Oleny Isl. Rhagio scolopaceus L. – Eglov Isl., Ernitskiy Isl., Kizhi Isl., Lelikovo, Lipovitsy, Myagrozero, Polya, Rogachev Isl., Sennaya Guba, Vegoruksy, Vorobyi Chrysopilus nubecula Fallén – Klimenicy, Kosmozero, Kurgenitsy, Oyatevschina, Vorobyi Symphoromyia crassicornis Panzer – Kuzaranda Stratiomyidae Beris morrisi Dale – Eglov Isl., Khvost Isl., Kizhi Isl., Klimenicy, Kosmozero, Lelikovo, Paleostrov Isl., Rogachev Isl., Vavlok Isl., Velikaya Niva, Yu. Oleny Isl. Microchrysa polita L. – Kizhi Isl. Sargus ruipes Wahlberg – Oyatevschina, Polya Stratiomys chamaeleon L. – Velikaya Niva Stratiomys singularior Harris – Shun’ga Odontomyia hydroleon L. – Tolvuya Odontomyia tigrina Fabricius – Sennaya Guba Oplodontha viridula Fabricius – Velikaya Guba Neopachygaster meromelas Dufour – Kopanets lake, Oyatevschina Xylomyidae Xylomya czekanovskii Pleske – Khvost Isl., Klimenicy, Kopanets lake, Podyelniki, Polya, Tambitsy, Tipinitsy Tabanidae Chrysops caecutiens L. – Polya, Uzkaya Salma Chrysops divaricatus Loew – Lipovitsy, Podyelniki, Polya, Turastamozero, Uzkaya Salma, Vikshezero Chrysops nigripes Zetterstedt – Lipovitsy, Polya, Uzkaya Salma Chrysops relictus Meigen – Oyatevschina, Podyelniki, Sennaya Guba, Turastamozero 318 Reports of the Finnish Environment Institute 40 | 2014 Chrysops sepulcralis Fabricius – Vegoruksy Chrysops sp1 – Oyatevschina Chrysops viduatus Fabricius – Lipovitsy, Podyelniki, Polya, Turastamozero, Uzkaya Salma Hybomitra arpadi Szilády – Lipovitsy, Polya, Uzkaya Salma Hybomitra bimaculata Macquart – Lipovitsy, Polya, Turastamozero, Uzkaya Salma Hybomitra borealis Fabricius – Lipovitsy, Polya, Uzkaya Salma Hybomitra coniformis Chvála et Moucha – Lelikovo Hybomitra distinguenda Verrall – Lipovitsy, Polya, Uzkaya Salma Hybomitra kaurii Chvála et Lyneborg – Uzkaya Salma Hybomitra lundbecki Lyneborg – Lipovitsy, Polya, Uzkaya Salma Hybomitra montana Meigen – Uzkaya Salma Hybomitra muehlfeldi Brauer – Lipovitsy, Oyatevschina, Podyelniki, Polya, Turastamozero, Uzkaya Salma Hybomitra nigricornis Zetterstedt – Turastamozero, Volkostrov Isl. ? Tabanus bromius L. – Turastamozero Tabanus glaucopis Meigen – Vorobyi Tabanus maculicornis Zetterstedt – Lipovitsy, Polya, Uzkaya Salma Atylotus fulvus Meigen – Kopanets lake, Podyelniki, Uzkaya Salma Heptatoma pellucens Fabricius – Oyatevschina, Uzkaya Salma Haematopota pluvialis L. – Oyatevschina, Podyelniki, Polya, Turastamozero Xylophagidae Xylophagus ater Meigen – Kizhi Isl., Vorobyi Xylophagus cinctus DeGeer – Velikaya Niva Brachystomatidae Gloma fuscipennis Meigen – Lipovitsy Heleodromia immaculata Haliday – Lipovitsy Trichopeza albocincta Boheman – Yu. Oleny Isl. Dolichopodidae Dolichopus claviger Stannius – Khvost Isl., Kopanets lake, Nizhneje Myagrozero, Podyelniki Dolichopus discifer Stannius – Bol. Lelikovskiy Isl., Eglov Isl., Klimenicy, Kopanets lake, Kurgenitsy, Lelikovo, Lipovitsy, Myagrozero, Oyatevschina, Podyelniki, Polya, Uzkaya Salma, Vegoruksy, Verkhnee Myagrozero, Vorobyi Dolichopus lepidus Staeger – Ernitskiy Isl., Lelikovo, Lyudskoi Isl., Nizhneje Myagrozero, Podyelniki Dolichopus nigripes Fallén – Ernitskiy Isl. Dolichopus nitidus Fallén – Ernitskiy Isl., Kizhi Isl., Klimenicy, Sennaya Guba, Vegoruksy Dolichopus notatus Staeger – Kizhi Isl. Dolichopus pennatus Meigen – Oyatevschina, Vorobyi Dolichopus picipes Meigen – Bol. Lelikovskiy Isl., Klimenicy, Kopanets lake Dolichopus plumipes Scopoli – Kizhi Isl., Klimenicy, Kopanets lake, Kurgenitsy, Kuzaranda, Shunevskiy Isl., Tipinitsy, Vegoruksy, Volkostrov Isl. Dolichopus popularis Wiedemann – Eglov Isl. Dolichopus simplex Meigen – Bol. Lelikovskiy Isl., Kizhi Isl., Klimenicy Dolichopus trivialis Haliday – Kosmozero, Vorobyi Dolichopus ungulatus L. – Eglov Isl., Kizhi Isl., Podyelniki, Vorobyi Dolichopus wahlbergi Zetterstedt – Oyatevschina Dolichopus zetterstedti Stenhammar – Eglov Isl., Kurgenitsy, Vegoruksy Hercostomus aerosus Fallén – Bol. Lelikovskiy Isl., Eglov Isl., Ernitskiy Isl., Khvost Isl., Klimenicy, Lelikovo, Lipovitsy, Shunevskiy Isl., Vikshezero Hercostomus angustifrons Staeger – Ernitskiy Isl., Lelikovo, Lyudskoi Isl. Reports of the Finnish Environment Institute 40 | 2014 319 Hercostomus celer Meigen – Vikshezero Hercostomus chalybeus Wiedemann – Eglov Isl., Kizhi Isl., Kurgenitsy, Podyelniki Hercostomus metallicus Stannius – Eglov Isl., Khvost Isl., Klimenicy, Lyudskoi Isl., Polya, Sennaya Guba, Shunevskiy Isl., Vikshezero Hercostomus nigrilamellatus Macquart – Shunevskiy Isl. Hercostomus sahlbergi Zetterstedt – Turastamozero Hydrophorus praecox Lehmann – Kuzaranda Dolichophorus kerteszi Lichtwardt – Lelikovo, Lyudskoi Isl. Rhaphium crassipes Meigen – Oyatevschina, Vorobyi Rhaphium elegantulum Meigen – Kopanets lake Rhaphium lanceolatum Loew – Kizhi Isl. ? Rhaphium riparium Meigen – Vorobyi Syntormon bicolorellum Zetterstedt – Vorobyi Syntormon tarsatus Fallén – Kurgenitsy Neurigona abdominalis Fallén – Eglov Isl., Kizhi Isl. Neurigona pallida Fallén – Bol. Lelikovskiy Isl., Kainos Isl., Kopanets lake, Kosmozero, Kurgenitsy, Lipovitsy, Myagrozero, Podyelniki, Polya Neurigona quadrifasciata Fabricius – Eglov Isl., Khvost Isl., Klimenicy, Kopanets lake, Kurgenitsy, Oyatevschina, Shunevskiy Isl., Turastamozero, Vavlok Isl., Volkostrov Isl., Yu. Oleny Isl. Chrysotus cilipes Meigen – Nizhneje Myagrozero Chrysotus neglectus Wiedemann – Vorobyi Campsicnemus curvipes Fallén – Bol. Lelikovskiy Isl. Campsicnemus scambus Fallén – Bol. Lelikovskiy Isl., Lelikovo, Lipovitsy, Myagrozero, Podyelniki, Polya, Sennaya Guba, Shunevskiy Isl., Tambitsy, Tipinitsy, Vorobyi Empididae Rhamphomyia anomalina Zetterstedt – Vorobyi Rhamphomyia galacoptera Strobl – Kizhi Isl. Rhamphomyia lividiventris Zetterstedt – Uzkaya Salma ? Rhamphomyia modesta Wahlberg – Yu. Oleny Isl. Rhamphomyia nigripennis Fabricius – Khvost Isl., Lelikovo, Yu. Oleny Isl. Rhamphomyia nigripes Strobl – Vikshezero Rhamphomyia obscuripennis Meigen – Ernitskiy Isl., Kuivakhda Isl., Sennaya Guba Rhamphomyia sp2 (cf. hybotina) – Paleostrov Isl. Rhamphomyia spinipes Fallén – Tambitsy Rhamphomyia stigmosa Macquart – Vikshezero Rhamphomyia sulcatina Collin – Oyatevschina ? Rhamphomyia tipularia Fallén – Kopanets lake Rhamphomyia trigemina Oldenberg – Kizhi Isl. Rhamphomyia umbripennis Meigen – Ernitskiy Isl., Kizhi Isl., Lyudskoi Isl., Oyatevschina, Vorobyi Empis bicuspidata Collin – Lelikovo Empis borealis L. – Kizhi Isl., Klimenicy Empis livida L. – Vorobyi Empis prodromus Loew – Lelikovo Empis stercorea L. – Eglov Isl. Empis tessellata Fabricius – Eglov Isl., Kizhi Isl., Kurgenitsy, Lelikovo, Oyatevschina, Paleostrov Isl., Rogachev Isl., Sennaya Guba, Vegoruksy, Vikshezero, Vorobyi, Yu. Oleny Isl. Hilara sp1 (cf. canescens) – Vegoruksy Chelipoda albiseta Zetterstedt – Kosmozero, Yu. Oleny Isl. Chelipoda inexpactata Tuomikoski – Lipovitsy Chelipoda vocatoria Fallén – Lipovitsy 320 Reports of the Finnish Environment Institute 40 | 2014 Phyllodromia melanocephala Fabricius – Bol. Lelikovskiy Isl., Khvost Isl., Kopanets lake, Podyelniki ? Hemerodromia melangyna Collin – Kurgenitsy, Yu. Oleny Isl. Hemerodromia raptoria Meigen – Kurgenitsy, Vorobyi Hybotidae Hybos femoratus Müller – Eglov Isl., Ernitskiy Isl., Klimenicy, Lipovitsy, Polya Hybos grossipes L. – Bol. Lelikovskiy Isl., Eglov Isl., Khvost Isl., Klimenicy, Kopanets lake, Kosmozero, Kurgenitsy, Kuzaranda, Lipovitsy, Myagrozero, Nizhneje Myagrozero, Oyatevschina, Paleostrov Isl., Polya, Tambitsy, Tipinitsy, Turastamozero, Uzkaya Salma, Verkhnee Myagrozero, Volkostrov Isl., Vorobyi Trichinomyia lavipes Meigen – Lipovitsy, Myagrozero, Tambitsy, Turastamozero, Uzkaya Salma, Vorobyi Trichina bilobata Collin – Lipovitsy Trichina clavipes Meigen – Kosmozero Bicellaria intermedia Lundbeck – Bol. Lelikovskiy Isl., Kurgenitsy Bicellaria nigra Meigen – Kuivakhda Isl., Verkhnee Myagrozero Oedalea holmgreni Zetterstedt – Vikshezero Oedalea stigmatella Zetterstedt – Lyudskoi Isl. Oedalea zetterstedti Collin – Lipovitsy Euthyneura myrtilli Macquart – Lipovitsy, Velikaya Niva Ocydromia glabricula Fallén – Paleostrov Isl., Podyelniki, Tambitsy, Tipinitsy, Velikaya Niva Leptopeza borealis Zetterstedt – Kurgenitsy, Oyatevschina Leptopeza lavipes Meigen – Eglov Isl., Klimenicy, Kuivakhda Isl., Podyelniki, Vorobyi ? Platypalpus calceatus Meigen – Vorobyi Platypalpus candicans Fallén – Eglov Isl., Khvost Isl. Platypalpus ciliaris Fallén – Khvost Isl., Klimenicy, Kopanets lake, Polya, Tambitsy, Uzkaya Salma, Vorobyi Platypalpus cursitans Fabricius – Kizhi Isl., Lyudskoi Isl., Oyatevschina, Sennaya Guba, Tolvuya, Vorobyi ? Platypalpus dificilis Frey – Bol. Lelikovskiy Isl. Platypalpus ecalceatus Zetterstedt – Eglov Isl., Ernitskiy Isl., Khvost Isl., Klimenicy, Kuivakhda Isl., Lyudskoi Isl., Myagrozero, Myal’ Isl., Polya Platypalpus exilis Meigen – Eglov Isl., Klimenicy, Paleostrov Isl., Vavlok Isl. Platypalpus longicornis Meigen – Turastamozero, Vorobyi ? Platypalpus longicornoides Chvála – Sennaya Guba Platypalpus luteus Meigen – Kainos Isl., Lipovitsy, Podyelniki, Polya, Vorobyi Platypalpus macula Zetterstedt – Lipovitsy, Vavlok Isl. Platypalpus major Zetterstedt – Kopanets lake, Tipinitsy Platypalpus nigritarsis Fallén – Myagrozero Platypalpus nonstriatus Strobl – Klimenicy Platypalpus pectoralis Fallén – Bol. Lelikovskiy Isl., Podyelniki, Polya, Tipinitsy, Turastamozero, Uzkaya Salma, Verkhnee Myagrozero Platypalpus pseudorapidus Kovalev – Kizhi Isl., Oyatevschina, Vorobyi Platypalpus scandinavicus Chvála – Oyatevschina Platypalpus stigmatellus Zetterstedt – Klimenicy, Tambitsy ? Platypalpus tuomikoskii Chvála – Turastamozero Tachypeza fennica Tuomikoski – Vikshezero, Vorobyi Tachypeza fuscipennis Fallén – Vorobyi Tachypeza heeri Zetterstedt – Lipovitsy, Oyatevschina, Polya, Volkostrov Isl. Tachypeza nubila Meigen – Eglov Isl., Kurgenitsy, Lipovitsy, Polya, Vavlok Isl., Vorobyi Tachypeza truncorum Fallén – Lipovitsy, Polya Reports of the Finnish Environment Institute 40 | 2014 321 Tachydromia aemula Loew – Khvost Isl. Drapetis parilis Collin – Nizhneje Myagrozero Lonchopteridae Lonchoptera fallax de Meijere – Klimenicy, Lelikovo, Lyudskoi Isl. Lonchoptera lutea Panzer – Kizhi Isl., Vegoruksy, Vorobyi Platypezidae Microsania pectipennis Meigen – Bol. Lelikovskiy Isl., Klimenicy Callomyia amoena Meigen – Klimenicy, Lyudskoi Isl., Myal’ Isl. Callomyia speciosa Meigen – Eglov Isl., Lyudskoi Isl. Agathomyia elegantula Fallén – Lipovitsy Polyporivora ornata Meigen – Polya Polyporivora picta Meigen – Tipinitsy Platypeza consobrina Zetterstedt – Myagrozero Platypeza fasciata Meigen – Myagrozero Platypezina connexa Boheman – Tipinitsy Phoridae Anevrina thoracica Meigen – Kizhi Isl. Pipunculidae Chalarus holosericeus Meigen – Podyelniki ? Chalarus spurius Fallén – Podyelniki Verrallia aucta Fallén – Eglov Isl., Khvost Isl., Rogachev Isl., Turastamozero Nephrocerus lavicornis Zetterstedt – Oyatevschina Tomosvaryella geniculata Meigen – Lipovitsy Dorylomorpha maculata Walker – Kurgenitsy, Podyelniki, Verkhnee Myagrozero ? Cephalops semifumosus Kowarz – Turastamozero ? Eudorylas terminalis Thomson – Turastamozero Syrphidae Paragus albifrons Fallén – Vorobyi Paragus bicolor Fabricius – Eglov Isl., Vorobyi Paragus initimus Goeldlin – Sennaya Guba, Tolvuya, Vikshezero Paragus pecchiolii Rondani – Vikshezero Paragus tibialis Fallén – Oyatevschina Baccha elongata Fabricius – Bol. Lelikovskiy Isl., Eglov Isl., Lelikovo, Paleostrov Isl., Polya, Tipinitsy, Turastamozero, Velikaya Guba, Verkhnee Myagrozero, Volkostrov Isl. Platycheirus albimanus Fabricius – Kuivakhda Isl., Kurgenitsy, Lyudskoi Isl., Vikshezero Platycheirus angustatus Zetterstedt – Sennaya Guba Platycheirus clypeatus Meigen – Kosmozero, Lelikovo, Lyudskoi Isl., Nizhneje Myagrozero, Sennaya Guba, Tipinitsy Platycheirus europaeus Goeldlin, Maibach & Speight – Vikshezero Platycheirus fulviventris Macquart – Eglov Isl., Rogachev Isl. Platycheirus granditarsus Förster – Bol. Lelikovskiy Isl., Klimenicy, Kurgenitsy, Nizhneje Myagrozero, Podyelniki, Turastamozero, Volkostrov Isl. Platycheirus immarginatus Zetterstedt – Kosmozero Platycheirus occultus Goeldlin, Maibach & Speight – Turastamozero Platycheirus peltatus Meigen – Kizhi Isl., Velikaya Niva Platycheirus rosarum Fabricius – Eglov Isl., Kizhi Isl. Platycheirus scambus Staeger – Kopanets lake, Velikaya Niva Platycheirus scutatus Meigen – Kosmozero, Kurgenitsy Xanthandrus comtus Harris – Tipinitsy, Uzkaya Salma Melanostoma mellinum L. – Eglov Isl., Khvost Isl., Kopanets lake, Kosmozero, Kurgenitsy, Kuzaranda, Lelikovo, Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Turastamozero, Velikaya Niva, Verkhnee Myagrozero, Vikshezero, Volkostrov Isl., Vorobyi 322 Reports of the Finnish Environment Institute 40 | 2014 Melanostoma scalare Fabricius – Eglov Isl., Ernitskiy Isl., Klimenicy, Lelikovo, Lipovitsy, Lyudskoi Isl., Oyatevschina, Paleostrov Isl., Polya, Sennaya Guba, Tipinitsy, Turastamozero, Uzkaya Salma, Vorobyi Melangyna compositarum Verrall – Turastamozero, Verkhnee Myagrozero Melangyna umbellatarum Fabricius – Khvost Isl., Kizhi Isl., Vorobyi Meligramma guttata Fallén – Klimenicy Leucozona glaucia L. – Kurgenitsy, Nizhneje Myagrozero, Turastamozero, Velikaya Niva, Verkhnee Myagrozero, Vorobyi Leucozona inopinata Doczkal – Uzkaya Salma Leucozona laternaria Müller – Khvost Isl., Kurgenitsy, Nizhneje Myagrozero, Paleostrov Isl., Rogachev Isl. Leucozona lucorum L. – Kizhi Isl., Oyatevschina, Velikaya Niva Epistrophe lava Doczkal & Schmid – Eglov Isl. Epistrophe grossulariae Meigen – Turastamozero, Vorobyi Eriozona erratica L. – Tambitsy Scaeva pyrastri L. – Vegoruksy, Velikaya Niva, Vorobyi Scaeva selenitica Meigen – Kurgenitsy, Nizhneje Myagrozero, Turastamozero, Verkhnee Myagrozero Meliscaeva cinctella Zetterstedt – Lipovitsy, Turastamozero, Vikshezero, Vorobyi Didea fasciata Macquart – Lipovitsy, Uzkaya Salma Didea intermedia Loew – Eglov Isl., Kurgenitsy, Turastamozero, Vegoruksy Dasysyrphus hilaris Zetterstedt – Eglov Isl., Vikshezero Dasysyrphus pinastri DeGeer – Eglov Isl., Vikshezero Dasysyrphus tricinctus Fallén – o. B.Klimeckiy, Klimenicy, Kopanets lake, Nizhneje Myagrozero, Oyatevschina, Turastamozero, Velikaya Niva, Vorobyi Dasysyrphus venustus Meigen – Eglov Isl., Vikshezero Episyrphus balteatus DeGeer – Kizhi Isl., Kosmozero, Oyatevschina, Turastamozero, Uzkaya Salma, Vikshezero, Vorobyi Eupeodes bucculatus Rondani – Turastamozero, Vorobyi Eupeodes corollae Fabricius – Nizhneje Myagrozero Eupeodes latifasciatus Macquart – Klimenicy Eupeodes lundbecki Soot Ryen – Velikaya Niva, Vorobyi Eupeodes nitens Zetterstedt – Turastamozero Syrphus admirandus Goeldlin – Vikshezero Syrphus ribesii L. – Eglov Isl., Khvost Isl., Turastamozero, Vikshezero, Vorobyi Syrphus torvus Osten-Sacken – Eglov Isl., Kizhi Isl., Nizhneje Myagrozero, Vorobyi Syrphus vitripennis Meigen – Eglov Isl., Vikshezero Parasyrphus annulatus Zetterstedt – Velikaya Niva Parasyrphus lineolus Zetterstedt – Nizhneje Myagrozero Parasyrphus nigritarsis Zetterstedt – Vikshezero Sphaerophoria batava Goeldlin – Eglov Isl., Podyelniki, Vikshezero Sphaerophoria interrupta Fabricius – Kizhi Isl., Kosmozero, Lyudskoi Isl., Vikshezero, Vorobyi Sphaerophoria menthastri L. – Kuzaranda, Paleostrov Isl. Sphaerophoria philantha Meigen – Kurgenitsy, Sennaya Guba, Vikshezero Sphaerophoria scripta L. – Eglov Isl., Kizhi Isl., Klimenicy, Kosmozero, Kuzaranda, Lelikovo, Lyudskoi Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Rogachev Isl., Sennaya Guba, Tipinitsy, Turastamozero, Vertilovo, Vikshezero, Volkostrov Isl., Vorobyi Sphaerophoria taeniata Meigen – Kizhi Isl., Kuzaranda, Podyelniki, Rogachev Isl., Vorobyi Sphaerophoria virgata Goeldlin – Eglov Isl., Tipinitsy Reports of the Finnish Environment Institute 40 | 2014 323 Xanthogramma pedissequum Harris – Rogachev Isl., Vorobyi Xanthogramma stackelbergi Violovitsh – Khvost Isl., Rogachev Isl. Ceriana conopsoides L. – Turastamozero Chrysotoxum arcuatum L. – Velikaya Guba, Vikshezero Chrysotoxum bicinctum L. – Eglov Isl., Khvost Isl., Kuzaranda, Rogachev Isl., Turastamozero, Vikshezero, Vorobyi Chrysotoxum fasciolatum DeGeer – Kosmozero Chrysotoxum festivum L. – Shun’ga Rhingia borealis Ringdahl – Oyatevschina, Velikaya Niva Rhingia campestris Meigen – Kizhi Isl., Tolvuya Hammerschmidtia ferruginea Fallén – Klimenicy, Velikaya Niva Neoascia geniculata Meigen – Vikshezero Neoascia tenur Harris – Eglov Isl., Ernitskiy Isl., Kizhi Isl., Klimenicy, Kurgenitsy, Lelikovo, Lyudskoi Isl., Sennaya Guba, Vikshezero Sphegina clunipes Fallén – Klimenicy, Kopanets lake, Lipovitsy Sphegina sibirica Stackelberg – Kizhi Isl., Klimenicy, Tipinitsy, Vavlok Isl., Vikshezero Pipizella certa Violovitsh – Rogachev Isl. Pipizella viduata L. – Klimenicy, Kuzaranda, Lyudskoi Isl., Rogachev Isl., Turastamozero, Vikshezero Pipiza austriaca Meigen – Lelikovo, Velikaya Niva Pipiza bimaculata Meigen – Lelikovo, Paleostrov Isl. Pipiza noctiluca L. – Velikaya Niva, Vikshezero, Yu. Oleny Isl. Pipiza quadrimaculata Panzer – Velikaya Guba, Vikshezero Orthonevra erythrogona Malm – Sennaya Guba Orthonevra stackelbergi Thompson & Torp – Klimenicy, Vikshezero ? Chrysogaster virescens Loew – Sennaya Guba Cheilosia carbonaria Egger – Oyatevschina, Vikshezero Cheilosia lavipes Panzer – Kizhi Isl., Tolvuya Cheilosia frontalis Loew – Kizhi Isl. Cheilosia gigantea Zetterstedt – Klimenicy Cheilosia illustrata Harris – Eglov Isl., Kizhi Isl., Kosmozero, Kurgenitsy, Nizhneje Myagrozero, Oyatevschina, Rogachev Isl., Vorobyi Cheilosia impressa Loew – Ernitskiy Isl. Cheilosia longula Zetterstedt – Myagrozero, Nizhneje Myagrozero, Turastamozero, Velikaya Niva Cheilosia mutabilis Fallén – Kurgenitsy, Podyelniki, Rogachev Isl., Turastamozero, Vegoruksy, Velikaya Niva, Verkhnee Myagrozero, Volkostrov Isl. Cheilosia pagana Meigen – Eglov Isl., Kizhi Isl., Kurgenitsy, Lelikovo, Nizhneje Myagrozero, Oyatevschina, Podyelniki, Rogachev Isl., Tolvuya, Vikshezero, Vorobyi Cheilosia pubera Zetterstedt – Klimenicy, Oyatevschina, Sennaya Guba Cheilosia rotundiventris Becker – Kizhi Isl. Cheilosia scutellata Fallén – Velikaya Niva Cheilosia sootryeni Nielsen – Vikshezero Cheilosia variabilis Panzer – Kainos Isl. Cheilosia vernalis Fallén – Kizhi Isl., Lelikovo, Nizhneje Myagrozero, Velikaya Niva, Vorobyi ? Cheilosia vicina Zetterstedt – Vikshezero Cheilosia vulpina Meigen – Kizhi Isl., Klimenicy Chamaesyrphus scaevoides Fallén – Ernitskiy Isl., Paleostrov Isl. Volucella bombylans L. – Eglov Isl., Khvost Isl., Kizhi Isl., Lelikovo, Lyudskoi Isl., Oyatevschina, Rogachev Isl., Sennaya Guba, Volkostrov Isl. 324 Reports of the Finnish Environment Institute 40 | 2014 Volucella pellucens L. – Eglov Isl., Khvost Isl., Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Turastamozero Sericomyia lappona L. – Podyelniki, Uzkaya Salma Sericomyia nigra Portschinsky – Nizhneje Myagrozero Sericomyia silentis Harris – Dianova Gora, Tambitsy, Turastamozero Eristalis abusiva Collin – Kosmozero, Kurgenitsy Eristalis anthophorina Fallén – Shun’ga Eristalis arbustorum L. – Lipovitsy, Nizhneje Myagrozero, Verkhnee Myagrozero, Vorobyi Eristalis cryptarum Fabricius – Tolvuya Eristalis horticola DeGeer – Kizhi Isl. Eristalis interrupta Poda – Eglov Isl., Nizhneje Myagrozero, Turastamozero, Vegoruksy, Velikaya Niva, Verkhnee Myagrozero, Vorobyi Eristalis intricaria L. – Shun’ga, Vegoruksy Eristalis obscura Loew – Eglov Isl., Kurgenitsy, Nizhneje Myagrozero, Turastamozero, Verkhnee Myagrozero, Vikshezero, Vorobyi Eristalis oestracea L. – Kizhi Isl. Eristalis rupium Fabricius – Oyatevschina, Podyelniki, Turastamozero Eristalis tenax L. – Turastamozero, Vegoruksy Myathropa lorea L. – Eglov Isl., Podyelniki, Turastamozero Anasimyia interpuncta Harris – Lelikovo Anasimyia lineata Fabricius – Eglov Isl., Podyelniki Anasimyia lunulata Meigen – Uzkaya Salma, Vikshezero, Vorobyi Helophilus afinis Wahlberg – Lyudskoi Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Turastamozero, Vavlok Isl., Vikshezero, Volkostrov Isl., Vorobyi Helophilus hybridus Loew – Kurgenitsy, Lelikovo, Lyudskoi Isl., Nizhneje Myagrozero, Podyelniki, Tipinitsy, Turastamozero, Volkostrov Isl. Helophilus pendulus L. – Eglov Isl., Kizhi Isl., Kurgenitsy, Nizhneje Myagrozero, Oyatevschina, Paleostrov Isl., Podyelniki, Rogachev Isl., Shun’ga, Turastamozero, Vegoruksy, Verkhnee Myagrozero, Vikshezero, Volkostrov Isl., Vorobyi Helophilus trivittatus Fabricius – Kizhi Isl., Kurgenitsy Parhelophilus consimilis Malm – Rogachev Isl., Volkostrov Isl., Vorobyi Eumerus strigatus Fallén – Nizhneje Myagrozero, Rogachev Isl., Velikaya Niva Microdon miki Doczkal & Schmid – Kosmozero Criorrchina asilica Fallén – Polya, Velikaya Niva, Vikshezero Blera fallax L. – Lipovitsy, Vegoruksy Xylota abiens Meigen – Podyelniki Xylota caeruleiventris Zetterstedt – Polya Xylota lorum Fabricius – Eglov Isl., Nizhneje Myagrozero, Podyelniki, Vegoruksy, Verkhnee Myagrozero Xylota jakutorum Bagatshanova – Eglov Isl. Xylota meigeniana Stackelberg – Eglov Isl., Klimenicy, Kurgenitsy, Kuzaranda, Nizhneje Myagrozero, Podyelniki, Polya, Turastamozero Xylota segnis L. – Eglov Isl., Kosmozero, Kuzaranda, Nizhneje Myagrozero, Podyelniki, Vegoruksy, Velikaya Niva, Verkhnee Myagrozero Xylota sylvarum L. – Khvost Isl., Lipovitsy, Oyatevschina, Polya, Turastamozero Xylota tarda Meigen – Eglov Isl., Khvost Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Tambitsy, Verkhnee Myagrozero Xylota xanthocnema Collin – Klimenicy, Verkhnee Myagrozero Chalcosyrphus nemorum Fabricius – Kosmozero, Podyelniki, Rogachev Isl., Uzkaya Salma Chalcosyrphus ruipes Loew – Eglov Isl. Reports of the Finnish Environment Institute 40 | 2014 325 Chalcosyrphus valgus Gmelin – Klimenicy Syritta pipiens L. – Kosmozero Spilomyia diophthalma L. – Kurgenitsy, Oyatevschina, Podyelniki, Turastamozero, Uzkaya Salma, Vorobyi Temnostoma angustistriatum Krivosheina – Klimenicy, Kosmozero, Rogachev Isl., Tipinitsy, Vikshezero Temnostoma apiforme Fabricius – Klimenicy, Kosmozero, Rogachev Isl., Turastamozero, Velikaya Niva, Verkhnee Myagrozero, Vikshezero, Yu. Oleny Isl. Temnostoma carens Gaunitz – Eglov Isl. Temnostoma sericomyiaeforme Portschinsky – Eglov Isl., Kizhi Isl., Kurgenitsy, Rogachev Isl., Turastamozero, Uzkaya Salma, Vegoruksy Temnostoma vespiforme L. – Eglov Isl., Klimenicy, Lipovitsy, Oyatevschina, Paleostrov Isl., Rogachev Isl., Turastamozero, Velikaya Niva, Yu. Oleny Isl. Conopidae Conops quadrifasciatus DeGeer – Bol. Lelikovskiy Isl., Oyatevschina, Podyelniki, Turastamozero, Verkhnee Myagrozero, Vorobyi Myopa buccata L. – Vikshezero Sicus ferrugineus L. – Eglov Isl., Kizhi Isl., Kurgenitsy, Nizhneje Myagrozero, Oyatevschina, Podyelniki, Sennaya Guba, Vegoruksy, Verkhnee Myagrozero, Vorobyi Chloropidae Gaurax dubius Macquart – Lelikovo Elachiptera cornuta Fallén – Bol. Lelikovskiy Isl., Eglov Isl., Ernitskiy Isl., Kurgenitsy, Lelikovo, Lyudskoi Isl., Myagrozero, Podyelniki, Sennaya Guba Elachiptera tuberculifera Corti – Lelikovo, Lyudskoi Isl., Myagrozero, Nizhneje Myagrozero Lasiambia palposa Fallén – Vorobyi Siphonella oscinina Fallén – Vorobyi Tricimba cincta s.l. – Vorobyi Oscinella cariciphila Collin – Sennaya Guba Oscinella frit L. – Lelikovo Oscinella pusilla Meigen – Myagrozero, Sennaya Guba Rhopalopterum fasciola Meigen – Kurgenitsy Rhopalopterum femorale Collin – Lelikovo, Lyudskoi Isl. Dicraeus fennicus Duda – Kurgenitsy Meromyza ornata Wiedemann – Lelikovo ? Meromyza pluriseta Peteri – Sennaya Guba Meromyza saltatrix L. – Lelikovo, Sennaya Guba Cetema cereris Fallén – Nizhneje Myagrozero, Podyelniki, Vorobyi Cetema myopinum Loew – Oyatevschina Chlorops frontosus Meigen – Lelikovo Chlorops hypostigma Meigen – Oyatevschina Chlorops limbata Meigen – Ernitskiy Isl., Klimenicy, Kurgenitsy, Lipovitsy, Polya, Sennaya Guba Chlorops meigenii Loew – Eglov Isl., Ernitskiy Isl., Khvost Isl., Klimenicy, Kuivakhda Isl., Lyudskoi Isl., Paleostrov Isl., Polya, Vikshezero Chlorops planifrons Loew – Khvost Isl. Chlorops ringens Loew – Vorobyi ? Chlorops rossicus Smirnov – Polya Chlorops scalaris Meigen – Kuzaranda, Sennaya Guba Chlorops speciosa Meigen – o. B.Klimeckiy, Eglov Isl., Klimenicy, Nizhneje Myagrozero, Podyelniki, Vikshezero Chlorops troglodytes Zetterstedt – o. B.Klimeckiy, Podyelniki, Vorobyi 326 Reports of the Finnish Environment Institute 40 | 2014 Thaumatomyia glabra Meigen – Kuzaranda, Sennaya Guba Thaumatomyia hallandica Anderson – Kuzaranda, Lelikovo, Sennaya Guba Thaumatomyia notata Meigen – Kuzaranda Thaumatomyia rufa Macquart – Lelikovo, Sennaya Guba Thaumatomyia trifasciata Zetterstedt – Kurgenitsy Aphanotrigonum trilineatum Meigen – Sennaya Guba Eribulus nana Zetterstedt – Sennaya Guba Incertella albipalpis Meigen – Kuzaranda Speccafrons halophila Duda – Sennaya Guba Milichiidae Phyllomyza equitans Hendel – Sennaya Guba Phyllomyza securicornis Fallén – Rogachev Isl., Vorobyi Neophyllomyza acyglossa Villeneuve – Lyudskoi Isl. Ephydridae Discomyza incurva Fallén – Lyudskoi Isl. ? Psilopa stackelbergi Nartshuk – Vikshezero Dichaeta caudata Fallén – Lelikovo, Oyatevschina, Sennaya Guba Notiphila aquatica Becker – Klimenicy Nostima picta Fallén – Bol. Lelikovskiy Isl. Limnellia stenhammari Zetterstedt – Myagrozero Coenia curvicauda Meigen – Rogachev Isl., Sennaya Guba, Vikshezero Coenia palustris Fallén – Lelikovo Drosophilidae Stegana baechlii Laštovka & Maca – Turastamozero Stegana furta L. – Ernitskiy Isl., Kizhi Isl., Lelikovo, Rogachev Isl., Sennaya Guba Chymomyza fuscimana Zetterstedt – Turastamozero Drosophila eskoi Lakovaara & Lankinen – Yu. Oleny Isl. Drosophila histrio Meigen – Kainos Isl., Uzkaya Salma, Vavlok Isl. Drosophila littoralis Meigen – Yu. Oleny Isl. Drosophila phalerata Meigen – Tambitsy, Verkhnee Myagrozero Drosophila testacea von Roser – Lipovitsy, Tipinitsy, Turastamozero, Verkhnee Myagrozero, Yu. Oleny Isl. Drosophila transversa Fallén – Kizhi Isl., Polya, Turastamozero, Uzkaya Salma, Verkhnee Myagrozero, Volkostrov Isl., Vorobyi Hirtorosophila trivittata Strobl – Lipovitsy Lordiphosa fenestrarum Fallén – Kizhi Isl. Lordiphosa hexasticha Papp – Podyelniki Lordiphosa nigricolor Strobl – Kizhi Isl. Scaptomyza consimilis Hackman – Tipinitsy, Turastamozero Scaptomyza graminum Fallén – Tipinitsy Scaptomyza pallida Zetterstedt – Kizhi Isl., Nizhneje Myagrozero, Vegoruksy, Vorobyi Diastatidae Diastata nebulosa Fallén – Lipovitsy Chamaemyiidae Chamaemyia aestiva Tanasijtshuk – Ernitskiy Isl., Lelikovo, Myagrozero Chamaemyia elegans Panzer – Ernitskiy Isl., Lelikovo, Lyudskoi Isl., Myal’ Isl., Sennaya Guba Chamaemyia geniculata Zetterstedt – Lelikovo Chamaemyia juncorum Fallén – Kurgenitsy, Lyudskoi Isl., Myagrozero, Sennaya Guba Chamaemyia polystigma Meigen – Kurgenitsy, Lelikovo Lauxaniidae Homoneura interstincta Fallén – Uzkaya Salma Homoneura lamellata Becker – Lipovitsy, Polya, Turastamozero Reports of the Finnish Environment Institute 40 | 2014 327 Homoneura tenera Loew – Khvost Isl., Lyudskoi Isl., Turastamozero, Vikshezero Minettia helvola Becker – Khvost Isl., Lipovitsy, Podyelniki, Polya, Tambitsy, Turastamozero, Verkhnee Myagrozero Minettia loewi Schiner – Ernitskiy Isl., Klimenicy, Lipovitsy, Polya, Tipinitsy Minettia longipennis Fabricius – Eglov Isl., Khvost Isl., Kizhi Isl., Kosmozero, Lipovitsy, Lyudskoi Isl., Myal’ Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Polya, Sennaya Guba, Vegoruksy, Vorobyi Minettia lupulina Fabricius – Kainos Isl., Khvost Isl., Kizhi Isl., Klimenicy, Nizhneje Myagrozero, Oyatevschina, Sennaya Guba, Shunevskiy Isl., Tipinitsy, Verkhnee Myagrozero, Vikshezero, Volkostrov Isl., Vorobyi Tricholauxania praeusta Fallén – Bol. Lelikovskiy Isl., Eglov Isl., Kopanets lake, Oyatevschina, Podyelniki, Shunevskiy Isl., Turastamozero, Verkhnee Myagrozero, Volkostrov Isl. Cnemacantha muscaria Fallén – Kizhi Isl., Sennaya Guba Meiosimyza afinis Zetterstedt – Klimenicy, Myal’ Isl., Verkhnee Myagrozero, Yu. Oleny Isl. Meiosimyza decempunctata Fallén – Eglov Isl., Ernitskiy Isl., Kainos Isl., Myal’ Isl., Nizhneje Myagrozero, Podyelniki, Tipinitsy, Vavlok Isl. Meiosimyza decipiens Loew – Khvost Isl., Klimenicy, Sennaya Guba, Uzkaya Salma Meiosimyza illota Loew – Kizhi Isl., Vikshezero Meiosimyza mihalyii Papp – Vorobyi Meiosimyza platycephala Loew – Lipovitsy, Lyudskoi Isl., Podyelniki Meiosimyza rorida Fallén – Bol. Lelikovskiy Isl., Eglov Isl., Ernitskiy Isl., Kainos Isl., Kizhi Isl., Klimenicy, Kopanets lake, Kuivakhda Isl., Kurgenitsy, Myal’ Isl., Podyelniki, Polya, Sennaya Guba, Shunevskiy Isl., Turastamozero, Vavlok Isl., Vegoruksy, Verkhnee Myagrozero, Volkostrov Isl., Yu. Oleny Isl. Meiosimyza subfasciata Zetterstedt – Kizhi Isl., Kurgenitsy, Vikshezero Poecilolycia vittata Walker – Ernitskiy Isl., Oyatevschina Sapromyza amabilis Frey – Polya Sapromyza basalis Zetterstedt – Lipovitsy, Oyatevschina, Podyelniki, Polya, Tambitsy, Turastamozero, Verkhnee Myagrozero, Yu. Oleny Isl. Sapromyza hyalinata Meigen – Bol. Lelikovskiy Isl., Ernitskiy Isl., Klimenicy, Kopanets lake, Lelikovo, Lipovitsy, Lyudskoi Isl., Myagrozero, Myal’ Isl., Oyatevschina, Paleostrov Isl., Podyelniki, Polya, Rogachev Isl., Sennaya Guba, Shunevskiy Isl., Turastamozero, Vavlok Isl., Velikaya Niva, Volkostrov Isl., Vorobyi, Yu. Oleny Isl. Sapromyza opaca Becker – Vorobyi Sapromyza sexpunctata Meigen – Khvost Isl., Kosmozero, Nizhneje Myagrozero, Oyatevschina, Podyelniki, Turastamozero, Vorobyi Sapromyza zetterstedti Hendel – Lipovitsy, Uzkaya Salma Calliopum aeneum Fallén – Kuzaranda Calliopum elisae Meigen – Kuzaranda, Nizhneje Myagrozero, Sennaya Guba, Tipinitsy, Turastamozero Lauxania cylindricornis Fabricius – Ernitskiy Isl., Kainos Isl., Kizhi Isl., Kurgenitsy, Kuzaranda, Lelikovo, Lyudskoi Isl., Nizhneje Myagrozero, Sennaya Guba, Tolvuya, Uzkaya Salma, Vavlok Isl., Vegoruksy, Vikshezero, Vorobyi Micropezidae Rainieria latifrons Loew – Lipovitsy Micropeza corrigiolata L. – Tolvuya Neriidae Neria cibaria L. – Eglov Isl. Neria commutata Czerny – Eglov Isl., Ernitskiy Isl., Lelikovo, Paleostrov Isl., Rogachev Isl., Tipinitsy Acartophthalmidae Acartophthalmus bicolor Oldenberg – Lyudskoi Isl. 328 Reports of the Finnish Environment Institute 40 | 2014 Anthomyzidae ? Anthomyza dissors Collin – Kopanets lake Anthomyza gracilis Fallén – Kizhi Isl. Clusiidae Hendelia beckeri Czerny – Lyudskoi Isl., Shunevskiy Isl., Vikshezero Clusiodes albimanus Meigen – Kopanets lake, Lipovitsy, Shunevskiy Isl., Turastamozero Clusiodes apicalis Zetterstedt – Ernitskiy Isl., Uzkaya Salma Clusiodes geomyzinus Fallén – Oyatevschina Clusiodes pictipes Zetterstedt – Oyatevschina, Vorobyi Clusiodes ruicollis Meigen – Lyudskoi Isl. Clusia lava Meigen – Klimenicy, Lipovitsy, Oyatevschina, Polya, Uzkaya Salma, Vikshezero Megamerinidae Megamerina dolium Fabricius – Kopanets lake, Kurgenitsy, Polya, Vikshezero Odiniidae Odinia ornata Zetterstedt – Turastamozero Opomyzidae Anomalochaeta guttipennis Zetterstedt – Shunevskiy Isl. Opomyza punctella Fallén – Podyelniki Geomyza hackmani Nartshuk – Nizhneje Myagrozero Geomyza tripunctata Fallén – Lyudskoi Isl. Pallopteridae Temnosira saltuum L. – Kizhi Isl., Myal’ Isl., Paleostrov Isl., Rogachev Isl., Sennaya Guba, Vikshezero Toxoneura modesta Meigen – Nizhneje Myagrozero Toxoneura trimacula Meigen – Podyelniki, Tipinitsy Dryomyzidae Dryomyza decrepita Zetterstedt – Ernitskiy Isl., Klimenicy, Vorobyi Neuroctena anilis Fallén – Bol. Lelikovskiy Isl., Kizhi Isl., Rogachev Isl., Yu. Oleny Isl. Phaeomyiidae Pelidnoptera fuscipennis Meigen – Turastamozero Sciomyzidae Pherbellia albocostata Fallén – Klimenicy, Lipovitsy, Oyatevschina, Podyelniki, Polya, Turastamozero, Uzkaya Salma Pherbellia alpina Frey – Lipovitsy Pherbellia argyra Verbeke – Lelikovo, Sennaya Guba Pherbellia brunnipes Meigen – Sennaya Guba Pherbellia dubia Fallén – Ernitskiy Isl., Kizhi Isl., Lipovitsy, Podyelniki, Vorobyi Pherbellia griseola Fallén – Bol. Lelikovskiy Isl., Kazhma, Lelikovo, Sennaya Guba Pherbellia obtusa Fallén – Kizhi Isl., Shunevskiy Isl., Uzkaya Salma, Vavlok Isl. Pherbellia pallidiventris Fallén – Kopanets lake, Kosmozero, Lipovitsy, Paleostrov Isl., Podyelniki, Velikaya Niva Pherbellia schoenherri Fallén – Kurgenitsy, Vorobyi Pherbellia sordida Hendel – Kurgenitsy, Sennaya Guba, Shunevskiy Isl. Pherbellia ventralis Fallén – Kurgenitsy Pteromicra angustipennis Staeger – Ernitskiy Isl. Pteromicra glabricula Fallén – Ernitskiy Isl., Sennaya Guba, Shunevskiy Isl., Vikshezero Colobaea distincta Meigen – Shunevskiy Isl. Renocera pallida Fallén – Ernitskiy Isl., Klimenicy, Shunevskiy Isl., Vikshezero Renocera strobli Hendel – Vikshezero Anticheta atriseta Loew – Shunevskiy Isl., Vikshezero Ectinocera borealis Zetterstedt – Uzkaya Salma Reports of the Finnish Environment Institute 40 | 2014 329 Tetanocera amurensis Hendel – Klimenicy Tetanocera arrogans Meigen – Ernitskiy Isl., Khvost Isl., Kizhi Isl., Klimenicy, Kurgenitsy, Lelikovo, Sennaya Guba, Tolvuya, Vegoruksy Tetanocera elata Fabricius – Bol. Lelikovskiy Isl., Kizhi Isl., Podyelniki, Sennaya Guba, Tipinitsy, Velikaya Niva, Volkostrov Isl., Vorobyi Tetanocera ferruginea Fallén – Kizhi Isl., Klimenicy, Tipinitsy, Vorobyi Tetanocera freyi Stackelberg – Kurgenitsy, Tipinitsy, Volkostrov Isl. Tetanocera fuscinervis Zetterstedt – Ernitskiy Isl., Lelikovo, Lyudskoi Isl. Tetanocera hyalipennis von Roser – Kurgenitsy, Vorobyi Tetanocera montana Day – Kazhma, Kurgenitsy Tetanocera phyllophora Melander – Ernitskiy Isl., Kizhi Isl., Myagrozero, Nizhneje Myagrozero, Tipinitsy, Verkhnee Myagrozero Tetanocera robusta Loew – Bol. Lelikovskiy Isl., Kurgenitsy, Rogachev Isl., Shunevskiy Isl., Tipinitsy Euthycera chaerophylli Fabricius – Nizhneje Myagrozero Trypetoptera punctulata Scopoli – Bol. Lelikovskiy Isl., Dianova Gora, Khvost Isl., Kurgenitsy, Lipovitsy, Myagrozero, Podyelniki, Tipinitsy, Turastamozero, Vegoruksy, Velikaya Guba, Velikaya Niva, Vorobyi, Yu. Oleny Isl. Pherbina coryleti Scopoli – Bol. Lelikovskiy Isl., Ernitskiy Isl., Kizhi Isl., Kurgenitsy, Tipinitsy Psacadina zernyi Mayer – Sennaya Guba Elgiva cucularia L. – Kurgenitsy, Sennaya Guba Ilione lineata Fallén – Kurgenitsy, Vorobyi Hydromya dorsalis Fabricius – Vikshezero Limnia paludicola Elberg – Kurgenitsy, Oyatevschina, Polya, Tipinitsy, Uzkaya Salma, Velikaya Guba, Verkhnee Myagrozero Limnia unguicornis Scopoli – Nizhneje Myagrozero, Rogachev Isl. Sepedon spinipes Scopoli – Kizhi Isl., Klimenicy, Lelikovo, Sennaya Guba, Volkostrov Isl. Dichetophora inlandica Verbeke – Volkostrov Isl. Tetanura pallidiventris Fallén – Klimenicy Sepsidae Themira annulipes Meigen – Kizhi Isl., Kuzaranda, Nizhneje Myagrozero, Oyatevschina, Vorobyi Themira germanica Duda – Bol. Lelikovskiy Isl. Themira leachi Meigen – Nizhneje Myagrozero Nemopoda nitidula Fallén – Rogachev Isl., Vikshezero Sepsis cynipsea L. – Kizhi Isl., Kuzaranda, Sennaya Guba Sepsis orthocnemis Frey – Myagrozero, Nizhneje Myagrozero Sepsis punctum Fabricius – Bol. Lelikovskiy Isl., Kizhi Isl., Nizhneje Myagrozero, Vikshezero Heleomyzidae ? Borboropsis puberula Zetterstedt – Vorobyi Neoleria ruiceps Zetterstedt – Myagrozero Morpholeria ruicornis Meigen – Bol. Lelikovskiy Isl. Scoliocentra amplicornis Czerny – Kurgenitsy, Turastamozero Suillia apicalis Loew – Khvost Isl., Turastamozero Suillia atricornis Meigen – Bol. Lelikovskiy Isl., Klimenicy, Lipovitsy, Paleostrov Isl., Polya, Tambitsy, Tipinitsy, Turastamozero, Verkhnee Myagrozero, Vikshezero, Yu. Oleny Isl. Suillia bicolor Zetterstedt – Bol. Lelikovskiy Isl., Klimenicy, Kopanets lake, Lipovitsy, Myagrozero, Paleostrov Isl., Polya, Tambitsy, Tipinitsy, Turastamozero, Uzkaya Salma, Vavlok Isl., Vegoruksy, Verkhnee Myagrozero, Volkostrov Isl., Yu. Oleny Isl. 330 Reports of the Finnish Environment Institute 40 | 2014 Suillia lava Meigen – Eglov Isl., Nizhneje Myagrozero, Oyatevschina, Turastamozero, Uzkaya Salma, Vorobyi Suillia lavifrons Zetterstedt – Bol. Lelikovskiy Isl., Klimenicy, Polya, Tambitsy Suillia fuscicornis Zetterstedt – Myal’ Isl., Paleostrov Isl., Podyelniki, Tambitsy, Turastamozero, Verkhnee Myagrozero, Yu. Oleny Isl. Suillia humilis Meigen – Bol. Lelikovskiy Isl., Lipovitsy, Uzkaya Salma, Verkhnee Myagrozero, Vorobyi Suillia laevifrons Loew – Bol. Lelikovskiy Isl., Myagrozero, Podyelniki, Polya, Tipinitsy, Turastamozero, Volkostrov Isl., Vorobyi Suillia mikii Pokorny – Paleostrov Isl. Suillia nemorum Meigen – Turastamozero Suillia parva Loew – Podyelniki, Tipinitsy Suillia quadrilineata Czerny – Verkhnee Myagrozero Sphaeroceridae Crumomyia pedestris Meigen – Klimenicy Psilidae Chamaepsila atra Meigen – Eglov Isl., Kizhi Isl., Klimenicy, Kuivakhda Isl., Lelikovo, Lyudskoi Isl., Sennaya Guba, Vikshezero, Vorobyi Chamaepsila humeralis Zetterstedt – Kizhi Isl., Rogachev Isl., Vorobyi ? Chamaepsila nigra Fallén – Kizhi Isl. Chamaepsila nigricornis Meigen – Vorobyi Chamaepsila pallida Fallén – Kurgenitsy Chamaepsila pectoralis Meigen – Kopanets lake, Podyelniki ? Chamaepsila rosae Fabricius – Kizhi Isl., Vorobyi Psila imetaria L. – Eglov Isl., Khvost Isl., Rogachev Isl. Psila merdaria Collin – Sennaya Guba, Vikshezero Loxocera nigrifrons Macquart – Myal’ Isl. Chyliza vittata Meigen – Kosmozero Tanypezidae Strongylophthalmyia pictipes Frey – Kopanets lake, Polya, Vavlok Isl. Strongylophthalmyia ustulata Zetterstedt – Bol. Lelikovskiy Isl., Kopanets lake, Lipovitsy, Podyelniki, Polya Tanypeza longimana Fallén – Kopanets lake, Nizhneje Myagrozero, Podyelniki, Tipinitsy Lonchaeidae ? Dasiops occultus Collin – Vavlok Isl. Lonchaea laxa Collin – Uzkaya Salma Lonchaea patens Collin – Verkhnee Myagrozero Ulidiidae Homalocephala angustata Wahlberg – Podyelniki, Vegoruksy, Verkhnee Myagrozero, Vikshezero Homalocephala biumbrata Wahlberg – Kurgenitsy, Podyelniki, Tambitsy Melieria crassipennis Fabricius – Bol. Lelikovskiy Isl. Herina frondescentiae L. – Kuzaranda Tephritidae Urophora cuspidata Meigen – Lelikovo Urophora jaceana Hering – Lelikovo, Rogachev Isl., Sennaya Guba ? Urophora mauritanica Macquart – Vikshezero ? Urophora solsticialis L. – Lelikovo, Nizhneje Myagrozero, Oyatevschina, Sennaya Guba, Vorobyi Urophora stigma Loew – Kuzaranda, Sennaya Guba Rhagoletis cerasi L. – Nizhneje Myagrozero, Oyatevschina, Podyelniki, Vorobyi Reports of the Finnish Environment Institute 40 | 2014 331 Euleia heraclei L. – Rogachev Isl. Myoleja lucida Fallén – Kainos Isl., Klimenicy, Rogachev Isl., Vavlok Isl. Cryptaciura rotundiventris Fallén – Eglov Isl., Rogachev Isl., Volkostrov Isl. Chaetorellia jaceae Robineau-Desvoidy – Eglov Isl., Kuzaranda, Lelikovo, Paleostrov Isl., Rogachev Isl., Sennaya Guba, Vikshezero, Vorobyi Chaetorellia loricata Rondani – Eglov Isl., Kizhi Isl., Kurgenitsy, Lelikovo, Lyudskoi Isl., Rogachev Isl., Sennaya Guba Chaetostomella cylindrica Robineau-Desvoidy – Bol. Lelikovskiy Isl., Eglov Isl., Khvost Isl., Kizhi Isl., Kosmozero, Kuzaranda, Lelikovo, Oyatevschina, Podyelniki, Rogachev Isl., Tolvuya, Turastamozero, Vertilovo, Vikshezero, Vorobyi ? Terellia gynaecochroma Hering – Rogachev Isl. Terellia plagiata Dahlbom – Volkostrov Isl., Vorobyi Terellia ruicauda Fabricius – Kurgenitsy Terellia tussilaginis Fabricius – Kazhma Terellia winthemi Meigen – Polya Orellia scorzonerae Robineau-Desvoidy – Lelikovo, Lyudskoi Isl., Sennaya Guba Xyphosia miliaria Schrank – Verkhnee Myagrozero ? Campiglossa doronici Loew – Vikshezero Tephritis angustipennis Loew – Tipinitsy Tephritis conura Loew – Kizhi Isl. Tephritis hyoscyami L. – Polya Hippoboscidae Ornithomya chloropus Bergroth – Klimenicy, Uzkaya Salma Lipoptena cervi L. – Tipinitsy Fanniidae Fannia parva Stein – Vorobyi Fannia polychaeta Stein – Polya Fannia posticata Meigen – Podyelniki Fannia ringdahlana Collin – Vikshezero Fannia rondanii Strobl – Vikshezero Fannia serena Fallén – Rogachev Isl. Fannia sociella Zetterstedt – Nizhneje Myagrozero, Podyelniki, Turastamozero, Verkhnee Myagrozero Fannia spathiophora Malloch – Lyudskoi Isl., Polya, Vikshezero Muscidae Mydaea afinis Myade – Polya, Uzkaya Salma Mydaea humeralis Robineau-Desvoidy – Eglov Isl. Mydaea orthonevra Macquart – Lipovitsy Mydaea ortonevra Macquart – Turastamozero Mydaea urbana Meigen – Turastamozero ? Helina depuncta Fallén – Podyelniki Helina evecta Harris – Eglov Isl., Khvost Isl., Nizhneje Myagrozero, Podyelniki, Polya, Vegoruksy Helina impuncta Fallén – Eglov Isl. Helina pubiseta Zetterstedt – Lipovitsy, Polya Helina subvittata Seguy – Eglov Isl. Graphomyia maculata Scopoli – Kurgenitsy ? Spilogona carbonella Zetterstedt – Lipovitsy Spilogona contractifrons Zetterstedt – Eglov Isl., Podyelniki, Polya, Vegoruksy ? Spilogona karelica Tiensuu – Podyelniki Coenosia intermedia Fallén – Lipovitsy, Podyelniki 332 Reports of the Finnish Environment Institute 40 | 2014 Coenosia mollicula Fallén – Podyelniki, Turastamozero, Uzkaya Salma, Verkhnee Myagrozero Coenosia ruipalpis Meigen – Khvost Isl., Podyelniki Coenosia trilineella Zetterstedt – Khvost Isl., Uzkaya Salma Thricops albibasalis Zetterstedt – Eglov Isl., Uzkaya Salma Thricops cunctans Meigen – Eglov Isl., Khvost Isl., Rogachev Isl., Verkhnee Myagrozero Thricops diaphanus Wiedemann – Turastamozero, Uzkaya Salma, Vikshezero Thricops genarum Zetterstedt – Podyelniki Thricops lividiventris Zetterstedt – Podyelniki Thricops longipes Zetterstedt – Eglov Isl. Thricops nigrifrons Robineau-Desvoidy – Eglov Isl. Thricops nigritellus Zetterstedt – Lyudskoi Isl. Thricops semicinereus Wiedemann – Eglov Isl., Lipovitsy, Nizhneje Myagrozero, Turastamozero, Vegoruksy ? Drymeia hamata Fallén – Nizhneje Myagrozero Hydrotaea borussica Stein – Lipovitsy, Polya, Turastamozero, Uzkaya Salma, Vorobyi Hydrotaea militaris Meigen – Lipovitsy Hydrotaea pandellei Stein – Eglov Isl., Kosmozero, Lipovitsy, Oyatevschina, Polya, Turastamozero, Uzkaya Salma Hydrotaea pellucens Portschinsky – Ernitskiy Isl., Kosmozero, Uzkaya Salma Hydrotaea velutina Robineau-Desvoidy – Turastamozero Muscina levida Harris – Eglov Isl., Podyelniki Phaonia angelicae Scopoli – Eglov Isl., Lipovitsy, Nizhneje Myagrozero, Polya, Turastamozero Phaonia errans Meigen – Lipovitsy, Polya, Uzkaya Salma Phaonia pallida Fabricius – Turastamozero ? Morellia hortorum Fallén – Podyelniki, Polya, Uzkaya Salma Morellia podagrica Loew – Lipovitsy, Polya, Uzkaya Salma Mesembrina mystacea L. – Lipovitsy Mesembrina resplendens Wahlberg – Bol. Lelikovskiy Isl., Klimenicy, Lipovitsy, Polya, Turastamozero, Uzkaya Salma Stomoxys calcitrans L. – Podyelniki Anthomyiidae Botanophila brunnelinea Zetterstedt – Nizhneje Myagrozero Botanophila fugax Meigen – Nizhneje Myagrozero Botanophila hucketti Ringdahl – Nizhneje Myagrozero Hydrophoria lancifer Harris – Eglov Isl., Lipovitsy, Turastamozero, Vegoruksy Zaphne ambigua Fallén – Podyelniki Zaphne caudata Zetterstedt – Eglov Isl., Podyelniki Anthomyia monilis Meigen – Ernitskiy Isl., Kizhi Isl., Kuivakhda Isl., Lelikovo, Lyudskoi Isl., Myal’ Isl., Sennaya Guba, Shunevskiy Isl., Turastamozero, Vorobyi Anthomyia plurisetosa Brullé – Oyatevschina Anthomyia pluvialis L. – Vorobyi Anthomyia procellaris Rondani – Rogachev Isl. Eutrichota frigida Zetterstedt – Polya Pegomya circumpolaris Ackland et Grifiths – Turastamozero Pegomya lavoscutellata Zetterstedt – Lipovitsy Pegomya fulgens Meigen – Podyelniki Pegomya geniculata Bouché – Lipovitsy, Polya, Uzkaya Salma Pegomya incisiva Stein – Podyelniki Pegomya maculata Stein – Lipovitsy, Turastamozero Pegomya pulchripes Loew – Podyelniki Reports of the Finnish Environment Institute 40 | 2014 333 Pegomya scapularis Zetterstedt – Polya, Turastamozero Pegomya zonata Zetterstedt – Lipovitsy Pegoplata inirma Meigen – Nizhneje Myagrozero Pegoplata juvenilis Stein – Eglov Isl. Heterostylodes pilifera Zetterstedt – Podyelniki Delia coarctata Fallén – Nizhneje Myagrozero Delia fabricii Holmgren – Nizhneje Myagrozero Delia lorilega Zetterstedt – Nizhneje Myagrozero Delia lophota Pandellé – Turastamozero Delia platura Meigen – Nizhneje Myagrozero, Turastamozero Scathophagidae Parallelomma vittatum Meigen – Kopanets lake, Lelikovo, Lyudskoi Isl., Paleostrov Isl., Turastamozero Leptopa iliformis Zetterstedt – Khvost Isl. Cordilura albipes Fallén – Eglov Isl., Kurgenitsy, Lipovitsy, Rogachev Isl., Velikaya Niva, Vikshezero Cordilura ciliata Meigen – Kopanets lake, Kurgenitsy, Rogachev Isl., Vorobyi Cordilura picipes Meigen – Bol. Lelikovskiy Isl., Eglov Isl., Ernitskiy Isl., Kizhi Isl., Lyudskoi Isl. Cordilura pubera L. – Kizhi Isl., Tipinitsy, Velikaya Niva Cordilura pudica Meigen – Klimenicy Megaphthalma pallida Fallén – Bol. Lelikovskiy Isl., Kopanets lake, Kurgenitsy, Lyudskoi Isl., Myagrozero, Tambitsy, Turastamozero, Uzkaya Salma, Velikaya Niva, Vikshezero, Volkostrov Isl., Vorobyi Hexamitocera loxocerata Fallén – Tolvuya Nanna armillata Zetterstedt – Vorobyi Nanna lavipes Fallén – Kizhi Isl., Lyudskoi Isl., Oyatevschina Nanna inermis Becker – Klimenicy Cleigastra apicalis Meigen – Kurgenitsy, Lelikovo Conisternum obscurum Fallén – Vorobyi Scathophaga furcata Say – Klimenicy, Lyudskoi Isl., Myagrozero Scathophaga inquinata Meigen – Rogachev Isl., Vorobyi Scathophaga stercoraria L. – Kizhi Isl., Kuzaranda Scathophaga suilla Fabricius – Ernitskiy Isl., Kizhi Isl., Oyatevschina, Tambitsy, Vorobyi Chaetosa punctipes Meigen – Kizhi Isl., Kopanets lake, Lelikovo, Sennaya Guba Microprosopa pallidicauda Zetterstedt – Kopanets lake, Tipinitsy Hydromyza livens Fabricius – Podyelniki Staegeria kunzei Zetterstedt – Klimenicy, Vorobyi Pogonota barbata Zetterstedt – Klimenicy, Kopanets lake, Kurgenitsy, Tipinitsy, Vegoruksy, Verkhnee Myagrozero Calliphoridae Bellardia viarum Robineau-Desvoidy – Kizhi Isl. Calliphora vomitoria L. – Podyelniki Cynomya mortuorum L. – Eglov Isl., Kizhi Isl. Eurychaeta palpalis Robineau-Desvoidy – Oyatevschina Lucilia bufonivora Moniez – Eglov Isl., Podyelniki Sarcophagidae Amobia oculata Zetterstedt – Podyelniki Metopia grandii Venturi – Podyelniki Agria mamillata Pandellé – Oyatevschina, Vorobyi Brachicoma devia Fallén – Eglov Isl., Nizhneje Myagrozero, Oyatevschina, Podyelniki, Vorobyi 334 Reports of the Finnish Environment Institute 40 | 2014 Sarcophaga albiceps Meigen – Nizhneje Myagrozero, Podyelniki, Vegoruksy Sarcophaga aratrix Pandellé – Eglov Isl., Klimenicy, Nizhneje Myagrozero, Vikshezero Sarcophaga caerulescens Zetterstedt – Eglov Isl., Nizhneje Myagrozero, Vorobyi Sarcophaga carnaria L. – Paleostrov Isl. Sarcophaga haemorrhoides Böttcher – Nizhneje Myagrozero Sarcophaga melanura Meigen – Rogachev Isl. Sarcophaga schuetzei Kramer – Eglov Isl. Sarcophaga sexpunctata Fabricius – Eglov Isl. Sarcophaga similis Meade – Kizhi Isl., Podyelniki Sarcophaga socrus Rondani – Sennaya Guba Sarcophaga subulata Pandellé – Podyelniki Sarcophaga uliginosa Kramer – Eglov Isl., Vikshezero Sarcophaga vagans Meigen – Oyatevschina Sarcophaga variegata Scopoli – Eglov Isl., Kizhi Isl., Oyatevschina, Rogachev Isl., Vikshezero, Vorobyi Tachinidae ? Paratryphera barbatula Rondani – Podyelniki ? Winthemia quadripustulata Fabricius – Turastamozero Bactromyia aurulenta Meigen – Podyelniki Aplomya coninis Fallén – Turastamozero Allophorocera ferruginea Meigen – Nizhneje Myagrozero Exorista larvarum L. – Podyelniki Medina collaris Fallén – Podyelniki Medina multispina Herting – Podyelniki Medina separata Meigen – Podyelniki ? Actia pilipennis Fallén – Podyelniki, Vorobyi Ceromya silacea Meigen – Eglov Isl., Lipovitsy, Podyelniki, Polya, Turastamozero, Uzkaya Salma Tachina fera L. – Nizhneje Myagrozero, Oyatevschina Tachina grossa L. – Turastamozero Nowickia marklini Zetterstedt – Eglov Isl., Nizhneje Myagrozero, Podyelniki, Rogachev Isl., Turastamozero Ernestia rudis Fallén – Eglov Isl. Eurithia connivens Zetterstedt – Podyelniki Halidaya aurea Egger – Podyelniki Eriothrix rufomaculatus DeGeer – Vorobyi Voria ruralis Fallén – Eglov Isl. Thelaira nigripes Fabricius – Nizhneje Myagrozero, Podyelniki, Vegoruksy ? Thelaira solivaga Harris – Oyatevschina Subclytia rotundiventris Fallén – Turastamozero Gymnosoma nudifrons Herting – Paleostrov Isl. Phasia aurulans Meigen – Vorobyi Phasia hemiptera Fabricius – Klimenicy ? 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SТХПЯОrЛОrР, H. 1987. MКЩЩТЧР ЭСО FТЧЧТsС CСrвsШЦОХТНКО (CШХОШЩЭОrК). I. – NШЭЮХКО EЧЭШЦШХШРТМКО 67: 5–16. SТХПЯОrЛОrР, H. 2010. EЧЮЦОrКЭТШ rОЧШЯКЭК CШХОШЩЭОrШrЮЦ FОЧЧШsМКЧНТКО, DКЧТКО ОЭ BКХЭТКО. – SКСХЛОrРТК 16(2): 1–144. HОХsТЧФТ, FТЧХКЧН, ISSN 1237–3273. SТХПЯОrЛОrР, H. & BТsЭröЦ, O. 1981. KКrЭОrТЧР КЯ FТЧХКЧНs ХфЧРСШrЧТЧРКr (CШХОШЩЭОrК, CОrКЦЛвМТНКО). – NШЭЮХКО EЧЭШЦШХШРТМКО 61: 15–29. SЭКrý, J. & SКХЦОХК, J. 2004. RОНОsМrТЩЭТШЧ КЧН ЛТШХШРв ШП Limonia badia (АКХФОr) (DТЩЭОrК: LТЦШЧТТНКО). – EЧЭШЦШХШРТМК FОЧЧТМК 15 (1): 41–47. SöНОrЦКЧ, G. & LОТЧШЧОЧ, R. 2003. SЮШЦОЧ ЦОsТЩТsЭТТsОЭ УК ЧТТНОЧ ЮСКЧКХКТsЮЮs. – TrОЦОб PrОss Oв, HОХsТЧФТ..420 Щ. TТОЧsЮЮ, L. 1933. SШrЭКЯКХКЧ ЩТЭтУтЧ sЮНОЧФШrОЧЧШТsОЭ. – AЧЧКХОs SШМТОЭКЭТs ГШШХШРТМКО–BШЭКЧТМКО FОЧЧТМКО. VКЧКЦШ 14(4): 287–370. VКХХО, K. J. 1927. ГЮr KОЧЧЭЧТs НОr OНШЧКЭОЧПКЮЧК FТЧЧХКЧНs III. ErРтЧгЮЧРОЧ ЮЧН гЮsтЭгО. – AМЭК SШМТОЭКЭТs ЩrШ FКЮЧК ОЭ FХШrК FОЧЧТМК 56 (11): 1–36. VКХХО, K. J. 1952. DТО ШsЭПОЧЧШsФКЧНТОsМСОЧ OНШЧКЭОЧ (ГЮr KОЧЧЭЧТs НОr OНШЧКЭОЧПКЮЧК FТЧЧХКЧНs VI). – AМЭК EЧЭШЦШХШРТМК FОЧЧТМК 10: 1–59. VТrКЦШ, J. 1969. ГЮr KОЧЧЭЧТs НОr MТЧТОrОrПКЮЧК FТЧЧХКЧНs. оЛОr НТО АТrЭsЩlКЧгОЧ ЮЧН НТО VОrЛrОТЭЮЧР НОr ЦТЧТОrОЧНОЧ BХКЭЭаОsЩОЧ (HвЦ., TОЧЭСrОНТЧШТНОК). – AЧЧКХОs EЧЭШЦШХШРТМТ FОЧЧТМТ 35: 3−44. АШХП, H. 1967. DТО АОРаОsЩОЧ FТЧЧХКЧНs. – AМЭК EЧЭШЦШХШРТМК FОЧЧТМК 23: 1–46. 338 Reports of the Finnish Environment Institute 40 | 2014 3.7 Localities in Zaonezhye area used in species lists of vascular plants, bryophytes, lichens, fungi and insects, and their toponyms Alexei V. Kravchenko*#, Pertti Uotila** and Jevgeni Jakovlev*** * Forest Research Institute of the Karelian Research Center of Russian Academy of Sciences. Petrozavodsk, 11 Pushkinskaya St., RU-185910 Petrozavodsk, Karelia, Russia ** Botany Unit, Finnish Museum of natural History, P.O.Box 7, FI-00014 University of Helsinki, Finland ***The Finnish Enviroment Institute (SYKE) Mechelininkatu 34a. P.O.Box 140, FIN-00251 Helsinki, Finland #Corresponding author E-mail: alex.kravchen@mail.ru The accuracy of collection localities given on the labels of herbarium specimens and insect collections, as well in the literature, is very variable. In most cases the geographical names have been taken from maps in use during particular historical periods. Several place names have changed over time. All found localities, where species have been recorded in Zaonezhye area, are included in the table, with their known toponyms. At present, many villages in the table have been abandoned. All place names indicated on old labels could not be found from Mullonen et al. (2013) or other sources (printed papers, maps, internet sources), and such names are excluded from the table. In some cases two or more places have the same name, and they are excluded as well. Coordinates (if not otherwise mentioned) indicate the center of the settlement, lake, island, peninsula, etc. The actual collection place is located within the locality given and usually well-marked on the maps or in its more or less immediate vicinity (labels often include words like “near, “close”, “next to”, etc.). * RЮssТКЧ ЧКЦОs КrО РТЯОЧ КММШrНТЧР ЭШ: MЮХХШЧОЧ, I.I., AгКrШЯК, I.V. & GОrН, A.S. 2013. . ., . ., . . ДCКЭКХШР ШП РОШРrКЩСТМКХ ЩХКМО ЧКЦОs ШП ГКШЧОгСвОЖ. KКrОХТКЧ RОsОКrМС CОЧЭОr ШП RЮssТКЧ AМКНОЦв ШП SМТОЧМОs. PОЭrШгКЯШНsФ. 251 Щ. (IЧ RЮssТКЧ). English (shortened in parentheses) Azhepnavolok Russian name* Spelling variants Type of the place and Finnish names Decimal coordinates AгСОЛЧКЯШХШФ AsСОЛ 62.628826 N; 34.962074 E Peninsula Reports of the Finnish Environment Institute 40 | 2014 339 VТХХКРО 62.251903 N; 35.039493 E IsХКЧН 61.969199 N; 35.261581 E IsХКЧН 61.963382 N; 35.129745 E VТХХКРО 62.070505 N; 35.197037 E Bukolnikovskiy IsХКЧН 62.006502 N; 35.199783 E Butenevo VТХХКРО 62.532975 N; 35.363165 E Chelozero Lake 62.416746 N; 34.983793 E VТХХКРО 62.632001 N; 34.648367 E Dolgiy IsХКЧН 62.111704 N; 35.267761 E Eglov IsХКЧН 62.134774 N; 35.164249 E Ernitskiy IsХКЧН 61.989196 N; 35.168057 E FОНШЭШЯШ VТХХКРО 62.660191 N; 34.682274 E FШЦТЧШ VТХХКРО 62.561743 N; 34.887663 E TаТЧ ЯТХХКРО ШЧ B. Klim. 61.978328 N; 35.213344 E GКЛШsЭrШЯ IsХКЧН 62.483694 N; 34.557043 E Gizhozero Lake 62.469416 N; 35.084604 E Gryz IsХКЧН 62.022556 N; 35.222379 E Gryznavolok Cape on B. Klim. 62.022556 N; 35.222379 E IгЛЮsСОМСЧвТ IsХКЧН 62.111657 N; 34.954397 E Kainos IsХКЧН 62.584217 N; 35.405647 E Kalgostrov IsХКЧН 62.004324 N; 35.128652 E Kanev IsХКЧН 62.010591 N; 35.215688 E Karasozero VТХХКРО КЧН ХКФО 62.407075 N; 34.890936 E Kaskoselga VТХХКРО 62.246321 N; 35.467176 E Kazhma VТХХКРО 62.550795 N; 34.839851 E Bolnichnyi Limosaari KХТЦsФТУ Klimetskoi Klimenetskiy . Bolshoi Klimenetsky Bolshoi Klimetskiy (B. Klim., Bol. Klim.) Bolshoi Lelikovskiy (B. Lelik., Bol. Lelik.) Boyarstchina Boyarschina DТКЧШЯК-GШrК DТКЧШаК-GШrК Dianova Gora Garnitsy (Pervye & VЭШrвО) 340 ( ) Reports of the Finnish Environment Institute 40 | 2014 Garnitsa Limoluoto IsХКЧН 62.084754 N; 35.213453 E Khvost IsХКЧН 62.149371 N; 35.152435 E Klim Nos Peninsula 62.552257 N; 35.343228 E Klimenitsy VТХХКРО ШЧ B. Klim. (former monastery) 61.849696 N; 35.180698 E Lake 62.033892 N; 35.124841 E KШrЛШгОrШ Lake 62.206441 N; 35.287818 E Koselga VТХХКРО ШЧ B. Klim. 62.003596 N; 35.321121 E Kosmozero Lake 62.447286 N; 34.941034 E Kosmozero VТХХКРО 62.334634 N; 35.057163 E Krokhino VТХХКРО 62.363944 N; 35.270308 E Kuivakhda IsХКЧН 61.959308 N; 35.170975 E Kurgenitsy VТХХКРО ШЧ B. Klim. 62.071655 N; 35.286457 E VТХХКРО 62.374627 N; 35.525054 E Ladmozero Lake 62.536845 N; 34.683295 E Ladmozero VТХХКРО 62.56553 N; 34.664413 E VТХХКРО 62.287764 N; 34.876731 E LКЦЛТЧsФТО IsХОs 61.957767 N; 35.09107 E Lelikozero VТХХКРО КЧН ХКФО 62.303488 N; 34.93185 E Kizhi Kopanetz Kuzaranda LКЦЛКsrЮМСОв Kischi Kiischi Kishi Kopanets Kusaranda Kuusiranta LКЦЛКs RЮМСОТ Lichkov See: Lyudskoy Lizhma VТХХКРО 62.378977 N; 34.515067 E Lipovitsy VТХХКРО 62.115029 N; 35.060123 E Longasy VТХХКРО ШЧ B. Klim. 61.988603 N; 35.210739 E IsХКЧН 61.965502 N; 35.175376 E Lukova Bay on B. Klim. 61.913642 N; 35.188769v Medvedevo VТХХКРО 62.532611 N; 34.852555 E Medvezhia Gora HТХХ КЧ B. KХТЦ. 61.891034 N; 35.217605 E Megostrov IsХКЧН 62.563731 N; 35.42894 E MОХШТРЮЛК VТХХКРО КЧН ЛКв 62.512201 N; 34.588486 E Lyudskoi Lyudskoy LТМСФШЯ Reports of the Finnish Environment Institute 40 | 2014 341 VТХХКРО КЧН island 62.289042 N; 34.831215 E Motalovo VТХХКРО ШЧ B. Klim. 61.974821 N; 35.237151 E Myal’ IsХКЧН 62.000035 N; 35.147269 E Mysh’i IsХОs 62.013107 N; 35.080665 E Nikonova Gora VТХХКРО 62.573608 N; 34.824744 E Nizhnee Myagrozero VТХХКРО КЧН ХКФО 62.512977 N; 34.769135 E VТХХКРО 62.586729 N; 34.921611 E IsХКЧН 61.985826 N; 35.200828 E Mizhostrov Okatovstchina Mezhostrov Okatovschina Orozh Oyatevstchina Oyatevschina VТХХКРО 62.082301 N; 35.180677 E Padmozero Padmosero Lake 62.493025 N; 35.170732 E Paleostov IsХКЧН 62.565773 N; 35.252533 E Petry VТХХКРО ШЧ B. Klim. 62.026242 N; 35.247021 E Pod’elniki Podyelniki VТХХКРО 62.110299 N; 35.169004 E Polya VТХХКРО 62.304761 N; 35.299123 E VТХХКРО 62.492318 N; 35.283284 E Lake 62.497105 N; 35.090828 E Pryalichinskaya PШУКХТЭsТЧsФКУК Putkozero 342 Radkolie Radkolye Radkol’e Cape on B. Lelik. 61.943054 N; 35.098279 E Radkolie Radkol’e IsХКЧН 61.995407 N; 35.1872 E Rechka VТХХКРО 62.095981 N; 35.178617 E Rechnoy IsХКЧН 62.590887 N; 35.211506 E Regimatka VТХХКРО 62.515407 N; 34.887147 E Rogachev IsХКЧН 62.12555 N; 35.185621 E Rogostrov IsХКЧН 62.002221 N; 35.185387 E 62.15173 N; 34.94471 E Rugozero RЮЮСТУтrЯТ Lake SОЧЧКвК GЮЛК SОЧЧШРЮЛК HОТЧтХКСЭТ VТХХКРО ШЧ 61.995891 N; B. KХТЦ. КЧН ЛКв 35.208143 E Seredka VТХХКРО ШЧ B. Klim. 62.044124 N; 35.245565 E Severnyi Myshyi IsХКЧН 62.015097 N; 35.078784 E Severnyi Sokoliy IsХКЧН 62.371764 N; 34.749412 E Reports of the Finnish Environment Institute 40 | 2014 Shiltya VТХХКРО 62.411273 N; 35.174178 E Shunevskiy IsХКЧН 62.139556 N; 35.21371 E VТХХКРО 62.594115 N; 34.93187 E Schsuchia Bay on B. Klim. 61.856936 N; 35.207616 E Spirovka VТХХКРО 62.437613 N; 35.133151 E HТХХ 62.572901 N; 34.696694 E TКЦЛТЭsв VТХХКРО 62.229184 N; 35.55747 E TОХЩШгОrШ VТХХКРО КЧН ХКФО 62.613468 N; 34.885905 E TОХвКЭЧТФШЯШ VТХХКРО 62.047867 N; 35.20233 E TОrОФСШЯШ VТХХКРО 62.318605 N; 35.065858 E TТЩТЧТЭsв VТХХКРО 62.189107 N; 35.414819 E VТХХКРО 62.51028 N; 35.285149 E TШХЯЮвsФТв BШr VТХХКРО 62.503503 N; 35.241239 E TШХsЭвТ NКЯШХШФ Cape 62.298311 N; 35.575323 E Sunku Schungu Shun’ga Shunga - Sypun Gora TШХЯЮвК TЮХЯШУК TШХЯШУК TЮХаШУК TШХаШУК TЮrКsЭКЦШгОrШ TЮrКsЭКЦ VТХХКРО КЧН ХКФО 62.552306 N; 34.714546 E Unitsa Unitza VТХХКРО 62.597279 N; 34.460144 E Bay of Lake Onega 62.486782 N; 34.583397 E VТХХКРО 62.173124 N; 35.272083 E VТХХКРО 62.135474 N; 34.930992 E Uzkie VТХХКРО 62.437475 N; 34.958559 E VКЛХШФ IsХКЧН 62.575909 N; 35.410805 E VКЧМСШгОrШ Lake 62.529951 N; 34.800377 E VКrЧКЯШХШФ Cape 62.162788 N; 35.462198 E VТХХКРО 62.218831 N; 34.883711 E Lake 62.136668 N; 35.115797 E VТХХКРО КЧН ЛКв 62.251825 N; 35.068103 E UЧТЭsФКвК GЮЛК UsЭ’-ВКЧНШЦК Uzkie Salmy VОРШrЮФsК VОРШrЮФsв - UsЭУКЧНШЦК Uzkaya Salma VОРКrЮs АТРШrЮs VОФСФШгОrШ VОХТФКвК GЮЛК АОХТФКУК-РЮЛК VОХТФКУК GЮЛК Suurlahti Reports of the Finnish Environment Institute 40 | 2014 343 VОХТФКвК NТЯК VТХХКРО 62.362816 N; 35.223443 E VОrФСЧОО Myagrozero VТХХКРО КЧН ХКФО 62.482016 N; 34.819946 E VОrЭТХШЯШ VТХХКРО 62.00665 N; 35.181214 E VШТЧКЯШХШФ VТХХКРО КЧН peninsula 61.97791 N; 35.33571 E IsХКЧН 62.112554 N; 35.207836 E VШrШЛ´Т VШrШЛвТ VТХХКРО ШЧ B. Klim. 62.056191 N; 35.251095 E VШrШЧТЧsФШО VТХХКРО 62.471389 N; 35.205934 E VТХХКРО 62.519262 N; 35.366265 E Zimnyaya Mountain 62.386252 N; 35.052639 E Zharnikovo VТХХКРО 62.056789 N; 35.207882 E VТХХКРО 62.103317 N; 35.177155 E IsХКЧН 61.992243 N; 35.1928 E IsХКЧН 62.045831 N; 35.363579 E VШХФШsЭrШЯ Zaselezhye ГЮЛШЯШ VОХТФКУК NТЯК VШХФ OsЭrШЯ Susisaari ГКsОХОгУО ГЮЛШЯК ВКЦ ВЮгСЧвТ OХОЧТв (ВЮ. OХОЧТв) ВЮгСЧв OХОЧв Abandoned villages in Zaonezhye Peninsula (Photo Boris Rayevsky). 344 Reports of the Finnish Environment Institute 40 | 2014 Karelian and Finnish botanists and entomologists on the Ekolog ship. July 2004. In front: Alexei Kravchenko (left),and Pertti Uotila (right); behind, left to right: Andrei Humala, Alexei Polevoi, Jevgeni Jakovlev (Photo Tapio Lindholm). Reports of the Finnish Environment Institute 40 | 2014 345 Karelian botanists on the shore of Lake Onega. Losyi Islands. July 2004. Left to right: Elena Gnatyuk, Alexei Kravchenko and Oleg Kuznetsov (Photo Tapio Lindholm). 346 Reports of the Finnish Environment Institute 40 | 2014 Aconitum septentrionale – an eastern («Siberian») species which can be found from Zaonezhye close to the western limit of its distribution area (Photo Tapio Lindholm). Reports of the Finnish Environment Institute 40 | 2014 347 Polemonium caeruleum in blossom on meadows along the Kuzaranda shore of Lake Onega (Photo Tapio Lindholm). 348 Reports of the Finnish Environment Institute 40 | 2014 Luxuriant shore meadow of Allium schoenoprasum and Melampirum nemorosum on the shore of Lukova Bay (Photo Pertti Uotila). Reports of the Finnish Environment Institute 40 | 2014 349 Rauno Ruuhijärvi (in front) and Mikko Piiranen (behind) on the Kuzaranda shore of Lake Onega. The adults of Black-veined White butterly (Aporia crataegi) are very abundant on mineralized soils (Photo Pertti Uotila). 350 Reports of the Finnish Environment Institute 40 | 2014 Ecolog, the ship of the Karelian Research Center of Russian Academy of Sciences (Photo Tapio Lindholm). Reports of the Finnish Environment Institute 40 | 2014 351 Sunset in Vegoruksa Bay of Lake Onega (Photo Boris Rayevsky). 352 Reports of the Finnish Environment Institute 40 | 2014 Tapio Lindholm (Photo Jevgeni Jakovlev). Reports of the Finnish Environment Institute 40 | 2014 353 Olli Manninen (left) and Alexei Kravchenko (right) found a rare fungus, Piloporia sajanensis in herb-rich spruce forest in the vicinity of Uzkie Salmy (Photo Jevgeni Jakovlev). 354 Reports of the Finnish Environment Institute 40 | 2014 Andrei Humala (left) and Alexei Polevoi (right) in herb-rich spruce forest with Aconitum septentrionale (Photo Jevgeni Jakovlev). Reports of the Finnish Environment Institute 40 | 2014 355 356 Reports of the Finnish Environment Institute 40 | 2014 DOC U ME N TAT ION PAGE Publisher Finnish Environment Institute Author(s) Tapio Lindholm, Jevgeni Jakovlev and Alexei Kravchenko (eds.) Title of publication Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia Publication series and number Reports of the Finnish Environment Institute 40/2014 Date March 2015 Theme of publication Parts of publication/ other project publications The publication is available in the internet: www.syke.i/publications | helda.helsinki.i/syke | www.bpan.i Abstract Zaonezhye Peninsula (Zaonezhsky Peninsula; in Russian transcription) is situated on the northwestern coast of Lake Onega in the Republic of Karelia, Russia. The territory of Zaonezhye is unique in that it contains nearly every type of terrain and unconsolidated sediment known in the vast expanses of northwest Russia. It is also eastern part of Fennoscandian shield. It is characterized by a high diversity of basic limestone and carbonate rocks that determine the fertility of local soils as well as the unique diversity of habitats, lora and fauna. Numerous rare calciphile plant and lichen species are found here, as well as rich, eutrophic wetlands. Long-term farming and animal husbandry have led to a large number of grassland communities in the area. As a result, a mosaic structure of diverse habitats has evolved here. Europe’s second largest lake, Lake Onega, with its clear and deep waters also affect the local climate, making it milder. This report provides for the irst time detailed species lists of vascular plants, bryophytes, lichens, wood-growing fungi and insects covering the entire Zaonezhye Peninsula, Kizhi archipelago and other adjacent islands. The most important sites for protection were observed, and six new nature monuments in the southern and southerneast parts of Zaonezhye Peninsula are recommended to be established. This publication contents following articles characterizing nature of Zaonezhye area: 1. Geology and physical geography: 1.1.Geological description, 1.2. Geomorphology and Quaternary deposits, 1.3. Hydrological characteristics, 1.4. Soil cover, 1.5. Palaeogeography, 1.6. Existing and planned protected areas; 2. Landscapes and ecosystems: 2.1. Modern landscapes of Zaonezhye, 2.2. Landscape structure, 2.3. Structure of the forest covered land and forest stands, 2.4. Forest structures, 2.5. Mires, 2.6. Meadows; 3. Flora and fauna: 3.1.Vascular plants, 3.2. Bryophyte lora, 3.3 Species list of lichens and allied fungi, 3.4. Red listed and indicator lichens, 3.5. Aphyllophoroid fungi and 3.6. Insect fauna. 3.7. Localities in Zaonezhye area used in species lists of vascular plants, bryophytes, lichens, fungi and insects, and their toponyms. Keywords geology, palaeogeography, landscapes, forest, mires, meadows, vascular plants, bryophytes, lichens, wood-growing fungi, insects, biodiversity, nature conservation, Zaonezhye Peninsula, Kizhi archipelago, Onega Lake, Republic of Karelia Financier/ commissioner Nordic Council of Ministers; Ministries of the Environment of Finland, Norway, Sweden; Ministries for Foreign Affairs of Finland, Norway and Sweden, Directorate of regional protected areas of the Republic of Karelia ISBN 978-952-11-4404-2 (pbk.) ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 (print.) ISSN 1796-1726 (online) No. of pages 359 Language English Restrictions public Price (incl. tax 8 %) For sale at/ distributor Finnish Environment Institute (SYKE), neuvonta P.O. Box 140, FI-00251 Helsinki, Finland, Email: neuvonta.syke@ymparisto.i Financier of publication Finnish Environment Institute (SYKE), P.O. Box 140, FI-00251 Helsinki, Finland Phone +358 295 251 000 Printing place and year Juvenes Print, 2015 Reports of the Finnish Environment Institute 40 | 2014 357 И И ИЯ И ЦИИ И А 2015 , ( ) ( .) BТogОogrКpСy, lКnНscКpОs, ОcosystОms КnН spОcТОs oП ZКonОzСyО PОnТnsulК, Тn LКkО OnОgК, RussТКn KКrОlТК ( , , , ) 40 / 2014 Т / : , ааа.sвФО.i/puЛlТМКtТons е СОlНК.СОlsТnФТ.i/sвФО е ааа.ЛpКn.i Ч − , , .Э , , - . – . , , . . , , – , , , , 2.2. : 3.1. , 1.4. , 3.5. , К , Ф , - , 1.5. , 2.4. , 3.2. , 3.3 , 3.6. , , ( , , , , , . : 1. , 1.3. : 2.1. C , 2.5. 3.7. , , . , . ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 ( Ш ) Ц %) (SВKE), P.O. Boб 140, FI-00251 HОlsТnФТ, FТnlКnН, EmКТl: nОuЯontК.sвФО@вmpКrТsto.i JuЯОnОs PrТnt, 2015 358 Reports of the Finnish Environment Institute 40 | 2014 ( , , , ISSN 1796-1726 ( (SВKE), P.O. Boб 140, FI-00251 HОlsТnФТ, FТnlКnН FТnnТsС EnЯТronmОnt InstТtutО (SВKE), P.O. Boб 140, FI-00251 HОlsТnФТ, FТnlКnН : + 358 0295 251 000 Ф , ; 3. , 360 / ), 3.4. , 2.6. , , ; ; ) , 1.6. , . , , ISBN 978-95211-4404-2- ( , , Ш / ; 2. , 2.3. , 1.2. , . . : 1.1. , . , . , , , , . ) 8 KU VA I LU LEHTI Julkaisija Suomen ympäristökeskus Julkaisuaika maaliskuu 2015 Tekijä(t) Tapio Lindholm, Jevgeni Jakovlev ja Alexei Kravchenko (toim.) Julkaisun nimi Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia (Äänisenniemen alueen biogeograia, maisemat ja lajisto. Ääninen,Venäjän Karjala) Julkaisusarjan nimi ja numero Suomen ympäristökeskuksen raportteja 40/2014 Julkaisun teema Julkaisun osat/ muut saman projektin tuottamat julkaisut Julkaisu on saatavana internetistä: www.syke.i/julkaisut | helda.helsinki.i/syke | www.bpan.i Tiivistelmä Äänisenniemi, venäjäksi , sijaitsee Äänisen luoteisosassa Karjalan tasavallassa Venäjällä. Äänisenniemi on maaperällisesti monimuotoinen ja siellä on lähes kaikkia maaston tyyppejä ja irtaimia maalajeja, joita esiintyy laajalla Venäjän alueella. Se on myös itäistä osaa Fennoskandian kilvestä. Alueelle ovat tyypillisiä kalkkikivi ja muut emäksiset kivilajit, mistä johtuu maaperän rehevyys sekä elinympäristöjen ja lajiston rikkaus. Lukuisia kalkinvaatija putkilokasveja ja jäkäliä esiintyy täten alueella. Alueella on myös runsaasti lettosoita. Pitkäaikainen asutushistoria ja sen karja- ja maatalous on luonut alueelle runsaasti maatalousmaata, joka nyt on niittyinä. Tämä lisää Äänisenniemen elinympäristökirjoa. Euroopan toiseksi suurin järvi Ääninen, jossa on syvä ja kirkas vesi, tuo oman leudomman paikallisilmaston Äänisenniemelle. Tämä raportti sisältää runsaasti uutta tietoa putkilokasveista, sammalista, jäkälistä, käävistä ja hyönteisistä Äänisenniemeltä ja siihen liittyviltä saarilta, mukaan lukien Kiźin saarelta. Suojelun kannalta tärkeimpiä alueita inventoitiin ja kuutta uutta suojelualuetta ehdotetaan perustettavaksi Äänisenniemen eteläosiin. Tämä julkaisu käsittää seuraavat artikkelit Äänisenniemen alueelta. 1. Geologia ja fysikaalinen maantiede: 1.1. Geologinen kuvaus. 1.2. Geomorfologia ja jääkauden luomat kerrostumat, 1.3. Alueen hydrologinen luonnehdinta, 1.4. Maaperä, 1.5. Palaeomaantiede, 1.6. Suojelualueet ja ehdotetut suojelualueet; 2. Maisemat ja ekosysteemit: 2.1. Äänisenniemen nykyiset maisemat, 2.2. Maisemien rakenne, 2.3. Metsäpeitteisten alueiden rakenne ja metsiköt. 2.3. Metsien rakenne, 2.5. Suot, 2.6. Niityt; 3. Flora and fauna: 3.1. Putkilokasvit, 3.2. Sammalet, 3.3. Jäkälät ja jäkälänkaltaiset sienet, 3.4. Uhanalaiset ja indikaattorijäkälät, 3.5. Käävät, 3.7. Hyönteisfauna, 3.7. Paikat Äänisenniemellä, joissa tehtiin lajihavaintoja. Asiasanat geologia, muinaismaantiede, metsät, suot, niityt, putkilokasvit, sammalet, jäkälät, käävät, hyönteiset, luonnon monimuotoisuus, Äänisenniemi, Kizhin saaristo, Ääninen, Karjalan tasavalta Rahoittaja/ toimeksiantaja Pohjoismainen ministerineuvosto, Suomen, Norjan ja Ruotsin ympäristö- ja ulkoasiainministeriöt ISBN 978-952-11-4404-2 (pbk.) ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 (pain.) ISSN 1796-1726 (verkkoj.) Sivuja 360 Kieli Englanti Luottamuksellisuus julkinen Hinta Julkaisun jakelu Suomen ympäristökeskus (SYKE), neuvonta PL 140, 00251, Helsinki Sähköposti: neuvonta.syke@ymparisto.i Julkaisun kustantaja Suomen ympäristökeskus (SYKE), syke.i PL 140, 00251, Helsinki Puh. 0295 251 000 Painopaikka ja -aika Juvenes Print, 2015 Reports of the Finnish Environment Institute 40 | 2014 359 P R E SE N TATI ONSBLAD Utgivare Finlands miljöcentral Författare Tapio Lindholm, Jevgeni Jakovlev och Alexei Kravchenko (eds.) Publikationens titel Biogeography, landscapes, ecosystems and species of Zaonezhye Peninsula, in Lake Onega, Russian Karelia (Biogeograi, landskapen, ekosystem och arter av Zaonezhye halvön, i Onega Sjön, ryska Karelen) Publikationsserie och nummer Finlands miljöcentrals rapporter 40/2014 Datum mars 2015 Publikationens tema Publikationens delar/ andra publikationer inom samma projekt Publikationen inns på internet: www.syke.i/publikationer | helda.helsinki.i/syke | www.bpan.i Sammandrag Zaonezhie halvön, på ryska och i inska Äänisenniemi, ligger i Karelska republiken, på den östra delen av Fennoscandia skölden. Halvön omfattar den mellersta delen av den norra Onega kusten, och de närbelägna öarna. Zaonezhie är ett unikt naturområde med nästan alla typer av Kvartära tidens jordarter och jordformer som har formats i nordvästra Ryssland. Tack vare berggrundets höga halt av kalksten och andra alkalina bergarter är jorden i trakten särskild bördig. Till följd av det är naturet i området ovanligt rikt med en stor mångfald av lora av sällsynta växtarter och lavar och fauna. På Zaonezhie områden inns så artrika skogar, men också mycket myrar och dessutom rikmyrar. Närheten till Onega sjön, dess djup och klar vatten, den näst största sjön i Europa, har en gynnsam effekt på lokala klimatet. Tack vare den bördiga jorden och relativt milda klimatet har området en lång jordbrukshistoria. Många forna åkrar är nuförtiden naturnära ängar. Zaonezhie är ett särskilds mångfaldigt område tack för dess areal och belägenhet. I denna publikation inns de första detaljerade listor över arter av kärlväxter, mossor, lavar, svampar och insekter över hela territoriet i Zaonezhie halvön, Kizhi skärgård och andra närliggande öar. Inventeringen omfattar de största bevarandevärda områden av södra och sydöstra halvön, där det rekommenderas att grunda sex nya naturskyddsområden. Boken beskriver naturen på Zaonezhie halvön i följande avsnitt: 1. Geologi och geograi: 1.1.Geologisk beskrivning, 1.2. Geomorfologi och kvartära sediment, 1,3.Vattensystem, 1.4. Jordmån, 1.5. Paleogeograi, 1,6. Beintliga och planerade skyddsområden; 2. Landskap, ekosystem och biogeograi: 2.1. Moderna landskap, 2.2. Landskapets struktur, 2.3. Skogstäcke, 2.4. Skogarnas stånd struktur, 2,5. Myrar, 2,6. Ängar; 3. Flora och fauna 3.1. Kärlväxter, 3.2. Mossor, 3.3 Lavar och lavartade svampar 3.4. Sällsynta och sårbar lav arter, 3.5. Tickor och 3.6. Insekt fauna. och 3.7. Index för geograiska namn och ortnamn som nämnts i förteckningen över olika typer av förekomster av lora och fauna. Nyckelord geologi, paleogeograi, landskapen, skogar, myrar, ängar, kärlväxter, mossor, lavar, tickor, insekter, naturens mångfald, Naturskydd, Zaoneshie halvön, Kizhi skärgård, Onega sjön, Republiken Karelia Finansiär/ uppdragsgivare Nordiska ministerrådet, miljö- och utrikesministerierna i Finland, Norge och Sverige, Directorate of regional protected areas of the Republic of Karelia ISBN 978-952-11-4404-2 (pbk.) ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 (print) ISSN 1796-1726 (online) Sidantal 360 Språk engelska Offentlighet Offentlig Pris (inneh. moms 8 %) Beställningar/ distribution Finlands miljöcentral (SYKE), PB 140, 00251 Helsingfors, Epost: neuvonta.syke@ymparisto.i Förläggare Finlands miljöcentral (SYKE), PB 140, 00251 Helsingfors Tel. 0295 251 000 Tryckeri/tryckningsort -år Juvenes Print, 2015 360 Reports of the Finnish Environment Institute 40 | 2014 The BPAN project promotes and supports the establishment of a representative network of protected areas in the Barents Region. Protected area networks are an important tool for biodiversity conservation as well as climate change adaptation and mitigation. A representative network of protected areas safeguards biodiversity, supports natural ecosystems and maintains ecosystem services. The BPAN project started in 2011 as an initiative of the nature protection subgroup of the BEAC Working Group on Environment. The project has been implemented by nature conservation authorities, scientiic institutes and nature conservation NGOs in Finland, Sweden, Norway and Northwest Russia. Within the project, ive regional pilot projects have been implemented in high conservation value areas of Northwest Russia. All of these areas are under threat from human activities. In Karelia, the pilot project has been implemented on Zaonezhye Peninsula. Zaonezhye Peninsula has a distinctive and diverse natural heritage, which has been recognised for a long time. Although its unique habitats are included in regional nature conservation plans, documentation necessary for the establishment of a protected area has been lacking. At the same time high conservation value forests have been under threat from logging. This publication gives an overview of Zaonezhye Peninsula. It discusses geology, hydrology and landscapes. It also describes present-day species of vascular plants, bryophytes, lichens, wood-growing fungi and insects on the Zaonezhye Peninsula and its adjacent islands, as well as earlier records from the peninsula since the end of the 19th century. We hope that the information on these pages will promote the protection of hundreds of red-listed species and valuable habitats in the Zaonezhye area. ISBN 978-952-11-4404-2 (pbk.) ISBN 978-952-11-4405-9 (PDF) ISSN 1796-1718 (print) ISSN 1796-1726 (online)