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既存のイベント型植樹林における目標植生の再設定と目標への誘導過程に関する事例的研究

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ㄽᩥ 

ORIGINAL ARTICLE

 

᪤Ꮡࡢ࢖࣋ࣥࢺᆺ᳜ᶞᯘ࡟࠾ࡅࡿ┠ᶆ᳜⏕ࡢ෌タᐃ࡜┠ᶆ࡬ࡢ

ㄏᑟ㐣⛬࡟㛵ࡍࡿ஦౛ⓗ◊✲



ᮏ㒊 ᫍ

*1)

࣭᪥⨨ెஅ

2)

1㸧 㫽ྲྀ኱Ꮫ኱Ꮫ㝔ᣢ⥆ᛶ♫఍๰⏕⛉Ꮫ◊✲⛉ Grad. Sch. of Sustainability Science, Tottori Univ.

2㸧 㫽ྲྀ኱Ꮫ㎰Ꮫ㒊 Fac.of Agri. , Tottori Univ.

᦬せ㸸ᕷẸཧຍ➼࡟ࡼࡿ᳜ᶞ࢖࣋ࣥࢺ࡟ࡣ㸪᫂☜࡞┠ᶆ᳜⏕ࡀᐃࡵࡽࢀࡎ࡟㸪₍↛࡜᳃࡙ࡃࡾࢆ┠ⓗ࡜ࡋࡓࡶࡢࡀከ࠸ࠋࡑࡢࡼ࠺࡞᳜ ᶞᯘ࡛ࡣ㸪┠ᶆࢆ᫂☜࡟෌タᐃࡋ㸪ࡑࡇ࡬ᑟࡃᚲせࡀ࠶ࡿࠋᮏ◊✲࡛ࡣ㸪㫽ྲྀ┴ෆࡢ᳜ᶞ࢖࣋ࣥࢺࡀ⾜ࢃࢀࡓᕤሙࡢ஦౛ᆅ࡟࠾࠸࡚㸪 (1)┠ᶆ᳜⏕ࢆ෌タᐃࡍࡿ᪉ἲ࡜㸪(2)ࡑࡇ࡬ㄏᑟࡍࡿ㐣⛬ࢆ㸪᳨ウࡋࡓࠋ᳜ᶞᯘ࡜ࡑࡢ㏆㞄ࡢ⮬↛ᯘཬࡧ஧ḟᯘࡢ✀⤌ᡂ࡜ᵓ㐀ࢆẚ㍑ ࡋࡓࠋࡑࡢ⤖ᯝ㸪஦౛ᆅ࡛ࡣ㸪࣑ࢬ࣓ࡸ࣑ࢬࢼࣛࡀΰ⏕ࡍࡿࣈࢼᯘࡀ┠ᶆ᳜⏕࡜ࡋ࡚෌タᐃࡉࢀࡓࠋࡲࡓ㸪ࡑࢀ࡟⮳ࡿ㐨➽࡜ࡋ࡚㸪ࣈ ࢼᯘ࡜ࡑࡢ㏵୰┦࡛࠶ࡿࢥࢼࣛᯘࡢ୰㛫ⓗ࡞✀⤌ᡂࡢᶞᯘࢆ⤒⏤ࡍࡿࡢࡀ㐺ษ࡛࠶ࡿ࡜ุᐃࡉࢀࡓࠋ ࣮࣮࢟࣡ࢻ㸸࢖࣋ࣥࢺᆺ᳜ᶞᯘ㸪┠ᶆ᳜⏕㸪෌タᐃ㸪ㄏᑟ㸪✀⤌ᡂ㸪ᵓ㐀

MOTOBE, Akari and HIOKI, Yoshiyuki: A case study on goal re-setting and forestation approach for a tree planting event Abstract: Many tree-planting events aim to create forests without a certain vegetation type as a target. For such planted “forest”, re-setting a clear target and finding an appropriate approach to reach that target is required. In this case study, we discuss an approach to re-set the target vegetation type at a factory’s tree-planting event area, in Tottori prefecture, Japan. The species composition and structure of surrounding climax and secondary forest were compared to those of the planted “forest”. Consequently, the Fagus crenata forest mixed with Betura grossa and Quercus crispula was identified as the long-term goal for the planting site. Additionally, tracing species composition between the climax and secondary forest was considered as an appropriate approach with which to set this goal.

Key words: forest planted by planting event, target vegetation, re-setting, approach, species composition, structure 1. ࡣࡌࡵ࡟ ㏆ᖺ㸪᳃࡙ࡃࡾࢆ┠ⓗ࡟ྛᆅ㸪ྛศ㔝࡛᳜ᶞάືࡀάⓎ࡟ ⾜ࢃࢀࡿࡼ࠺࡟࡞ࡗ࡚࠸ࡿ12)ࠋ୰࡛ࡶ㸪⮬↛࡟㏆࠸ᶞᯘࡢ෌ ⏕ࢆ┠ⓗ࡜ࡋࡓ㸪ᕷẸཧຍᆺࡢ᳜ᶞ࢖࣋ࣥࢺࡣ㸪ཧຍ⪅ࡢ⎔ ቃព㆑ࡢྥୖࡀぢ㎸ࡲࢀ㸪CSR άືࡢ୍⎔࡜ࡋ࡚ྲྀࡾධࢀ࡚ ࠸ࡿ௻ᴗࡶከ࠸ࠋ ᳜ᶞ࢖࣋ࣥࢺ࡟ࡼࡿ᳃࡙ࡃࡾࢆᡂຌࡉࡏࡿࡓࡵ࡟ࡣ㸪ࡲࡎ㸪 ┠ᶆ࡜ࡑࡇ࡟ㄏᑟࡍࡿ㐣⛬ࢆ᫂☜࠿ࡘヲ⣽࡟タᐃࡍࡿᚲせࡀ ࠶ࡿࠋࡲࡓ㸪⟶⌮ẁ㝵࡛ࡣ㸪ࣔࢽࢱࣜࣥࢢࢆ⾜࠸㸪ࡑࢀ࡟ᇶ ࡙࠸࡚᳜⏕⟶⌮᪉ἲࡢᨵၿࢆ⾜࠺ࡇ࡜ࡀᮃࡲࡋ࠸ࠋ᳜ᶞ࢖࣋ ࣥࢺ࡟᭱ࡶࡼࡃ⏝࠸ࡽࢀࡿᡭἲ࡜ࡋ࡚㸪ᶓ὾ᅜ❧኱Ꮫࡢᐑ⬥ ᫛ྡ㄃ᩍᤵࡽ࡟ࡼࡿ͆ᐑ⬥᪉ᘧ͇7)ࡸ㸪࢚͆ࢥࣟࢪ࣮⥳໬͇ 12) ࡀ࠶ࡿࡀ㸪ࡇࡢᡭἲ࡟ࡼࡿ᳃࡙ࡃࡾࡢ┠ᶆࡣ₯ᅾ⮬↛᳜⏕࡛ ࠶ࡾ㸪᳜᱂᫬ࡢ≧ែ࠿ࡽ┤᥋┠ᶆ᳜⏕࡬฿㐩ࡍࡿࡇ࡜ࢆ┠ᣦ ࡋ࡚࠸ࡿ㸦௨ୗ㸪ࠕ┤㐩ᆺࠖ㸧ࠋᐩኈᒣ㯄࡟࠾ࡅࡿ͆ࣃࢵࢳ ᳜᱂ἲ͇19)ࡶྠᵝࡢ┠ᶆ࡜ㄏᑟ㐣⛬ࢆࡶࡗࡓᡭἲࡢ୍ࡘ࡛࠶ ࡿࠋ୍᪉࡛㸪͆⏕ែᏛⓗΰ᧛࣭ΰ᳜ἲ͇13)ࡸ͆⮬↛㓄᳜ᢏ⾡ ͇17)࡜࠸࠺ᡭἲࡶᏑᅾࡍࡿࠋࡇࡢᡭἲࡣ㸪᭱⤊ⓗ࡟ࡣᴟ┦ᯘ ࡸ࿘㎶⮬↛᳜⏕ࢆ┠ᣦࡍࡀ㸪ࡲࡎࡣඛ㥑ⓗ࡞᳜⏕ࢆᙧᡂࡋ㸪 ࡑࢀࡀ㑄⛣ࡍࡿࡇ࡜࡛┠ᶆ᳜⏕࡟ㄏᑟࡍࡿࡇ࡜ࢆ┠ᣦࡋ࡚࠸ ࡿ㸦௨ୗ㸪ࠕ㑄⛣ᆺࠖ㸧ࠋࡇࢀࡽࡢ᳜᱂ᡭἲ࡛ࡣ㸪࣐ࢽࣗ࢔ ࣝࡢసᡂ 7,12,13)ࡸ㸪᳜᱂࠿ࡽᩘᖺᚋࡢࣔࢽࢱࣜࣥࢢ࣭ホ౯ 11,14,15,20)ࡀ⾜ࢃࢀ࡚࠸ࡿࠋ  ࡋ࠿ࡋ㸪ୖグࡢࡼ࠺࡞ᡭἲ࡟ᇶ࡙࠿ࡎ㸪᳜᱂ᚋᨺ⨨ࡉࢀ࡚ ࠸ࡿ᳜ᶞ࢖࣋ࣥࢺ࡟ࡼࡿ᳃࡙ࡃࡾࡢ஦౛ࡶᑡ࡞ࡃ࡞࠸ࠋࡇࢀ ࡣ㸪᳜ᶞ࢖࣋ࣥࢺࡑࡢࡶࡢࡀ⮬ᕫ┠ⓗ໬ࡉࢀ㸪┠ᶆ᳜⏕ࡸ᳜ ⏕ィ⏬ࡀ᫂☜࡛࡞࠸ࡲࡲ᳜࠼ࡽࢀࡓࡓࡵࡔ࡜᥎ᐹࡉࢀࡿࠋ ࡑࡇ࡛ᮏ◊✲࡛ࡣ㸪㐣ཤ 10 ᖺ㛫࡟ࢃࡓࡗ࡚᳜ᶞ࢖࣋ࣥࢺ ࡀ⾜ࢃࢀࡓ㫽ྲྀ┴ࡢ᳜ᶞᯘ࡟࠾࠸࡚㸪┠ᶆ᳜⏕ࢆ᫂☜࡟෌タ ᐃࡍࡿ᪉ἲ࡜㸪タᐃࡋࡓ┠ᶆ࡟᳜ᶞᯘࢆㄏᑟࡍࡿ㐣⛬࡟ࡘ࠸ ࡚஦౛ⓗ࡟᳨ウࡋࡓࠋ ᮏ஦౛࡛⾜ࢃࢀࡓ᳜ᶞ࢖࣋ࣥࢺࡢᙜึࡢ┠ᶆ᳜⏕ࡣ㸪Ẽೃ ⓗᴟ┦࡛࠶ࡿࣈࢼᯘ࡛࠶ࡗࡓࠋࡋ࠿ࡋ㸪᳜᱂ᙜ᫬ࡣヲ⣽࡞᳨ ウࡀ⾜ࢃࢀ࡚࠾ࡽࡎ㸪᳜᱂ᶞ✀ࡀࣈࢼᯘࡢ✀⤌ᡂࢆ㐺ษ࡟཯ ᫎࡋࡓࡶࡢ࡟࡞ࡗ࡚࠸ࡿ࠿࡝࠺࠿ࡣ୙࡛᫂࠶ࡗࡓࠋࡑࡇ࡛㸪 ᩥ⊩ㄪᰝࡸ࿘㎶ᶞᯘࡢㄪᰝࢆᐇ᪋ࡋ㸪ᐇ⌧ࡍ࡭ࡁࣈࢼᯘࡢ✀ ⤌ᡂࡸ᳜ᶞᯘ࡜ࡢ✀⤌ᡂࡢ┦㐪ࢆ᫂ࡽ࠿࡟ࡍࡿ࡜ඹ࡟㸪ࡇࡢ

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ᅗ-1 ஦౛ᑐ㇟ᆅࡢ఩⨨ᅗ Fig. 1 Location of the study site

⾲-1 ᳜᱂ᶞ✀୍ぴ㸦2008㹼2017 ᖺ࡛᳜᱂ࡋࡓⱑᮌࡢ⣼ィ㸧 Table 1 Cumulative number of planted species

ࡼ࠺࡞┦㐪ࢆゎᾘࡍࡿࡓࡵࡢ᪉ἲ࡟ࡘ࠸᳨࡚ウࡋࡓࠋ 2. ㄪᰝᆅཬࡧ᪉ἲ 2.1 ஦౛ᑐ㇟ᆅ ஦౛ᑐ㇟ᆅࡣ㸪㫽ྲྀ┴᪥㔝㒆Ụᗓ⏫࡟఩⨨ࡍࡿ㸪ࢧࣥࢺࣜ ࣮ኳ↛Ỉዟ኱ᒣࣈࢼࡢ᳃ᕤሙࡢᩜᆅෆࡢ᳜ᶞ࢖࣋ࣥࢺ⏝ᆅ࡛ ࠶ࡿ㸦௨ୗࠊ᳜ᶞᯘ㸧㸦ᅗ-1㸧ࠋ໭⦋ 35 ᗘ 19 ศ㸪ᮾ⤒ 133 ᗘ24 ศ㸪ᶆ㧗 700 m㸪ᖺᖹᆒẼ ࡣ 9.6 Υ㸪 㔞ᣦᩘࡣ 74.6 ࡛෭ ᖏ࡟࠶ࡓࡿ㸦ᒸᒣ┴ୖ㛗⏣2004㹼2008 ᖺࡢẼ㇟ᗇ࢔ ࣓ࢲࢫࢹ࣮ࢱ㸪Ẽ ࡣྠࢹ࣮ࢱࢆᶆ㧗⿵ṇ㸧ࠋᖺ㛫ᖹᆒ㝆Ỉ 㔞ࡣ2,429 mm ࡛㸪෤Ꮨ࡟ࡣ 0.7㹼1.8 m ࡢ✚㞷ࡀ࠶ࡿࠋ᳜ᶞ ᯘ࿘㎶ࡣ㸪ᮾഃࡢᮏ㇂ᕝ࡜すഃࡢ⣽㇂ᕝ࡟๐ࡽࢀ࡚࡛ࡁࡓྎ ᆅ≧ᆅᙧ࡛㸪໭ᮾ࠿ࡽ༡す࡟ྥࡅ࡚⦆ࡸ࠿࡟ഴᩳࡋ࡚࠸ࡿࠋ ᅵተࡣ㯮࣎ࢡᅵ࡛࠶ࡾ㸪ᕤሙᘓタ๓ࡣ኱᰿⏿࡜ࡋ࡚฼⏝ࡉࢀ ࡚࠸ࡓࠋ᳜ᶞᯘࡣ1.6 ha ࡛㸪㞼㞛ୣᏛᅬ㸦රᗜ┴ᐆሯᕷ㸧ࡢ ⏕ᚐ࡟ࡼࡗ࡚᳜ᶞࡀ⾜ࢃࢀࡓ⠊ᅖ࡛࠶ࡿࠋ᳜ᶞ࢖࣋ࣥࢺࡣ㸪 ୖグࡢᕤሙࡀ❹ᕤࡋࡓ2008 ᖺ࠿ࡽ 2017 ᖺࡲ࡛㸪ẖᖺ 1 ᅇ ィ10 ᅇ⾜ࢃࢀࡓࠋ᳜᱂㛫㝸ࡣ୕ゅ᱁Ꮚ≧࡟⣙ 1.95 m㸦ᐦᗘ 3,000 ᮏ/ha㸧㸪᳜᱂ᶞ✀ࡣ኱ᒣᆅᇦ࡛᥇ྲྀࡋࡓ✀Ꮚࢆ⏝࠸ࡓ ὀ㸧ᅗෆࡢᩘᏐࡣᑐᛂࡍࡿぢฟࡋ␒ྕࢆ♧ࡍ ᅗ-2 ᮏ◊✲ࡢࣇ࣮ࣟࢳ࣮ࣕࢺ Fig. 2 Flowchart of this study

ᆅᇦᛶ✀ⱑ඲38 ✀㸦⾲-1㸧࡛㸪ࡑࢀࡽࡀྛᖺ࡛ᑡࡋࡎࡘᶞ✀ ᵓᡂࢆኚ࠼࡞ࡀࡽ᳜᱂ࡉࢀࡓࠋ᳜ᶞ࢖࣋ࣥࢺ㛤ጞᙜึࡢ┠ᶆ ࡣ70 ᖺᚋࡢ 2078 ᖺ㡭࡟ࣈࢼᯘࢆ┠ᣦࡍࡇ࡜࡜ࡉࢀ࡚࠸ࡓ ࡀ㸪ࡑࡢලయⓗ࡞✀⤌ᡂࡸᵓ㐀ࡢ┠ᶆࡣタᐃࡉࢀ࡚࠸࡞࠿ࡗ ࡓࠋࡲࡓ㸪᳜᱂ᶞ✀࡟ࡣ㸪ࣈࢼᯘ࡜ࡑࡢ௦ൾ⣔ิୗ࡟࠶ࡿ⩌ ⴠ࡟ᒓࡍࡿᶞ✀ࡀΰᅾࡋ࡚࠸ࡓࠋ 2.2 ㄪᰝ᪉ἲ 2.2.1 ᩥ⊩ㄪᰝ ┠ᶆ࡜ࡋ࡚ࡩࡉࢃࡋ࠸᳜⏕ࢆᢕᥱࡍࡿࡓࡵ㸪ᩥ⊩ㄪᰝࢆ⾜ ࡗࡓࠋᑐ㇟࡜ࡋࡓᩥ⊩ࡣ㸪(1)᪥ᮏ඲ᅜཬࡧ୰ᅜᆅ᪉ࡢ᳜⏕࡟ 㛵ࡍࡿᩥ⊩ 3,5,6,8,9,16) (2)᳜ᶞᯘ࿘㎶࡛ࡢ᪤ ㄪᰝࢹ࣮ࢱ 9,10) ࡜ࡋࡓࠋ(1)ࡼࡾ㸪୍⯡ⓗ࡞᳜⏕ศᕸ࡟ࡘ࠸࡚ᢕᥱࡋ㸪(2)ࡼࡾ㸪 ᳜ᶞᯘ࿘㎶ࡢ᳜⏕ศᕸࡸෆ㒊ᵓ㐀ࢆᢕᥱࡋࡓࠋ 2.2.2 ࿘㎶ᶞᯘ⌧ᆅㄪᰝ ᳜ᶞᯘ࿘㎶ࡢ⮬↛ᯘཪࡣ஧ḟᯘ࡟࠾࠸࡚㸪᳜≀♫఍Ꮫⓗ᳜ ⏕ㄪᰝ1)ࢆ⾜ࡗࡓࠋࡲࡓࡑࢀ࡜࠶ࢃࡏ࡚㸪㧗ᮌ㸦ྛࣉࣟࢵࢺ ࡟࠾࠸࡚㧗ᮌᒙࢆᙧᡂࡍࡿ㸪ࡘࡿᛶ࡛ࡣ࡞࠸ᮌᮏࡍ࡭࡚㸧ࡢ ᮏᩘࢆィ ࡋ㸪ࡑࡢ❧ᮌᐦᗘࢆ⟬ฟࡋࡓࠋㄪᰝࣉࣟࢵࢺࡣ 2009 ᖺ᫬Ⅼ࡛ࡢ኱ᒣ㞃ᒱᅜ❧බᅬዟ኱ᒣᆅ༊ࡢ⌧Ꮡ᳜⏕ᅗ 2)㸪㫽ྲྀ┴ᆅ⌮᝟ሗබ㛤ࢩࢫࢸ࣒࡜ࡗ࡜ࡾWeb ࣐ࢵࣉ18)㸪⌧ ᆅ㋃ᰝ࡟ࡼࡾỴᐃࡋࡓࠋ 2.2.3 ᳜ᶞᯘ⏕ṧᮌㄪᰝ ᳜᱂ᮌࡢ⏕ṧ≧ἣࢆㄪᰝࡋ㸪ᶞ✀ู࡟⏕ṧ⋡ࢆ⟬ฟࡋࡓࠋ ୍⯡࡟㸪᳜ᶞࡋࡓᶞᮌࡣ㸪⮬↛Ὲửཪࡣ㛫ఆ࡟ࡼࡾᚎࠎ࡟ᐦ ᗘࢆୗࡆ㸪⮬↛ᯘ࡜ྠ⛬ᗘࡢ❧ᮌᐦᗘ࡬࡜㏆࡙ࡅ࡚࠸ࡃࡇ࡜ ࡀᮃࡲࡋ࠸ࠋࡑࡇ࡛࿘㎶⮬↛ᯘ࡛ࡢ㧗ᮌࡢ❧ᮌᐦᗘࢆ㸪᳜ᶞ ᯘࡢ┠ᶆ❧ᮌᐦᗘ࡜ࡳ࡞ࡋ㸪ࡑࡢ⤖ᯝ࡜᳜ᶞ࢖࣋ࣥࢺࡢ᳜᱂ ᐦᗘ㸦3,000 ᮏ/ha㸧࠿ࡽ㸪᳜᱂ᐦᗘ࡟ᑐࡍࡿ┠ᶆ㐩ᡂ᫬ࡢ❧ ᮌᐦᗘࡢ๭ྜ㸦%㸧ࢆ⟬ฟࡋ㸪⏕ṧ⋡ࡢホ౯ᇶ‽࡜ࡋࡓࠋྛ ᶞ✀ࡢ⏕ṧ⋡ࡀࡇࡢホ౯ᇶ‽ࢆୗᅇࡗࡓሙྜ㸪┠ᶆ᳜⏕ࢆᙧ ✀ྡ ᮏᩘ ✀ྡ ᮏᩘ

ࣈࢼࠉFagus crenata Blume 619 ࢥࢼࣛࠉQuercus serrata Murray 355 ࣜࣙ࢘ࣈࠉClethra barbinervis Siebold et

Zucc. 345 ࣑ࢬ࢟ࠉCornus controversa Hemsl. ex Prain 141 ࢼࢼ࣐࢝ࢻࠉSorbus commixta Hedl. 136 ࢯࣚࢦࠉIlex pedunculosa Miq. 135 ࣑ࢬࢼࣛࠉQuercus crispula Blume 125 ࢘ࣜࣁࢲ࢚࢝ࢹࠉAcer rufinerve Siebold et 122 ࢖ࢾࢩࢹࠉCarpinus tschonoskii Maxim. 99 ࣐ࣖࢨࢡࣛࠉCerasus jamasakura (Siebold exKoidz.) H.Ohba 89 ࣑ࢬ࣓ࠉBetula grossa Siebold et Zucc. 75 ࢚ࢦࣀ࢟ࠉStyrax japonicus Siebold et Zucc. 70 ࣑࢘࣡ࢬࢨࢡࣛࠉPadus grayana (Maxim.)

C.K.Schneid. 65 ࢥࣁ࢘ࢳ࢚࣡࢝ࢹࠉAcer sieboldianum Miq. 60 ࣐࣑ࣖࣔࢪࠉAcer amoenum Carrière var.

matsumurae (Koidz.) K.Ogata 50 ࣍࢜ࣀ࢟ࠉMagnolia obovata Thunb. 45 ࢡ࣐ࣀ࣑ࢬ࢟ࠉCornus macrophylla Wall 41 ࢘ࣛࢪࣟࣀ࢟ࠉAria japonica Decne 41 ࢔ࢬ࢟ࢼࢩࠉAria alnifolia (Siebold et Zucc.)

Decne. 41 ࢱ࣒ࢩࣂࠉMagnolia salicifolia (Siebld etZucc.) Maxim. 39 ࢔࢜ࢲࣔࠉFraxinus lanuginosa Koidz. f.

serrata (Nakai) Murata 31 ࣐࢜࢜ࣖࢨࢡࣛࠉCerasus sargentii (Rehder)H.Ohba var. sargentii 23 ࢥࣈࢩࠉMagnolia kobus DC. 20 ࢡࣟࣔࢪࠉLindera umbellata Thunb. var.umbellata 20 ࣐ࣖ࣎࢘ࢩࠉCornus kousa Buerger ex

Hance subsp. Kousa 15 ࢝ࢫ࣑ࢨࢡࣛࠉCerasus leveilleana (Koehne)H.Ohba 10 ࢼࢶࣁࢮࠉVaccinium oldhamii Miq. 10 ࢧ࣡ࣇࢱࢠࠉSymplocos sawafutagi Nagam. 10 ࢔࢝ࢩࢹࠉCarpinus laxiflora (Siebold et

Zucc.) Blume 10

࣓࢜࢜࢝ࣀ࢟ࠉViburnum furcatum Blume ex Maxim. 10 ࢔࢜ࣁࢲࠉIlex macropoda Miq. 10 ࣑࣐࣐ࣖ࢞ࢬ࣑ࠉvar. wrightii Viburnum wrightii Miq. 10 ࢱ࢝ࣀࢶ࣓ࠉGamblea innovans (Siebold et

Zucc.) C.B.Shang, Lowry et Frodin 10

࢚ࢰ࢔ࢪࢧ࢖ࠉHydrangea serrata (Thunb.) Ser. var. yesoensis (Koidz.) H.Ohba 10 ࢿࢪ࢟ࠉLyonia ovalifolia (Wall.) Drude var.

elliptica (Siebold et Zucc.) Hand.-Mazz. 10

࢖ࢱ࢚ࣖ࢝ࢹࠉAcer pictum Thunb. subsp. dissectum (Wesm.) H.Ohashi 10 ࢥࢩ࢔ࣈࣛࠉChengiopanax sciadophylloides

(Franch. et Sav.) C.B.Shang et J.Y.Huang 10 ࢺࢳࣀ࢟ࠉAesculs turbinata Blume ᮏᩘ୙᫂ ࣈࢼࡢ᳃ᕤሙ

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ᡂࡍࡿ࡟ࡩࡉࢃࡋࡃ࡞࠸࡜ุ᩿ࡋ㸪⏕ṧ⋡ᡂ⦼୙Ⰻᮌ࡜ࡳ࡞ ࡋࡓࠋ 2.2.4 ᳜ᶞᯘᯘᗋ᳜⏕ㄪᰝ  ᳜ᶞᯘෆ࡟࠾ࡅࡿ᳜᱂ᮌ௨እࡢ᳜≀┦ࢆᢕᥱࡍࡿࡓࡵ㸪ⲡ ᮏ᳜≀ཬࡧᶞ㧗1 m ᮍ‶ࡢᮌᮏ᳜≀㸦᳜᱂ᮌࡣ㝖ࡃ㸧ࢆᑐ㇟ ࡟㸪᳜ᶞᯘෆ110 ࢝ᡤ࡟࠾࠸࡚᳜⏕ㄪᰝ1)ࢆ⾜ࡗࡓࠋㄪᰝࣉ ࣟࢵࢺࡣ᳜⏕㧗࡟ᛂࡌ࡚1 m™1 m ཪࡣ 2 m™2 m ࡜ࡋࡓࠋ 2.3 ┠ᶆタᐃ᪉ἲࡢ᳨ウ ᩥ⊩ㄪᰝ㸪᳜ᶞᯘࡢ᳜⏕㸪᳜᱂ᮌࡢ⏕ṧ⋡㸪࿘㎶ᶞᯘ᳜⏕ ㄪᰝࢆࡶ࡜࡟㸪┠ᶆ᳜⏕ࡢ⩌㞟㸪ୗ఩༢఩㸪✀⤌ᡂࡢ㡰࡛タ ᐃࡋࡓ㸦ᅗ-2㸧ࠋ௒ᅇࡣࡇࡢᡭ㡰ࢆ⏝࠸࡚㸪᳜ᶞᯘࡢ᭱⤊┠ ᶆࢆ㧗ᮌᒙ࣭ள㧗ᮌᒙ࡟ࡘ࠸࡚Ỵᐃࡋࡓࠋపᮌᒙ௨ୗࡢ᳜⏕ ࡣ㸪㧗ᮌ࣭ள㧗ᮌᒙࡼࡾࡶᚤ⣽࡞⎔ቃࡢኚ໬ࢆཷࡅࡸࡍࡃ㸪 ࢥࣥࢺ࣮ࣟࣝࡀᅔ㞴࡛࠶ࡿ࡜ุ᩿ࡋ㸪௒ᅇࡢ┠ᶆタᐃࡢᑐ㇟ ࠿ࡽ㝖እࡋࡓࠋ 2.3.1 ┠ᶆ⩌㞟ࡢタᐃ  ᶞᯘࡢศᕸࡣ㸪ᶞᮌࡢ✀ࡢศᕸࡢࣇࣟࣛⓗせᅉ࡜㸪Ẽೃࡸ ᅵተ࡞࡝ࡢ⎔ቃⓗせᅉ࡟ࡼࡗ࡚つᐃࡉࢀ࡚࠸ࡿ4)ࠋᮏ◊✲࡛ ࡣ㸪ࣇࣟࣛⓗせᅉ㸪⎔ቃⓗせᅉ㸪₯ᅾ⮬↛᳜⏕ࡢ3 ࡘࡢほⅬ ࠿ࡽᩥ⊩3,5,6,8,9,16)ࢆ᳨ウࡋ㸪᳜ᶞᯘ࡟ᡂ❧ࡍ࡭ࡁᴟ┦ࢆ≉ᐃ ࡋ࡚㸪ࡇࡢ᳜ᶞᯘࡢ᭱⤊┠ᶆ࡜ࡋࡓࠋ 2.3.2 ୗ఩༢఩ࡢタᐃ  ୖグ㸪ᩥ⊩9)ࡼࡾྛୗ఩༢఩ࡀᡂ❧ࡍࡿ⎔ቃ᮲௳ࢆ≉ᐃࡋ㸪 ᐑ⬥㸦1983㸧࡟ࡼࡿ㆑ู⾲10)㸦௨ୗ㸪㆑ู⾲㸧ࢆ⏝࠸࡚㸪ㄪ ᰝࡋࡓ࿘㎶ᶞᯘࡢ⩌ⴠࢆྠᐃࡋࡓࠋࡑࢀࡽࢆ㋃ࡲ࠼㸪┠ᶆ࡜ ࡍࡿ⩌㞟ࡢୗ఩༢఩ࢆタᐃࡋࡓࠋ 2.3.3 ✀⤌ᡂࡢタᐃ  ㆑ู⾲࡟グ㍕ࡉࢀ࡚࠸ࡿ✀ࡢ࠺ࡕ㸪(1)᳜ᶞᯘ࡟᳜᱂ࡉࢀࡓ ✀㸪(2)࿘㎶ᶞᯘㄪᰝ࡟ฟ⌧ࡋࡓ✀㸪(3)ᖖᅾᗘࡀϫ௨ୖ㸦60㸣 ௨ୖ㸧ࡢ✀ࢆ㡰࡟ᢳฟࡋ㸪ࡉࡽ࡟᳜ᶞᯘ࡟࠾࠸࡚ᡂ⦼୙Ⰻ࡜ ุ᩿ࡉࢀࡓᶞ✀ࢆ㝖࠸ࡓࡶࡢࢆ┠ᶆ᳜⏕ࡢᵓᡂ✀࡜ࡋࡓࠋ┠ ᶆ᳜⏕࡟࠾ࡅࡿྛ✀ࡢฟ⌧㝵ᒙࡣ㸪࿘㎶ᶞᯘ࡟ฟ⌧ࡋࡓ✀࡟ ࡘ࠸࡚ࡣࡑࡇ࡛ࡢฟ⌧㝵ᒙ㸪ࡑࢀ௨እࡢ✀࡟ࡘ࠸࡚ࡣ㆑ู⾲ ࡛ࡢฟ⌧㝵ᒙ࡜ࡋࡓࠋ  ඃ༨ᗘࢆ♧ࡍᣦᶆ࡜ࡋ࡚Braun-Blanquet㸦1964㸧1)ࡢඃ༨ ᗘ㝵⣭ࢆ⏝࠸ࡓࠋྍ⬟࡞㝈ࡾ᳜ᶞᯘࡢ᮲௳࡟ྜࢃࡏࡿࡓࡵ㸪 ࿘㎶ᶞᯘ࡟ฟ⌧ࡋࡓ✀࡟ࡘ࠸࡚ࡣࡑࡢ⿕ᗘ㸪ฟ⌧ࡋ࡞࠿ࡗࡓ ✀࡟ࡘ࠸࡚ࡣ㆑ู⾲࡛ࡢඃ༨ᗘ㝵⣭ࢆ⿕ᗘⓒศ⋡ 1)࡟┤ࡋࡓ ሙྜࡢ୰ኸ್ࢆඃ༨ᗘ࡜ࡋ࡚タᐃࡋࡓࠋ 2.4 ┠ᶆ᳜⏕࡬⮳ࡿ㐣⛬ࡢ᳨ウ ᳜᱂ᶞ✀ࡢጇᙜᛶࡸ᳜᱂ᚋࡢ⏕ṧ⋡࡟ࡼࡗ࡚ࡣ㸪┤᥋㸪᭱ ⤊┠ᶆࡢ᳜⏕ࢆᙧᡂࡍࡿࡼࡾࡶ㸪୍ᗘ᭱⤊┠ᶆࡢ㑄⛣ึ࣭୰ ᮇẁ㝵࡟࠶ࡓࡿ᳜⏕ࢆᙧᡂࡋ㸪ࡑࡇ࠿ࡽඛࢆ⮬↛ࡢ㑄⛣࡟ጤ ࡡࡿࡇ࡜ࡢ᪉ࡀྜ⌮ⓗ࡛࠶ࡿྍ⬟ᛶࡶ⪃࠼ࡽࢀࡿࠋ௒ᅇࡣ㸪 2.3 ࡛タᐃࡋࡓ┠ᶆ᳜⏕࡬⮳ࡿ㐣⛬࡜ࡋ࡚㸪࢚͆ࢥࣟࢪ࣮⥳໬ ͇14)➼ࡢࡼ࠺࡞ࠕ┤㐩ᆺࠖ࡜㸪͆⏕ែᏛⓗΰ᧛࣭ΰ᳜ἲ͇15) ➼ࡢࡼ࠺࡞ࠕ㑄⛣ᆺࠖࡢ࡝ࡕࡽࡢ㐣⛬ࢆ᥇ᢥࡍࡿ࡭ࡁ࠿᳨ウ ࡋࡓࠋ 2.4.1 ୰㛫┠ᶆࡢタᐃ ࠕ┤㐩ᆺࠖࢆ᥇ᢥࡋࡓሙྜ㸪ㄏᑟࡍ࡭ࡁ᳜⏕ࡣ2.3 ࡛タᐃ ࡋࡓ᭱⤊┠ᶆ࡛࠶ࡿࡢ࡟ᑐࡋ㸪ࠕ㑄⛣ᆺࠖࢆ㑅ᢥࡋࡓሙྜ࡟ ㄏᑟࡍ࡭ࡁ᳜⏕ࢆ୰㛫┠ᶆ࡜ࡋ㸪2.3 ࡜ྠᵝࡢᡭἲࢆ⏝࠸࡚ タᐃࡋࡓࠋ 2.4.2 㐺ษ࡞㐣⛬ࡢỴᐃ ┠ᶆࡢ✀⤌ᡂ࡬㏆࡙ࡅࡿࡓࡵ࡟ࡣ㸪┠ᶆᵓᡂ✀ࢆ⿵᳜ࡍࡿ ࡜ྠ᫬࡟㸪ࡑࢀ௨እࡢ✀ࢆ㝖ఆࡍࡿ㸦ᶞ✀㌿᥮㸧ᚲせࡀ࠶ࡿࠋ ୖグ2 ࡘࡢ㐣⛬࡟ࡘ࠸࡚㸪⌧ᅾࡢ᳜ᶞᯘࡢ✀⤌ᡂ࡜┠ᶆ᳜⏕ ࡢ㧗ᮌᒙࡢ✀⤌ᡂࢆẚ㍑ࡋ㸪࡝ࡕࡽࡀྜ⌮ⓗ࠿᳨ウࡋࡓࠋࡑ ࡢࡓࡵ࡟ࠊ௨ୗࡢࡼ࠺࡟ᶞ✀㌿᥮ᚲせᮌࡢ๭ྜࢆ⟬ฟࡋࡓࠋ ࡲࡎ㸪2018 ᖺ᫬Ⅼ࡛ࡢ᳜ᶞᯘࡢ඲᳜᱂ᮌᮏᩘ࡟ᑐࡍࡿྛᶞ ✀ࡢᮏᩘ๭ྜ㸦%㸧㸦ᶞ✀ูᮏᩘ๭ྜ㸦%㸧㸧࡜┠ᶆ᳜⏕ࡢ㧗 ᮌᒙᵓᡂ✀ࡢᶞ✀ูᮏᩘ๭ྜ㸦%㸧࡜ࡢᕪࢆྛࠎ⟬ฟࡋࡓࠋ ṇ್ࡣ⿵᳜๭ྜࠊ㈇್ࡣ㝖ఆ๭ྜࢆ♧ࡋࠊ㝖ఆࡋࡓ⟠ᡤ࡟⿵ ᳜ࡍࡿࡓࡵࠊṇ㈇ࡢྜィࡣ 0㸦ࢮࣟ㸧࡜࡞ࡿࠋࡑࡇ࡛ࠊṇ್ ࡢྜィࢆᶞ✀㌿᥮ᚲせᮌࡢ๭ྜ㸦%㸧࡜ࡋࡓࠋࡇࡇ࡛㸪┠ᶆ ᳜⏕ࡢ㧗ᮌᒙᵓᡂ✀ࡢᶞ✀ูᮏᩘ๭ྜ㸦%㸧ࡣ㸪ᶞ✀ࡈ࡜࡟ タᐃࡋࡓඃ༨ᗘ㝵⣭1)ࢆᖹᆒ⿕ᗘⓒศ⋡1)ࡢ୰ኸ್࡟ኚ᥮ࡋ㸪 㧗ᮌᒙࡢ᳜⿕⋡࡟ᑐࡍࡿྛᶞ✀ࡢ⿕ᗘࢆ⟬ฟࡋࡓࡶࡢ࡛࠶ ࡿࠋ 3. ⤖ᯝཬࡧ⪃ᐹ 3.1 ┠ᶆࡢ෌タᐃ 3.1.1 ⩌㞟 ᐑ⬥㸦1983㸧9)࡟ࡼࡿ࡜㸪୰ᅜᆅ᪉ࡢᒣ㝜ഃ࡛ࡣ㸪ࣖࣈࢶ ࣂ࢟ࢡࣛࢫ㸦Camellietea japonicae Miyawaki et Ohba 1963㸧࡜ࣈࢼࢡࣛࢫ㸦Fagetea crenatae Miyawaki, Ohba et Murase 1964㸧ࡢቃ⏺ࡀ㸪ᾏᢤ 300㹼400m ࡟࠶ࡿࠋࡲ ࡓ㸪๓ᕝ㸦1949㸧6)㸪Ἑ㔝㸦1977㸧7)ࡢ᳜≀༊⣔࡟ࡼࡿ࡜㸪 ᳜ᶞᯘࡣ᪥ᮏᾏᆅ༊࡟༊ศࡉࢀࡿࠋ୰ᅜᆅ᪉ࡢࣈࢼࢡࣛࢫᇦ ࡢ᳜⏕ࡣ᳜≀♫఍Ꮫⓗ࡞⩌ⴠయ⣔࡟࠾࠸࡚㸪᪥ᮏᾏᆅ༊࡟ᑐ ᛂࡋࡓࢳࢩ࣐ࢨࢧ㸫ࣈࢼ⩌ᅋ㸦Saso kurilensis-Fagion

crenatae Miyawaki, Ohba et Murase 1964㸧࡟ྵࡲࢀࡿ

9)ࠋࡇࢀࡲ࡛㸪ྠ⩌ᅋࡢୗ఩༢఩ࡣᵝࠎ࡟␗࡞ࡿ⩌㞟ࡀ᳨ウ ࡉࢀ࡚ࡁࡓ3,9,16)ࡀ㸪࠸ࡎࢀ࡟࠾࠸࡚ࡶ㸪᳜ᶞᯘ࿘㎶ࡣࢡࣟ ࣔࢪ㸫ࣈࢼ⩌㞟ࡢศᕸᇦ࡟ྜ⮴ࡋࡓࠋࡲࡓ㸪ᐑ⬥㸦1990㸧8) ࡟ࡼࡿ࡜㸪ࡇࡢ⩌㞟ࡣ 㔞ᣦᩘ85㹼45 ࡢከ㞷ᆅᇦ࡛㸪ᮾ᪥ ᮏ࡛ࡣᾏᢤ500m ௨㧗࡛Ⓨ㐩ࡍࡿࠋᐑ⬥㸦1983㸧9)࡟ࡼࡿ₯ ᅾ⮬↛᳜⏕࡟࠾࠸࡚㸪୰ᅜᆅ᪉ࡢ୺せ࡞₯ᅾ⮬↛᳜⏕ࡣࢡࣟ ࣔࢪ㸫ࣈࢼ⩌㞟㸦Linderoumbellatae-Fagetum crenatae ⾲-2 ⮬↛ᯘ࡛ࡢㄪᰝ⤖ᯝ

Table 2 Survey results from natural forests

ᾏᢤ 㠃✚ 㧗ᮌᒙ ┠ᶆ ⏕ṧ⋡ 㸦m㸧 㸦m2 ❧ᮌᮏᩘ ❧ᮌᐦᗘ㸦/ha㸧 ホ౯ᇶ㡰㸦%㸧 (1) 918 20×20 18 (2) 914 26.6×15 9 (3) 958 20×20 24 (4) 986 20×20 17 245 14.2

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⾲-3 ᭱⤊┠ᶆ࡜୰㛫┠ᶆࡢタᐃ࡟⏝࠸ࡓྛㄪᰝ⤖ᯝ࡜┠ᶆ᳜⏕ࡢ✀⤌ᡂ

Table 3 Results of each survey used for to set targets and species composition of target vegetation

ὀ1㸧ྛள⩌㞟ཬࡧኚ⩌㞟ࡢቃ⏺ࡣ◚⥺࡛♧ࡋ㸪⩌ⴠྡ࡟⏝࠸ࡽࢀ࡚࠸ࡿ✀ࡢ࿴ྡ࡟ͤࢆグࡋࡓࠋ⏕ṧ⋡ᡂ⦼୙Ⰻᶞ✀㸦⏕ṧ⋡ 14.2%㸦⾲-2㸧ᮍ‶㸧࡟ࡣ⏕ṧ⋡࡟ୗ⥺ࢆグࡋࡓࠋ ὀ2㸧B1㸸㧗ᮌᒙ㸪B2㸸ள㧗ᮌᒙ㸪S-K㸸పᮌᒙ㹼ⲡᮏᒙϩ ὀ3㸧ࢡࣟࣔࢪ㸫ࣈࢼ⩌㞟㸦࢜࢜࢖࣑࣡࢝࢞ள⩌㞟㸸ࢳࣗ࢘ࢦࢡࢨࢧኚ⩌㞟㸪ࢳࢩ࣐ࢨࢧኚ⩌㞟㸪ࢳ࣐࢟ࢨࢧኚ⩌㞟㸭඾ᆺள⩌㞟㸸ࢳࣗ࢘ࢦࢡࢨࢧኚ⩌㞟㸪ࢳࢩ࣐ࢨࢧኚ⩌㞟㸪ࢳ࣐࢟ࢨࢧኚ ⩌㞟㸭࣐ࣝࣂࣇࣘ࢖ࢳࢦள⩌㞟㸸ࢳࢩ࣐ࢨࢧኚ⩌㞟㸪ࢳ࣐࢟ࢨࢧኚ⩌㞟㸪࢚ࣥࣞ࢖ࢯ࢘ኚ⩌㞟) ࢡࣜ㸫࣑ࢬࢼࣛ⩌㞟㸦ࢥࣂࣀ࣐࢞ࢬ࣑ள⩌㞟㸸࢖ࢾࣈࢼኚ⩌㞟㸪ࢩࣟࣔࢪኚ⩌㞟㸪ࢳ࣐࢟ࢨࢧኚ⩌㞟㸪ࢳࢩ࣐ࢨࢧኚ⩌㞟㸪ࢳࣗ࢘ࢦࢡࢨࢧኚ⩌㞟㸪ࢡ࣐࢖ࢨࢧኚ⩌㞟㸭࣑࣐ࣖ࢖࣎ࢱ ள⩌㞟㸸඾ᆺኚ⩌㞟㸪ࢦ࣐࢟ኚ⩌㞟㸧 ὀ4㸧ࢡࣛࢫࡢᶆᚩ✀࣭㝶క✀࡟ࡘ࠸࡚㸪ྛ┠ᶆ⩌㞟ࡢᶆᚩᕢ࣭༊ศ✀࡟ྵࡲࢀࡿ✀ࡣ┬␎ࡋࡓࠋ (Sasaki 1964) Sasaki 1970㸧࡜ࢳࣕ࣎࢞ࣖ㸫࢖ࢾࣈࢼ⩌㞟 㸦Torreyo-Fagion japonicae Nakanishi et al.1970㸧ࡢኟ⥳ ᗈⴥᶞᯘ࡛࠶ࡿࠋ୧⩌㞟ࡣ୍㒊ࡢᆅᇦࢆ㝖࠸࡚࡯ࡰྠᾏᢤᇦ ࡟ΰᅾࡋ࡚࠾ࡾ㸪᫂☜࡟࡝ࡕࡽࡢ⩌㞟࡟༊ศࡉࢀࡿ࠿ࡣุู ࡛ࡁ࡞࠿ࡗࡓࠋ ௨ୖ㸪ࣇࣟࣛⓗせᅉ㸪⎔ቃⓗせᅉ㸪₯ᅾ⮬↛᳜⏕࠿ࡽ㸪ᙜ ᳜ᶞᯘࡢᴟ┦࡜ࡋ࡚ࡩࡉࢃࡋ࠸⩌㞟༢఩ࡢ᳜⏕ࢆࢡࣟࣔࢪ -ࣈࢼ⩌㞟࡜ุ᩿ࡋࡓࠋ 3.1.2 ୗ఩༢఩ タᐃࡍࡿ┠ᶆ⩌㞟ࡢ᳜ᶞᯘ࿘㎶࡟࠾ࡅࡿཧ⪃࡜ࡋ࡚㸪᳜ᶞ ิ␒ྕ䚷䚷䚷䚷䚷䚷䚷䚷䚷䚷䚷䚷䚷䚷䚷䚷䚷䚷䚷䚷1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 ࿴ྡ䠄Ꮫྡ䠅 ⏕ṧ⋡% ฟ⌧✀ B1 B2 B1 B2 B1 B2 S-K B1 B2 S-K B1 B2 B1 B2 ࢘ࣛࢪࣟࣀ࢟Aria japonica Decne 2࣭Ϩ 14.6 1

ࢱࣥࢼࢧ࣡ࣇࢱࢠࠉSymplocos coreana (H.Lév.) Ohwi ۑ

ࢡࣟࣔࢪࠉLindera umbellata Thunb. var. umbellata ۑ 1࣭1 ۑ 10.0 ௚2✀

ࢯࣚࢦࠉIlex pedunculosa Miq. +-2࣭ϩ ۑ 11.1 ࢿࢪ࢟ࠉLyonia ovalifolia (Wall.) Drude var. elliptica (Siebold et Zucc.)

Hand.-Mazz. +-2࣭ϩ ۑ 0.0

࢔࢝ࢩࢹࠉCarpinus laxiflora (Siebold et Zucc.) Blume 2࣭ϩ +-3࣭Ϫ 0.0

࢖ࢾࢩࢹࠉCarpinus tschonoskii Maxim. 1-4࣭ϩ +-3࣭ϩ 36.4 1 1 ࢜࢜࢖࣑࣡࢝࢞ͤSchizocodon soldanelloides Siebold et Zucc. var.

magnus (Makino) H.Haraɻ௚4✀

ࣇ࣓࢘ࣜࣥ࢘ࣔࢻ࢟ࠉIlex geniculata Maxim. ۑ ࣐ࣝࣂࣇࣘ࢖ࢳࢦͤRubus pectinellus Maxim.ɻ௚6✀

ࢳࣗ࢘ࢦࢡࢨࢧͤࠉSasa tyuhgokensis Makino

ࢳ࣐࢟ࢨࢧͤSasa palmata (Lat.-Marl. ex Burb.) E.G.Camus ۑ

ࢳࢩ࣐ࢨࢧͤSasa kurilensis (Rupr.) Makino et Shibata ۑ

ࢪࣗ࢘ࣔࣥࢪࢩࢲࠉPolystichum tripteron (Kunze) C.Presl ۑ ࢚ࣥࣞ࢖ࢯ࢘ͤTrillium apetalon Makinoɻ௚7✀

࣑ࢬࢼࣛࠉQuercus crispula Blume 1-3࣭ϫ 1-3࣭Ϭ 1-2࣭2 ۑ 68.0 1 1 ࢖࣑࣡࢞ࣛࠉHydrangea hydrangeoides (Siebold et Zucc.) B.Schulz ۑ 1࣭1 ۑ 1 ࢔࢜ࢲࣔࠉFraxinus lanuginosa Koidz. f. serrata (Nakai) Murata +࣭ϩ +࣭Ϩ 45.2 + + ࣓࢜࢜࢝ࣀ࢟ࠉViburnum furcatum Blume ex Maxim. +࣭Ϩ 1࣭Ϩ ۑ 30.0 1 ࣈࢼࠉFagus crenata Blume 4-5࣭Ϭ 1࣭ϩ 1-3࣭ϩ 3-4࣭4 +-2࣭2 ۑ 1࣭1 ۑ 42.0 4 2 1 ࢶࢱ࢘ࣝࢩࠉToxicodendron orientale Greene ۑ ۑ

ࢱ࣒ࢩࣂࠉMagnolia salicifolia (Siebld et Zucc.) Maxim. +-1࣭Ϩ ۑ 7.7 ௚5✀

࢔ࢭࣅࠉPieris japonica (Thunb.) D.Don ex G.Don subsp. Japonica +-2࣭ϩ 1࣭1 ۑ 1 ࢘ࣛࢪࣟࣀ࢟ࠉAria japonica Decne +-1࣭Ϫ 14.6 + ࢝ࢫ࣑ࢨࢡࣛࠉCerasus leveilleana (Koehne) H.Ohba +-1࣭ϩ ۑ 10.0

ࢥࣂࣀ࣐࢞ࢬ࣑ͤViburnum erosum Thunb.ɻ௚6✀

࣑࣐ࣖ࢖࣎ࢱͤLigustrum tschonoskii Decne.䚷௚4✀

࢖ࢾࣈࢼͤࠉFagus japonica Maxim.䚷௚4✀

ࢩࣟࣔࢪͤLindera triloba (Siebold et Zucc.) Blume䚷௚3✀

ࢳ࣐࢟ࢨࢧͤSasa palmata (Lat.-Marl. ex Burb.) E.G.Camus ۑ ۑ

ࢳࣗ࢘ࢦࢡࢨࢧͤSasa tyuhgokensis Makino

ࢳࢩ࣐ࢨࢧͤSasa kurilensis (Rupr.) Makino et Shibata

ࢡ࣐࢖ࢨࢧͤSasa senanensis (Franch. et Sav.) Rehder

ࢦ࣐࢟ͤViburnum sieboldii Miq.䚷௚4✀

ࢼࢼ࣐࢝ࢻࠉSorbus commixta Hedl. 33.8 1 1 + + ࣑ࢬ࣓ࠉBetula grossa Siebold et Zucc. 1-4࣭ϩ +࣭Ϩ 3-4࣭2 +࣭1 28.0 2 + 2 + ࢔ࢬ࢟ࢼࢩࠉAria alnifolia (Siebold et Zucc.) Decne. +-1࣭Ϭ +࣭Ϩ 31.7 1 + ࣐ࣖ࣎࢘ࢩࠉCornus kousa Buerger ex Hance subsp. Kousa +࣭ϩ +࣭1 46.7 + 1 2 ࢔࢜ࣁࢲࠉIlex macropoda Miq. +-1࣭ϫ +-1࣭Ϫ 20.0 + + ࢥࢼࣛࠉQuercus serrata Murray 3-5࣭Ϫ +-4࣭Ϫ 4-5࣭3 1࣭2 ۑ 58.0 ۑ 5 1 ࣐ࣖࢨࢡࣛࠉCerasus jamasakura (Siebold ex Koidz.) H.Ohba 66.3 ۑ + + ࣜࣙ࢘ࣈࠉClethra barbinervis Siebold et Zucc. +-1࣭Ϫ 1࣭Ϩ +-2࣭ϫ ۑ 1࣭1 3࣭1 ۑ 35.4 1 3 ࣑࢘࣡ࢬࢨࢡࣛࠉPadus grayana (Maxim.) C.K.Schneid. 1࣭Ϩ ۑ 1࣭1 ۑ 21.5 1 ࣐࣑ࣖࣔࢪࠉAcer amoenum Carrière var. matsumurae (Koidz.) +࣭Ϩ +࣭Ϩ ۑ 1࣭1 ۑ 52.0 ۑ 1 ࢘ࣜࣁࢲ࢚࢝ࢹࠉAcer rufinerve Siebold et Zucc. +-1࣭ϩ ۑ 1࣭1 ۑ 47.5 ۑ 1 ࢡࣜࠉCastanea crenata Siebold et Zucc. 1-3࣭ϫ 1-2 1࣭1 1 ࢶࣝ࢔ࢪࢧ࢖ࠉHydrangea petiolaris Siebold et Zucc. ۑ

࣐ࣖ࢘ࣝࢩࠉToxicodendron trichocarpum (Miq.) Kuntze +-1࣭ϩ ۑ ࢥࢩ࢔ࣈࣛࠉChengiopanax sciadophylloides (Franch. et Sav.)

C.B.Shang et J.Y.Huang +-1࣭Ϫ +-1࣭ϩ +࣭1 ۑ +࣭1 ۑ 10.0 ࢥࣁ࢘ࢳ࢚࣡࢝ࢹࠉAcer sieboldianum Miq. 1-3࣭ϫ +-1࣭ϩ 1-2࣭ϩ ۑ 11.7 ࣑ࢬ࢟ࠉCornus controversa Hemsl. ex Prain +࣭Ϩ ۑ 41.1 ࣐ࣖࣇࢪࠉWisteria brachybotrys Siebold et Zucc. +-1࣭Ϩ ۑ

࢚ࢦࣀ࢟ࠉStyrax japonicus Siebold et Zucc. +-2࣭ϩ ۑ 54.3 ۑ ࢡ࣐ࢩࢹࠉCarpinus japonica Blume 1-4࣭ϩ +-2࣭ϩ

࢚࢘ࣜ࢝ࢹࠉAcer crataegifolium Siebold et Zucc. +-1࣭ϩ ۑ ௚183✀ +࣭ϩ 1࣭Ϩ 2࣭Ϩ 1࣭ϩ ࢡࣟࣔࢪ㸫ࣈࢼ

㸫ள⩌㞟༊ศ✀ɻDifferential speacies of Sub-Association

㸫ள⩌㞟༊ศ✀ Differential speacies of Sub-Association

㸫ኚ⩌㞟༊ศ✀ Differential speacies of Variant

ࢡࣛࢫࡢᶆᚩ✀࣭㝶క✀ࠉCharacteristic speacies of Klasse and Companion speacies

+-1࣭ϩ +-2࣭ϫ +-1࣭ϩ ࢡࣟࣔࢪ㸫ࣈࢼ⩌㞟ᶆᚩ✀ࠉCharacteristic species of Linderoumbellatae-Fagetum creatae

ࢡࣜ㸫࣑ࢬࢼࣛ⩌㞟ᶆᚩ✀䚷Characteristic speacies of Castaneo-Quercetum crispulae 㸫ኚ⩌㞟༊ศ✀ɻDifferential speacies of Variant

᳜ᶞᯘ

㆑ู⾲㸦⿕ᗘ࣭ᖖᅾᗘ㸧 ࿘㎶ᶞᯘ㸦⿕ᗘ࣭ᖖᅾᗘ S-Kࡣฟ⌧✀࡟ࠐ 㸧 ┠ᶆ᳜⏕ ࢡࣜ㸫࣑ࢬࢼࣛ ࢡࣟࣔࢪ㸫ࣈࢼ ࢡࣜ㸫࣑ࢬࢼࣛ ᭱⤊┠ᶆ ୰ᮇ┠ᶆ

(5)

⾲-4 ࢡࣟࣔࢪ㸫ࣈࢼ⩌㞟ࡢୗ఩༢఩ࡢ⎔ቃ᮲௳

Table 4 Establishing environmental conditions of the lower unit ᯘ㏆㞄ࡢ⎩⳯ἑ∾ሙᶓ᳃ᯘෆ࡛2 ࣉࣟࢵࢺ㸦(1)㸪(2)㸧࡜㙾ࣨ ᡂ┴᭷ᯘ࡛2 ࣉࣟࢵࢺ㸦(3)㸪(4)㸧ࢆ㑅ᐃࡋࡓ㸦⾲-2㸧ࠋ㆑ู ⾲࡟グ㍕ࡉࢀ࡚࠸ࡿ✀ࢆ⾲-3 ࡢ 1 ิ┠࡟♧ࡍࠋࡲࡓࡑࡢ୰ ࡛㸪⮬↛ᯘࡢ㧗ᮌ࣭ள㧗ᮌᒙ࡟ฟ⌧ࡋࡓ✀࡟ࡣ⿕ᗘ࣭ᖖᅾᗘ ࢆ㸪పᮌᒙ௨ୗ࡟ฟ⌧ࡋࡓ✀࡟ࡣࠐࢆグࡋࡓ㸦⾲-3 ࡢ 6㹼8 ิ ┠㸧ࠋྛୗ఩༢఩ࡢศᕸ᮲௳࡜⮬↛ᯘฟ⌧✀ࡼࡾ㸪ㄪᰝࡋࡓ ⮬↛ᯘࡣࢡࣟࣔࢪ㸫ࣈࢼ⩌㞟඾ᆺள⩌㞟ࢳࢩ࣐ࢨࢧኚ⩌㞟 㸦Lindero umbellatae-Fagetum creatae, Typische Subass. ver. von of Lindero umbellatae-Fagetum creatae Sasa

kurilensis㸧࡜ྠᐃࡉࢀࡓࠋࡓࡔࡋ㸪᳜ᶞᯘࡣㄪᰝࡋࡓ⮬↛ᯘ ࡼࡾᶆ㧗ࡀ200㹼300 m పࡃ㸪ࡑࡢࡲࡲ᳜ᶞᯘࡢ┠ᶆ࡜ࡋ࡚ タᐃࡍࡿࡇ࡜ࡣ୙㐺ษ࡛࠶ࡿࠋࡑࡇ࡛᳜ᶞᯘࡢ⎔ቃࢆ⪃៖ࡋ ࡚┠ᶆ᳜⏕ࢆ෌᳨ウࡋࡓࠋྛள⩌㞟ࡢ❧ᆅ᮲௳ࢆ⾲-4 ࡟♧ ࡍࠋ᳜ᶞᯘࡣ㸪(1)ྎᆅ≧ᆅᙧࡢᖹᆠ࡞❧ᆅ࡟Ꮡᅾࡋ㸪(2)ᶆ㧗 ࡣ⣙700 m ࡛࠶ࡾ㸪(3)᳜ᶞᯘෆ࡟ࡣࢳࢩ࣐ࢨࢧ࡛ࡣ࡞ࡃࢳ ࣐࢟ࢨࢧࡀฟ⌧ࡍࡿ㸦⾲-3 ࡢ 13 ิ┠㸧ࠋ௨ୖ 3 Ⅼ࠿ࡽ㸪᳜ ᶞᯘࡢ᭱⤊┠ᶆ࡜ࡋ࡚ࡩࡉࢃࡋ࠸᳜⏕ࡣࢡࣟࣔࢪ㸫ࣈࢼ⩌㞟 ඾ᆺள⩌㞟ࢳ࣐࢟ࢨࢧኚ⩌㞟㸦Lindero umbellatae-Fagetum

creatae, Typische Subass. ver. von Sasa palmata㸧࡜ุ᩿ࡋ ࡓࠋ ࡲࡓཧ⪃࡜ࡋ࡚㸪ྛள⩌㞟ࡢ༊ศ✀࡜᳜᱂ᮌࡢᶞ✀ู⏕ṧ ⋡ᡂ⦼ࢆẚ㍑ࡋࡓ࡜ࡇࢁ㸪࢜࢜࢖࣑࣡࢝࢞ள⩌㞟ࡢ༊ศ✀ࡣ ࠸ࡎࢀࡶ஝ᛶ❧ᆅࡢᣦᶆ✀࡛࠶ࡾ㸪ࡑࢀࡽࡢ࠺ࡕࡢከࡃࡀ᳜ ᶞᯘ࡟࠾࠸࡚⏕ṧ⋡ᡂ⦼ࡀ୙Ⰻ࡛࠶ࡗࡓࠋࡇࡢࡇ࡜࠿ࡽ㸪ୗ ఩༢఩ࡢ≉ᛶḟ➨࡛ࡣ㸪༊ศ✀࡜᳜᱂ᮌࡢᶞ✀ู⏕ṧ⋡ᡂ⦼ ࡜ࡢ↷ྜ࡟ࡼࡾ㸪┠ᶆ࡜ࡋ࡚㐺ษ࡞᳜⏕ࢆุ᩿ࡍࡿࡇ࡜ࡀྍ ⬟࡜⪃࠼ࡽࢀࡓࠋ 3.1.3 ✀⤌ᡂ ᭱⤊┠ᶆ࡜ࡋ࡚෌タᐃࡉࢀࡓࢡࣟࣔࢪ㸫ࣈࢼ⩌㞟඾ᆺள⩌ 㞟ࢳ࣐࢟ࢨࢧኚ⩌㞟ࡢලయⓗ࡞✀⤌ᡂࢆ⾲-3 ࡢ 14,15 ิ┠࡟ ♧ࡋࡓࠋ᳜ᶞᯘࡢ┠ᶆ᳜⏕ࡣࣈࢼࡀඃ༨ࡋ㸪࣑ࢬ࣓ࡸ࣑ࢬࢼ ࣛࡀΰ⏕ࡍࡿࣈࢼᯘ࡜࡞ࡗࡓࠋ 3.2 㐺ษ࡞㐣⛬ࡢ᳨ウ 3.2.1 㑄⛣㏵୰┦࡟࠶ࡓࡿ୰㛫┠ᶆ᳜⏕ ᴟ┦ࡢ⩌㞟࡟㛵ࢃࡽࡎ㸪୰ᅜᆅ᪉ࡢࣈࢼࢡࣛࢫᇦ࡟࠾ࡅࡿ ஧ḟᯘࡣ࣑ࢬࢼࣛ㸪࢖ࢾࢩࢹ㸪ࢡ࣐ࢩࢹ㸪࢔࢝ࢩࢹ㸪ࢡࣜ ࡞࡝࠿ࡽ࡞ࡾ㸪ࡇࢀࡽࡣࢡࣜ㸫࣑ࢬࢼࣛ⩌㞟㸦 Castaneo-Quercetum crispulae㸧࡜ࡋ୍࡚ࡘ࡟ࡲ࡜ࡵࡽࢀࡿ 9)ࠋࡼࡗ ࡚㸪୰㛫┠ᶆࡢ⩌㞟࡜ࡋ࡚ࢡࣜ㸫࣑ࢬࢼࣛ⩌㞟ࡀࡩࡉࢃࡋ࠸ ⾲-5 ྛ┠ᶆ᳜⏕ᵓᡂ✀ࡢ 2018 ᖺࡢᮏᩘ࡜ᶞ✀㌿᥮࡟ᚲせ࡞ᮏ ᩘࡢ๭ྜ

Table 5 The number of species that make up each target vegetation in 2018, and the number of species that require tree species conversion

࡜ุ᩿ࡋࡓࠋ୰㛫┠ᶆ࡟ᑐᛂࡍࡿ࿘㎶ࡢ஧ḟᯘ࡜ࡋ࡚㸪᳜ᶞ ᯘࡢすഃ࡟㞄᥋ࡍࡿࢥࢼࣛᯘ࡛1 ࣉࣟࢵࢺ㸪ࣈࢼࡢ᳃ᕤሙᮾ ഃཬࡧすഃ࡟ศᕸࡍࡿࢥࢼࣛᯘࡑࢀࡒࢀ࡛1 ࣉࣟࢵࢺࡢ㸪ྜ ィ3 ࣉࣟࢵࢺ࡛ㄪᰝࢆ⾜ࡗࡓࠋ᪤Ꮡᩥ⊩࡟ࡼࡿࢡࣜ㸫࣑ࢬࢼ ࣛ⩌㞟ࡢฟ⌧✀ࡢ࠺ࡕ㸪ㄪᰝࡋࡓ஧ḟᯘ࡟ฟ⌧ࡋࡓ✀ࢆ⾲-3 ࡢ9㹼11 ิ┠࡟♧ࡍࠋ ࢡࣜ㸫࣑ࢬࢼࣛ⩌㞟ࡣࢥࣂࣀ࣐࢞ࢬ࣑ள⩌㞟㸦Subass. von Viburnum erosum f. punctatum㸧࡜࣑࣐ࣖ࢖࣎ࢱள⩌ 㞟㸦Subass. von Ligustrum tschonoskii㸧࡟༊ศࡉࢀࡿࠋ ࢥࣂࣀ࣐࢞ࢬ࣑ள⩌㞟ࡢୗ఩༢఩࡛࠶ࡿࢳ࣐࢟ࢨࢧኚ⩌㞟 ࡣ㸪ࢳ࣐࢟ࢨࢧࡀ㧗⿕ᗘ࡛⿕ࡗ࡚࠸ࡿᯘศࡀከ࠸ࠋ㧗ᮌᒙࡣ ࣑ࢬࢼࣛࡢ࡯࠿㸪ࢥࢼࣛࡀ⿕ᗘ5 ࡛ඃ༨ࡍࡿᯘศࡶࡋࡤࡋ ࡤࡳࡽࢀࡿ9)ࠋㄪᰝࡋࡓ஧ḟᯘ࡛ࡶ㸪ⲡᮏᒙ࡟ࢳ࣐࢟ࢨࢧ㸪 㧗ᮌᒙ࡟ࢥࢼࣛࡀ㧗⿕ᗘ࡛ඃ༨ࡋ࡚࠸ࡓࡇ࡜࠿ࡽ㸪ㄪᰝࡋࡓ ஧ḟᯘࡢ᳜⏕ࡣ㸪ࢡࣜ㸫࣑ࢬࢼࣛ⩌㞟ࢥࣂࣀ࣐࢞ࢬ࣑ள⩌㞟 ࢳ࣐࢟ࢨࢧኚ⩌㞟㸦Castaneo-Quercetum crispulae Subass. von Viburnum erosum f. punctatum. ver. von

Sasa palmata㸧࡜ྠᐃࡉࢀ㸪ࡇࢀࢆ᳜ᶞᯘࡢ୰㛫┠ᶆ࡜ࡋ ࡓࠋ  ㆑ู⾲㸪᳜ᶞᯘࡢ⏕ṧ⋡㸪࿘㎶஧ḟᯘฟ⌧✀ࡼࡾ㸪୰㛫┠ ᶆࡢලయⓗ࡞✀⤌ᡂࡣ⾲-3 ࡢ 16,17 ิ┠ࡢࡼ࠺࡟タᐃࡋࡓࠋ 㧗ᮌᒙ࡟ࢥࢼࣛ㸪ள㧗ᮌᒙ࡟ࣜࣙ࢘ࣈࡀඃ༨ࡋ㸪ࣈࢼࡸ࢖ࢾ ࢩࢹࡀΰ⏕ࡍࡿࢥࢼࣛᯘ࡜࡞ࡗࡓࠋ 3.2.2 ┠ᶆ࡬ࡢㄏᑟ㐣⛬ 2018 ᖺ᫬Ⅼࡢ᳜᱂ᮌᶞ✀ูᮏᩘ㸪᭱⤊┠ᶆཬࡧ୰㛫┠ᶆࡢ 㧗ᮌᒙᵓᡂ✀ࡢඃ༨ᗘࢆ⾲-5 ࡟♧ࡋࡓࠋ┠ᶆ࡟⮳ࡿ㐣⛬࡟ࡘ ࠸࡚㸪ࠕ┤㐩ᆺࠖࢆ᥇⏝ࡍࡿሙྜ࡜㸪ࠕ㑄⛣ᆺࠖࢆ᥇⏝ࡍࡿ ሙྜࡢ㸪ᶞ✀㌿᥮ᚲせᮌࡢ๭ྜ㸦%㸧ࢆྛࠎ⟬ฟࡋࡓ⤖ᯝ㸪 ๓⪅࡛66.6%㸪ᚋ⪅࡛ 67.2%࡛࠶ࡗࡓࠋ୧⪅࡛࡯࡜ࢇ࡝ᕪࡀ ぢࡽࢀࡎ㸪6 ๭௨ୖࡢ⌧Ꮡᮌࢆ㝖ఆࡋࡓ࠺࠼࡛⿵᳜ࡍࡿᚲせ ࡀ࠶ࡿࡇ࡜࠿ࡽ㸪࡝ࡕࡽࡢ㐣⛬ࡶᐇົୖྜ⌮ⓗ࡛ࡣ࡞࠸࡜⪃ ࠼ࡽࢀࡓࠋࡑࡇ࡛㸪ᙜ᳜ᶞᯘ࡛ࡣ㸪㝖ఆ࡜⿵᳜࡟ࡼࡗ࡚ᶞ✀ ㌿᥮ࡍࡿࡢ࡛ࡣ࡞ࡃ㸪᭱⤊┠ᶆࡢࣈࢼᯘ࡜㸪୰㛫┠ᶆ࡜ࡋ࡚ ள⩌㞟ྡ ᆅᙧ࣭ᶆ㧗 ᆅ㉁ ࢜࢜࢖࣑࣡࢝࢞ள⩌㞟

Subass. von Shortia magna ᑿ᰿㒊ࡸᩳ㠃ᆅ ஝ᛶ❧ᆅ

඾ᆺள⩌㞟

tipische Subass ࣐ࣝࣂࣇࣘ࢖ࢳࢦள⩌㞟࡜࢜࢜࢖࣑࣡࢝࢞ள⩌㞟࡜࡟ࡣࡉࡲࢀࡓᒣᆅࡢ୰⭡ᇦ ୰㛫ⓗ ࣐ࣝࣂࣇࣘ࢖ࢳࢦள⩌㞟

Subass. von. Rubus rectinellus ᒣᆅࡢ㡬ୖ௜㏆ࡸᑿ᰿ୖ㒊ᶆ㧗㸸⣙P௨ୖ ‵ᛶ❧ᆅ

2018ᖺᮏᩘ 㸦ඃ༨๭ྜ%㸧 ᳜ᶞᯘ ᭱⤊┠ᶆ ୰ᮇ┠ᶆ 䛂┤㐩ᆺ䛃 䛂⤒⏤ᆺ䛃 ࣈࢼ 243㸦21.8㸧 67.5㸦66.5㸧 0㸦0.0㸧 44.7 -21.8 ࢘ࣛࢪࣟࣀ࢟ 6㸦0.5㸧 5.5㸦5.4㸧 0㸦0.0㸧 4.9 -0.5 ࣑ࢬ࣓ 19㸦13.7㸧 17.5㸦17.2㸧 17.5㸦13.7㸧 15.5 12.0 ࣑ࢬࢼࣛ 84㸦7.5㸧 5.5㸦5.4㸧 5.5㸦4.3㸧 -2.1 -3.2 ࢼࢼ࣐࢝ࢻ 44㸦3.9㸧 5.5㸦5.4㸧 0.5㸦0.4㸧 1.5 -3.6 ࢥࢼࣛ 206㸦18.5㸧 0㸦0.0㸧 87.5㸦68.4㸧 -18.5 49.9 ࣜࣙ࢘ࣈ 122㸦10.9㸧 0㸦0.0㸧 5.5㸦4.3㸧 -10.9 -6.6 ࣐ࣖࢨࢡࣛ 55㸦4.9㸧 0㸦0.0㸧 0.5㸦0.4㸧 -4.9 -4.5 ࢖ࢾࢩࢹ 35㸦3.1㸧 0㸦0.0㸧 5.5㸦4.3㸧 -3.1 1.2 ࣐ࣖ࣎࢘ࢩ 1㸦0.1㸧 0㸦0.0㸧 5.5㸦4.3㸧 -0.1 4.2 ࡑࡢ௚ 301㸦27.0㸧 0㸦0.0㸧 0㸦0.0㸧 -27.0 -27.0 ྜィ 1116㸦100.0㸧 101.5㸦100.0㸧 128㸦100.0㸧 㸫 㸫 66.6 67.2 ᶞ✀㌿᥮ᚲせᮌࡢ๭ྜ㸦%㸧 ᖹᆒ⿕ᗘⓒศ⋡1)㸦ඃ༨๭ྜ%㸧 ኚ໬㔞㸦ඃ༨๭ྜࡢ%㸧

(6)

ὀ㸧ۑ㸸ᮏ᮶᳜᱂ࡉࢀࡿ࡭ࡁ࡛࠶ࡗࡓ✀⤌ᡂ࡜㸪ࡑࡢ㑄⛣㐣⛬ࡢ᳜⏕ ە㸸ᐇ㝿࡟᳜᱂ࡉࢀࡓ✀⤌ᡂ࡜㸪⌧ᅾཬࡧᑗ᮶ࡢ᳜⏕ ᅗ-3 ┠ᶆ࡟⮳ࡿ㐣⛬ࡢ᳨ウ⤖ᯝ

Fig. 3 Result of evaluating the approach used to reach the Goal ࠸ࡓࢥࢼࣛᯘࡢ୧ᵓᡂ✀ࢆྜࢃࡏᣢࡗࡓ᳜⏕ࢆ⤒⏤ࡋ࡞ࡀ ࡽ㸪ࢥࢼࣛᯘ࡜ࣈࢼᯘࡢ࡝ࡕࡽ࡟ࡶヱᙜࡋ࡞࠸✀㸪ࢥࢼࣛᯘ ᵓᡂ✀㸪ࡢ㡰࡛㝖ఆࡍࡿࡇ࡜࡛㸪ᚎࠎ࡟᭱⤊┠ᶆࡢࣈࢼᯘ࡬ ࡜㏆࡙ࡅࡿࡇ࡜ࡀྜ⌮ⓗ࡛࠶ࡿ࡜⪃࠼ࡽࢀࡓ㸦ᅗ-3㸧ࠋ ᙜ᳜ᶞᯘ࡛ࡣ㸪␗࡞ࡿ㑄⛣ẁ㝵࡟ᒓࡍࡿᶞ✀ࡀ᳜᱂ࡉࢀࡓ ࡓࡵ㸪ᴟ┦㸪୰ᮇ┦࡝ࡕࡽ࡜ࡶࡘ࠿࡞࠸ᶞ✀ᵓᡂ࡜࡞ࡾ㸪ࠕ┤ 㐩ᆺࠖࠕ㑄⛣ᆺࠖ࡝ࡕࡽࡢ㐣⛬࡟஌ࡏ┤ࡍࡇ࡜ࡶ㞴ࡋࡃ࡞ࡗ ࡓ࡜⪃࠼ࡽࢀࡿࠋ 4. ࡲ࡜ࡵ ᪤Ꮡࡢ࢖࣋ࣥࢺᆺ᳜ᶞᯘࢆᑐ㇟࡟㸪ᩥ⊩㸪᳜ᶞᯘ㸪࿘㎶ᶞ ᯘࢆㄪᰝࡍࡿࡇ࡜࡟ࡼࡾ㸪┠ᶆࢆ᫂☜࡟෌タᐃࡍࡿ᪉ἲ࡜㸪 ࡑࡇ࡬ࡢㄏᑟ㐣⛬ࢆ㸪஦౛ⓗ࡟᳨ウࡋࡓࠋ ┠ᶆࢆ෌タᐃࡍࡿ㝿㸪≉࡟᳜ᶞᯘ࿘㎶࡛ࡢ㐣ཤࡢ᳜⏕ࢹ࣮ ࢱ㸪᳜ᶞᯘ࿘㎶ࡢᶞᯘ࡛ࡢ᳜⏕ࢹ࣮ࢱࡣ㸪┠ᶆࢆලయ໬ࡍࡿ ࡓࡵࡢ᝟ሗ࡜ࡋ࡚᭷ຠ࡛࠶ࡗࡓࠋࡲࡓ㸪᳜᱂ᮌࡢ⏕ṧ⋡ࡣ㸪 ┠ᶆ᳜⏕ࡢุ᩿࡟᭷ຠ࡞᝟ሗ࡜࡞ࡾ࠺ࡿࡇ࡜ࡀ♧၀ࡉࢀࡓࠋ ┠ᶆ࡬ࡢㄏᑟ㐣⛬ࡣ㸪᳜ᶞᯘࡢ⌧✀⤌ᡂ࡜㸪୰㛫┠ᶆཬࡧ ᭱⤊┠ᶆྛࠎࡢ㧗ᮌᒙࡢ✀⤌ᡂࡢẚ㍑࡟ࡼࡗ᳨࡚ウࢆヨࡳ ࡓࠋࡑࡢ⤖ᯝ㸪௒ᅇࡢ஦౛࡛ࡣ㸪ࠕ┤㐩ᆺࠖࡸࠕ㑄⛣ᆺࠖ࡟ ㌶㐨ಟṇࡉࡏࡿࡢࡣ࡝ࡕࡽࡶ኱ᖜ࡞㝖ఆࡸ⿵᳜ࡀᚲせ࡜࡞ࡿ ࡓࡵ㸪ࡑࡢ୰㛫ࢆ⤒⏤ࡍࡿࡢࡀྜ⌮ⓗ࡜ุ᩿ࡉࢀࡓࠋ ௒ᚋࡣ㸪␗࡞ࡿ㑄⛣⣔ิ࣭㑄⛣ẁ㝵ࡢᶞ✀ࡀΰྜࡋ࡚᳜ᶞ ࡉࢀࡓ஦౛࡟ࡘ࠸࡚ࡶ㸪┠ᶆ෌タᐃ࡜ࡑࡢㄏᑟ㐣⛬࡟ࡘ࠸࡚ ᳨ウࡍࡿࡇ࡜ࡀㄢ㢟࡛࠶ࡿࠋ ㅰ㎡㸸ࢧࣥࢺ࣮࣮ࣜ࣍ࣝࢹ࢕ࣥࢢࢫ ᰴ ཬࡧࢧࣥࢺ࣮ࣜࣉࣟ ࢲࢡࢶ ᰴ ࡟ࡣ㸪ㄪᰝ඲⯡࡟ࢃࡓࡾ㓄៖࠸ࡓࡔ࠸ࡓࠋࡲࡓ㸪 ᰴ㸧すṊ㐀ᅬ࡟ࡣࠊ᳜ᶞ࡟㛵ࡍࡿࢹ࣮ࢱࢆࡈᥦ౪㡬࠸ࡓࡔ࠸ ࡓࠋグࡋ࡚῝ࡃឤㅰ⏦ࡋୖࡆࡓ࠸ࠋ ᘬ⏝ᩥ⊩

1) Braun-Blanquet, j. (1964) Pflanzensoziologie. Grundzüge der Vegetationskunde. 3. Aufl. 865pp. Wien. (ࣈࣛ࢘ࣥ-ࣈ ࣛࣥࢣ, J. 㕥ᮌ᫬ኵ (ヂ) 1971. ᳜≀♫఍ᏛϨ,ϩ, ᮅ಴᭩ᗑ) 2) ༓ᕸᣅ⏕࣭᪥⨨ెஅ (2017) ⮬↛බᅬ࡟࠾ࡅࡿ⏕≀ከᵝᛶ࡟ 㓄៖ࡋࡓ᳜⏕ィ⏬ࡢ⟇ᐃᡭἲࡢ᳨ウ㸫኱ᒣ㞃ᒱᅜ❧බᅬࢆ ஦౛࡜ࡋ࡚㸫. ᬒほ⏕ែᏛ, 22(1):11-32 3) ⚟ᓥྖ࣭㧗◁⿱அ࣭ᯇ஭ဴဢ࣭すᑿᏕె࣭႐ᒇṊ㇏࣭ᖖ෠㇏ (1995) ᪥ᮏࡢࣈࢼᯘ⩌ⴠࡢ᳜≀♫఍Ꮫⓗ᪂య⣔. ᪥ᮏ⏕ែ Ꮫ఍ㄅ, 45:79-98 4) ஭ୖᗣᖹ (1993) ⥳ᆅࡢ⎔ቃタィ.஭ᡭஂⓏ࣭டᒣ❶⦅, ⥳ᆅ ⏕ែᏛ. ᮅ಴᭩ᗑ, pp.65-76 5) Ἑ㔝᫛୍ (1977) ᳜≀ࡢ࡞࠿ࡲ࡜ᗈࡀࡾ. ᐑ⬥᫛⦅, ᪥ᮏࡢ ᳜⏕. Ꮫ◊, pp.1-19 6) ๓ᕝᩥ㞝 (1949) ᪥ᮏ᳜≀༊⣔࡜ࡋ࡚ࡢ࣐ࢿ࢟ࢩ࢔. ᳜≀◊ ✲㞧ㄅ, 24:91-96 7) ᐑ⬥᫛࣭⸨ཎ୍⧙࣭ᑠ⃝ṇ᫂ (1993) ࡩࡿࡉ࡜ࡢᮌ࡟ࡼࡿࡩ ࡿࡉ࡜ࡢ᳃࡙ࡃࡾ㸫₯ᅾ⮬↛᳜⏕࡟ࡼࡿ᳃ᯘ⏕ែ⣔ࡢ෌⏕ ἲ㸫(ᐑ⬥᪉ᘧ࡟ࡼࡿ⎔ቃಖ඲ᯘ๰㐀). ᶓ὾ᅜ❧኱Ꮫ⎔ቃ⛉ Ꮫ◊✲ࢭࣥࢱ࣮⣖せ, 19:73-107 8) ᐑ⬥᫛ (1990) ᪥ᮏ᳜≀⩌ⴠᅗㄝ. ⮳ᩥᇽ, 800pp. 9) ᐑ⬥᫛ (1983) ᪥ᮏ᳜⏕ㄅ ୰ᅜ. ⮳ᩥᇽ, 540pp. 10) ᐑ⬥᫛ (1983) ᪥ᮏ᳜⏕ㄅ ୰ᅜ ௜⾲ 17. ⮳ᩥᇽ 11) ୰ᓥᩔྖ࣭㣴∗ᚿ஀ኵ࣭ᒣ⏣ᏹஅ࣭㥖㉮⿱அ (1997) ‴ᓊᕤ ሙᆅ࡛ࡢࠕ࢚ࢥࣟࢪ࣮⥳໬ࠖ࡟࠾ࡅࡿ᪋ᕤ18 ᖺ┠ࡢᯘศᵓ 㐀. ࣛࣥࢻࢫࢣ࣮ࣉ◊✲, 61(5):505-510 12) ᪥ᮏ⥳໬ࢭࣥࢱ࣮ (1997) ࢚ࢥࣟࢪ࣮⥳໬ᢏ⾡࣐ࢽࣗ࢔ࣝ (ᗂⱑ᳜᱂ᢏ⾡ࡢᡭᘬࡁ). ᪥ᮏ⥳໬ࢭࣥࢱ࣮, 112pp. 13) ᒸᮧಇ㑥 (2004) ⏕ែᏛⓗΰ᧛࣭ΰ᳜ἲࡢ⌮ㄽ࣭ᐇ㊶࣭ホ౯ ఫẸཧຍ࡟ࡼࡿ⮬↛࡟㏆࠸ᶞᯘࡢ෌⏕ἲ. ▼⊁ᕝ᣺⯆㈈ᅋ, 71pp. 14) ᒸᮧಇ㑥࣭ᮡᒣ⿱࣭ྜྷ஭ཌᚿ (2015) ⏕ែᏛⓗΰ᧛࣭ΰ᳜ἲ ࡟ ࡼ ࡿ ⮬ ↛࡟㏆ ࠸ ᶞ ᯘ ෌⏕ࡢ ホ ౯. ᪥ᮏ⥳໬ᕤᏛ఍ㄅ, 31(2):230-238 15) ᴬཎ⳯ࠎ࣭㛗ᓥၨᏊ࣭ᔲ⏣▱ᕹ࣭㧗⏣◊୍࣭⏣୰࿴༤ (2015) ⮬↛㓄᳜ᢏ⾡࡟ࡼࡿ᳜᱂ᚋ⣙20 ᖺࡀ⤒㐣ࡋࡓἲ㠃ࡢᯘศᵓ 㐀̿࿘㎶⮬↛ᯘ࡜ࡢ㢮ఝᛶ̿, ᪥ᮏ⥳໬ᕤᏛ఍ㄅ, 41(1):109 -114 16) బࠎᮌዲஅ (1973) ᳜≀♫఍Ꮫ.⏕ែᏛㅮᗙ 4, ඹ❧ฟ∧, 158pp. 17) ᔲ⏣▱ᕹ࣭㛗ᓥၨᏊ࣭㧗⏣◊୍࣭⏣୰࿴༤ (2014) ඛ㥑✀,㑄 ⛣୰࣭ᚋᮇ✀ࡢΰ᳜࡟ࡼࡿἲ㠃⥳໬ࡢึᮇ⏕⫱≧ἣ. ᪥ᮏ⥳ ໬ᕤᏛ఍ㄅ, 39 (3):422-428 18) 㫽ྲྀ┴, ࡜ࡗ࡜ࡾ Web ࣐ࢵࣉ 㫽ྲྀ┴ᆅ⌮᝟ሗබ㛤ࢩࢫࢸ࣒ ᳃ᯘ᝟ሗ http://www2.wagmap.jp/pref-tottori/ top/select. asp?dtp=12&pl=3 (ཧ↷: 2019 ᖺ 12 ᭶ 17 ᪥) 19) Ώ㎶ᐃඖ (2002) ᐩኈᒣ⮬↛ࡢ᳃࡙ࡃࡾ̿ࣃࢵࢳ᳜᱂ἲࢆ ⏝࠸ࡓᴟ┦ᯘᵓᡂ✀࡟ࡼࡿ⮬↛ᯘࡢ᚟ඖ̿. ᳜⏕᝟ሗ, 6:9-14 20) ྜྷ㔝▱࣭᫂Ṋ⏣㐍 (2016) ᗂⱑ᳜᱂ᢏ⾡࡛๰ฟࡋࡓᶞᯘ࡟࠾ ࡅࡿ⮬↛㛫ᘬࡁ̿㛗㔝┴ୖ⏣ᕷ᪥⨨㟁ᶵ⥳ᆅࡢ᳜᱂ᚋ27 ᖺ ┠ࡢ஦౛̿. ⮬↛⎔ቃ᚟ඖ◊✲, 8(1):43-49 (2020 ᖺ 5 ᭶ 27 ᪥ཷ⌮)

Table 2 Survey results from natural forests
Table 3 Results of each survey used for to set targets and species composition of target vegetation
Table 5  The number of species that make up each target    vegetation in 2018, and the number of species that  require tree species conversion
Fig. 3  Result of evaluating the approach used to reach the    Goal  ࠸ࡓࢥࢼࣛᯘࡢ୧ᵓᡂ✀ࢆྜࢃࡏᣢࡗࡓ᳜⏕ࢆ⤒⏤ࡋ࡞ࡀ ࡽ㸪ࢥࢼࣛᯘ࡜ࣈࢼᯘࡢ࡝ࡕࡽ࡟ࡶヱᙜࡋ࡞࠸✀㸪ࢥࢼࣛᯘ ᵓᡂ✀㸪ࡢ㡰࡛㝖ఆࡍࡿࡇ࡜࡛㸪ᚎࠎ࡟᭱⤊┠ᶆࡢࣈࢼᯘ࡬ ࡜㏆࡙ࡅࡿࡇ࡜ࡀྜ⌮ⓗ࡛࠶ࡿ࡜⪃࠼ࡽࢀࡓ㸦ᅗ -3 㸧ࠋ    ᙜ᳜ᶞᯘ࡛ࡣ㸪␗࡞ࡿ㑄⛣ẁ㝵࡟ᒓࡍࡿᶞ✀ࡀ᳜᱂ࡉࢀࡓ ࡓࡵ㸪ᴟ┦㸪୰ᮇ┦࡝ࡕࡽ࡜ࡶࡘ࠿࡞࠸ᶞ✀ᵓᡂ࡜࡞ࡾ㸪ࠕ┤ 㐩ᆺࠖࠕ㑄⛣ᆺࠖ࡝ࡕࡽࡢ㐣⛬࡟஌

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