Biodiversity and conservation of mire ecosystems in 泥炭地管理国際会議 : 熱帯および冷温帯泥炭地管理の在り方とその未来像人と自然の調和とその持続性. Instructions for use

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Title Biodiversity and conservation of mire ecosystems in Author(s)Fujita, H.; Kobayashi, H.; Lee, A.; Niimi, E. 泥炭地管理国際会議 : 熱帯および冷温帯泥炭地管理の在り方とその未来像人と自然の調和とその持続性 (International Workshop on Peatland Management: Futu CitationPeatlands : Harmonious and Sustainable Relationship 会議室. 札幌市. Issue Date 2013-10-10 Doc URL http://hdl.handle.net/2115/53553 Type conference presentation File Information No.3_H.Fujita.pdf Instructions for use Hokkaido University Collection of Scholarly and Aca

International Workshop on Peatland Management Hokkaido Univ. Sustainability Weeks 2013 (Oct. 10) Biodiversity of wetland ecosystem Biodiversity and conservation of mire ecosystems in Hokkaido, Japan Cardamine pratensis Iris ensata var. spontanea Bean goose オオヒシクイ Anser fabalis middendorffii Yellow-breasted bunting シマアオジ Emberiza aureola ornata H. Fujita 1, H. Kobayashi 1, A. Lee 2 and E. Niimi 2 1 Botanic Garden FSC, Hokkaido University 2 Graduate School of Agriculture, Hokkaido University Viviparous lizard コモチカナヘビ Zootoca vivipara Japanese crane タンチョウ Grus japonensis Wetland area (km 2 ) Change in wetland area at different regions in Japan increase (change in land use) Increase (water level raising) Increase (water level decline) Increase (newly discovered) decrease (naturally) decrease (development) survival Today s Topics I. Introduction of mires in Hokkaido II. Decline and the present condition of mires in Hokkaido III. Biodiversity and conservation of remaining mire ecosystem in Hokkaido Hokkaido Eastern Japan Western Japan Total after Geospatial information Authority of Japan (GSI) http://www1.gsi.go.jp/geowww/lake/shicchimenseki2.html Ⅰ.. Introduction of mires in Hokkaido Climatic vegetational zones in East Asia, After Hamet-Ahti et al. (1974) Makunbetsu mire Explanetion of symbols: A - arctic HA - hemiarctic NB - northern boreal SB - southern boreal CT - cool temperate WT - warm temperate STR - subtropical TR - tropical 1

Climatic mire zones in Japan After Wolejko and Ito (1986) Explanetion of symbols: 1. mountain mire zone of Hokkaido 2. lowland mire zone of Hokkaido 3. mountain mire and upland bog zone of northern Honshu 4. transitional zone 5. peatless zone of southern Japan Major mires in the upland and lowland :upland mire 400m< :lowland mire 400m> Numanohara mire (Daisetsu mountain) Shizukari mire Fujita, H. (2009) Distribution of the present mires in Hokkaido Fujita, H. et. al (1997) Lowland (alluvial plain, river side) Typical mires in Hokkaido Kushiro Sarobetsu Sarobetsu Asajino Shizukari Utasai Upland (mountainous region ) Typical mires in Hokkaido Ⅱ.. Decline and the present condition of mires in Hokkaido Daisetsu moutain Numanohara Hiragadake-nanpou Daisetu Kumoigahara Ukishima Uryunuma Kushiro mire (Yasuhara Riverside) Sarobetsu mire 2

Change of mire area in Hokkaido Sarobetsu mire N Peatlands Current existing wetlands Ishhikari mire Complex 200,642 ha 59,881 ha Survival percentage 29.8 % 0 50 100 150 200 km Elevation (m) 0-10 10-20 20-40 40-100 100-200 200-300 300-400 400-800 800-2500 Fujita, H. (1997) Distribution of peatlands and current existing wetlands in Hokkaido Change in landuse of Ishikari (Miyaji & Kohyama 1997) 1916 1954 Present condition of Bibai Bog vegetation Invasion of Sasa palmata and Rhus trichocarpa 1968 1987 Wasteland Paddy field Cultivated land Forest Urban district Open water 10km Drain ditch between the mire and adjacent cultivated land Sasa palmate dominated area Bibai office of National Agriculture Research Center for Hokkaido Region N B Trench test area B east drain ditch paddy field 19 road 18 A west drain ditch road Scene of 2004 Bibai A 100m Bog vegetaion Hei ight (m) 17 16 15 14 13 600 500 400 300 200 100 0 Distance (m) cultivated land dressed soil and topsoil high-moot peat transitional-moor peat low-moor peat clayey peat peaty clay clay ground water level After Kasubuchi et al. 1995 3

Present condition of Shinsinotsu mire Change of the river network around Sarobestu mire Original river network (before1920s) Present river network 1961 April Reduction of Sarobestu mire Change of the mire area 1947 1975 1999 After Hokkaido Regional Development Bureau (1972) 泥炭地の生態 2010 October 1923 1970 : mire : farmland : open water mire area (ha) Photo by Takashi Inoue 1980 1995 Fujita, H. (1997) Expansion of Sasa growing area in Sarobestu mire Expansion of Sasa growing area in Sarobestu mire 4

Reduction of Penke-pond in Sarobetsu mire Reduction of Penke-pond in Sarobetsu mire area (km 2 ) 1947 1999 Change of the open water area of Penke-pond A dashed line is simulated Panke-pond area in the future. 国土地理院サロベツ地区湖沼湿原調査報告書 (2007) より引用 After Geospatial information Authority of Japan (GSI) (2007) The report of lake and wetland survey of Sarobetsu area, Hokkaido, northern Japan Ⅲ.. Biodiversity and conservation of remaining mire ecosystem Ownership of mires in Hokkaido Fujita et.al (2009) Uplands Federal land Ownership condition Prefectural, town, and municipal land Private land Federal land & Prefectural, town, and municipal land mixed Subtotal Federal land Prefectural, town, and municipal land Private land Lowlands Federall land & Prefectural, town, and municipal land mixed Federall, Prefectural, town, and land & Private land mixed Subtotal Number % in site ha % in area 29 67.4 654.8 70.9 10 23.3 255.2 27.7 3 7.0 13.0 1.4 1 2.3 - - 43 100.00 923.0 100.00 15 14.0 12,802.9 21.7 3 2.8 3,766.1 6.4 45 42.1 42,388.8 71.9 2 1.9 - - 42 39.2 - - 107 100.0 58,957.8 100.0 Total 150 59,880.8 The extent of designated mires protection in Hokkaido. Fujita et. al (2009) Conservation system Number % in site ha % in area National park 20 46.5 635.0 68.8 Quasi-national park 9 20.9 193.2 20.9 Uplands Prefectural national park 2 4.7 4.4 0.5 N=43 Other protected areas 3 7.0 57.9 6.3 No protection 9 20.9 32.5 3.5 Subtotal 43 100.0 923 100.0 National park 6 5.6 18080.7 30.7 Quasi-national park 8 7.5 2406.9 4.1 Lowlands Prefectural national park 26 24.3 7899.0 13.4 N=107 Other protected areas 25 23.4 2231.5 3.8 No protection 42 39.3 28339.7 48.1 Subtotal 107 100.0 58957.8 100.0 Total 150 59880.8 Database for wetland biodiversity analysis Literature used for the database Flora Vegetation No. of literature 91 139 Used for this analysis 57 104 The number of vascular plant species in the database No. of vascular plant 1,442 No. of Red data plant 173 No. of Invasive plant 151 83 151 mires in Hokkaido 5

Example of the analysis using the database No. of Vascular plant No. of Red list plant No. of Invasive plant Based upon Japanese Red list (Ministry of Environment, Japan 2010) Identify priority wetlands for conservation Based upon Hokkaido blue list (Hokkaido, Japan 2012) Blue list = invasive alian speacies list Scenario-1 Scenario-2 Scenario-3 Scenario-5 : Priority wetland for conservation Before Buffer zone between mire and grassland Old drain The water level in the farmland decreased after the construction of the new farm drain. groundwater table 25 m Buffer zone After setting up the buffer zone balancing pool (old darin) 湿原 old ditch filled by peat Buffer zone New drain Buffer zone Before 25m Buffer zone between mire and grassland. (after Wakkanai Development and Construction Department) After Buffer zone is flooded due to the over floowing of the old drain. Conclusion In Hokkaido, more than 70 % of mire area has been lost during the past 100 years. It is urgent for human society to protect and restore the remaining mires. The mires in the rural area and the urban area have serious problems due to drainage, land subsididence, mire vegetation change etc. For further progress; Accumulation of scientific knowledge and commitment of researches, Long term monitoring project, Organization of new method to evaluate biodiversity 6