Biodiversity and Conservation in Ili River Valley, Xinjiang
-
摘要:
目的 明确新疆伊犁河谷地区的生物多样性组成、空间分布和保护现状,为该地区的生物多样性保护和管理提供参考依据。 方法 基于文献资料的收集和查阅,以伊犁河谷分布的主要野生生物类群(包括维管植物、苔藓、地衣、大型真菌、昆虫、脊椎动物)为研究对象,整理了该地区生物物种名录及其县级地理空间分布数据,并基于此统计了该地区主要生物类群的数量组成特征及保护物种数量特征,分析了该地区物种多样性及县域保护优先等级的空间分布格局。 结果 1)该地区分布的主要野生生物共计3945种,隶属于445科1627属。其中,维管植物数量最多,占统计物种总数的52.7%;2)6类生物科级组成中均以寡型科数量占比最多,单型科次之,大、中型科最少。各类群中,大、中型科包含的属和种的数量占比较高;3)不同类群的物种多样性存在明显的空间差异。县域水平物种多样性不一致,伊宁县物种组成最丰富,包含了该地区74.8%的物种;4)该地区保护物种共计294种,占统计物种总数的7.5%。类群保护空缺较大,尤其是地衣、大型真菌、苔藓和昆虫。空间保护空缺以尼勒克县和昭苏县最为突出。 结论 伊犁河谷是新疆生物多样性分布的核心地区,关于开展该地区生物多样性保护工作,建议:1)将该地区列为新疆维吾尔自治区生物多样性保护重点关注地区;2)在生物类群保护层面,优先加强对地衣、大型真菌、苔藓和昆虫的关注力度;3)在县域空间层面,优先关注尼勒克县和昭苏县。 Abstract:Objective To clarify the biodiversity composition, spatial distribution and conservation status of the Ili River Valley region of Xinjiang, and to provide a reference basis for biodiversity conservation and management in this region. Method Based on the literature and references, we selected the major wildlife groups (vascular plants, mosses, lichens, macrofungi, insects, and vertebrates) distributed in the Ili River Valley. The list of biological species in the region and their county-level geospatial distribution data were compiled. Based on the data, the quantitative composition characteristics of major biological groups and protected species were counted. The spatial distribution patterns of species diversity and county-level conservation priorities in the region were analyzed. Result 1) A total of 3945 species of wildlife were distributed in the region, belonging to 1627 genera in 445 families. Among them, vascular plants are the most numerous, accounting for 52.7% of the total number of species counted. 2) The number of oligotypic families accounts for the largest proportion of the composition of all six biological family levels. The numberof genera and species was relatively high in plurimotypic and mesotypic families. 3) There were obvious spatial differences in species diversity of different taxa. Species diversity was not uniform at the county level, with Yining County having the richest species composition, containing 74.8% of the species in the region. 4) A total of 294 species were protected in the region, accounting for 7.5% of the total number of species counted. There was a large gap in the conservation of biological groups, especially lichens, macrofungi, mosses, and insects, and in the conservation of space, especially Nilka and Zhaosu County. Conclusion Regarding the development of biodiversity conservation in the region, it is recommended that 1) the region be listed as a key area of concern for biodiversity conservation in the Xinjiang Uygur Autonomous Region; 2) at the level of biological groups conservation, priority be given to strengthening the focus on lichens, macrofungi, mosses and insects; and 3) at the spatial level of county, priority be given to Nilka and Zhaosu County. -
图 2 新疆伊犁河谷地区各生物类群优势科、属对比
注:a.不同生物类群优势科(属)所包含的物种总数;b.不同生物类群优势科(属)所包含的物种总数占该类群物种总数的比例。a. Total number of species included in the dominant families (genera) of different biological groups; b. The proportion of the total number of species included in the dominant families (genera) of different groups to the total number of species in that group.
Figure 2. Comparison of dominant families and genera of various biological groups in Ili River Valley, Xinjiang
图 4 新疆伊犁河谷地区各生物类群物种丰富度空间分布等级
注:物种丰富度空间分布等级共分为5级,Ⅰ-Ⅴ级代表物种丰富度依次增加,Ⅴ级为物种丰富度最高等级。The spatial distribution of species richness is divided into five levels, Ⅰ-Ⅴ indicates the increasing species richness, and Ⅴ indicates the highest species richness.
Figure 4. Spatial distribution level of species richness of various biological groups in Ili River Valley, Xinjiang
图 5 新疆伊犁河谷地区生物多样性空间保护优先等级
注:生物多样性空间保护优先等级共分为5级,Ⅰ-Ⅴ级代表保护优先次序,Ⅴ级为最优先保护等级。The priority level of biodiversity spatial conservation is divided into five levels, Ⅰ-Ⅴ indicates the conservation priority, and Ⅴ indicates the highest conservation priority.
Figure 5. The priority level of biodiversity spatial conservation in Ili River Valley, Xinjiang
表 1 新疆伊犁河谷地区各生物类群科、属、种数量
Table 1. Number of families, genera and species of various biological groups in Ili River Valley, Xinjiang
生物类群
Biological group科
Family属
Genus种
Species维管植物
Vascular plants103 557 2078 苔藓
Mosses49 110 239 地衣
Lichens22 47 117 大型真菌
Macrofungi39 103 201 昆虫
Insects136 558 887 脊椎动物
Vertebrates96 252 423 合计
Total445 1627 3945 表 2 新疆伊犁河谷地区各县各生物类群物种数量
Table 2. Species quantity of various biological groups in each county of Ili River Valley, Xinjiang
县名
County维管植物
Vascular plants苔藓
Mosses地衣
Lichens大型真菌
Macrofungi昆虫
Insects脊椎动物
Vertebrates合计
Total伊宁县
Yining County1979 98 44 45 429 356 2951 霍城县
Huocheng County1989 77 34 31 322 284 2737 察布查尔县
Chapchal County1981 55 73 24 322 256 2711 昭苏县
Zhaosu County1897 77 67 94 312 254 2701 新源县
Xinyuan County1911 64 19 36 362 302 2694 巩留县
Gongliu County1917 61 12 94 312 269 2665 特克斯县
Tekes County1907 37 35 49 312 262 2602 尼勒克县
Nilka County1894 74 14 35 310 237 2564 表 3 新疆伊犁河谷地区各生物类群保护物种数量
Table 3. Number of protected species of various biological groups in Ili River Valley, Xinjiang
生物类群
Biological
group新疆重点保护物种
Key protected
species in
Xinjiang国家重点
保护物种
National key
protected species中国红色名录物种
Chinese red list speciesCITES物种
CITES species保护物种总数
Total number
of protected
speciesⅠ级
Grade ⅠⅡ级
Grade ⅡⅠ级
Grade ⅠⅡ级
Grade Ⅱ极危
CR濒危
EN易危
VU近危
NT附录Ⅰ
Appendix Ⅰ附录Ⅱ
Appendix Ⅱ附录Ⅲ
Appendix Ⅲ维管植物
Vascular plants23 17 0 30 1 9 19 49 0 33 0 153 苔藓
Mosses— — 0 0 0 0 1 1 — — — 2 地衣
Lichens— — — — 0 0 0 0 — — — 0 大型真菌
Macrofungi— — 0 0 0 0 0 0 — — — 0 昆虫
Insects— — 0 1 — — — — 0 1 0 1 脊椎动物
Vertebrates18 14 20 65 3 19 20 59 8 53 2 138 合计
Total41 31 20 96 4 28 40 109 8 87 2 294 注: “—”表示无相关数据信息。‘—’ indicates that no data is available. 表 4 新疆伊犁河谷地区各县各生物类群未被列为保护物种的百分比
Table 4. Percentage of various biological groups not listed as protected species in each county of Ili River Valley, Xinjiang
单位Unit:% 县名
County维管植物
Vascular plants苔藓
Mosses地衣
Lichens大型真菌
Macrofungi昆虫
Insects脊椎动物
Vertebrates合计
Total尼勒克县
Nilka County93.8 98.7 100.0 100.0 99.7 71.7 92.8 昭苏县
Zhaosu County93.9 100.0 100.0 100.0 100.0 68.5 92.7 特克斯县
Tekes County93.9 100.0 100.0 100.0 100.0 69.9 92.5 察布查尔县
Chapchal County93.1 100.0 100.0 100.0 100.0 73.4 92.4 巩留县
Gongliu County93.6 100.0 100.0 100.0 99.7 68.8 92.2 霍城县
Huocheng County93.1 100.0 100.0 100.0 99.7 72.2 92.0 新源县
Xinyuan County93.4 97.3 100.0 100.0 100.0 68.9 91.8 伊宁县
Yining County93.1 100.0 100.0 100.0 99.8 68.8 91.6 -
[1] 陈灵芝, 1993. 中国的生物多样性: 现状及其保护对策[M]. 北京: 科学出版社. [2] 陈忠升, 陈亚宁, 李卫红, 等, 2010. 基于生态服务价值的伊犁河谷土地利用变化环境影响评价[J]. 中国沙漠, 30(4): 870-877. [3] 高亚鸣, 孙慧兰, 2017. 基于土地分类利用下伊犁河谷地区的生态服务价值研究[J]. 生态科学, 36(1): 193-200. doi: 10.14108/j.cnki.1008-8873.2017.01.027 [4] 国家濒危物种科学委员会, (2019-12-12)[2022-03-09]. 2019年CITES附录中文版[EB/OL]. http://www.cites.org.cn/citesgy/fl/201911/t20191111_524091.html. [5] 国家林业和草原局, 农业农村部, (2021a-02-05)[2022-03-09]. 国家重点保护野生动物名录[EB/OL]. https://www.forestry.gov.cn/main/5461/20210205/122418860831352.html. [6] 国家林业和草原局, 农业农村部, (2021b-09-08)[2021-03-09]. 国家重点保护野生植物名录[EB/OL]. https://www.forestry.gov.cn/main/3954/20210908/163949170374051.html. [7] 环境保护部, 中国科学院, (2013-09-02)[2022-03-28]. 关于发布《中国生物多样性红色名录——高等植物卷》的公告[EB/OL]. https://www.mee.gov.cn/gkml/hbb/bgg/201309/t20130912_260061.htm. [8] 环境保护部, 中国科学院, (2015-05-21)[2022-03-28]. 关于发布《中国生物多样性红色名录——脊椎动物卷》的公告[EB/OL]. https://www.mee.gov.cn/gkml/hbb/bgg/201505/t20150525_302233.htm. [9] 李迪强, 宋延龄, 2000. 热点地区与GAP分析研究进展[J]. 生物多样性, 8(2): 208-214. doi: 10.3321/j.issn:1005-0094.2000.02.010 [10] 李利平, 尹林克, 唐志尧, 2011. 新疆野生动植物物种丰富度的分布格局[J]. 干旱区研究, 28(1): 1-9. doi: 10.13866/j.azr.2011.01.001 [11] 李骁, 吴纪华, 李博, 2019. 为生物多样性与人类未来而战[J]. 科学通报, 64(23): 2374-2378. doi: 10.1360/N972019-00283 [12] 栾福明, 王芳, 熊黑钢, 2017. 伊犁河谷文化遗址时空分布及地理背景研究[J]. 干旱区地理, 40(1): 211-221. doi: 10.13826/j.cnki.cn65-1103/x.2017.01.027 [13] 马克平, 2015. 中国生物多样性编目取得重要进展[J]. 生物多样性, 23(2): 137-138. doi: 10.17520/biods.2015077 [14] 沈泽昊, 张志明, 胡金明, 等, 2016. 西南干旱河谷植物多样性资源的保护与利用[J]. 生物多样性, 24(4): 475-488. doi: 10.17520/biods.2016022 [15] 生态环境部, 中国科学院, (2018-05-17)[2022-03-28]. 关于发布《中国生物多样性红色名录——大型真菌卷》的公告[EB/OL]. https://www.mee.gov.cn/xxgk2018/xxgk/xxgk01/201805/t20180524_629586.html. [16] 唐明龙, 2005. 伊犁河谷林木种质资源的保护与开发利用[J]. 新疆林业, (4): 40-41. doi: 10.3969/j.issn.1005-3522.2005.04.030 [17] 汪洋, 靳瑰丽, 李卫红, 等, 2017. 伊犁河谷土地利用变化对生态服务价值的影响[J]. 环境与可持续发展, 42(2): 151-155. doi: 10.3969/j.issn.1673-288X.2017.02.047 [18] 王荷生, 1997. 华北植物区系地理[M]. 北京: 科学出版社. [19] 肖文发, 阿力木江·牙生, 钱法文, 等, 2015. 新疆西天山国家级自然保护区生物多样性与自然保护管理[M]. 北京: 中国林业出版社. [20] 新疆维吾尔自治区人民政府办公厅, (2007-08-29)[2022-03-24]. 关于发布新疆维吾尔自治区重点保护野生植物名录(第一批)的通知[EB/OL]. http://www.xinjiang.gov.cn/xinjiang/gfxwj/200708/b5862cfc838a4c4aac5220337d19c2a0.shtml. [21] 新疆维吾尔自治区生态环境厅, (2011-10-21)[2022-03-24]. 新疆生物多样性现状与总体评价[EB/OL]. http://sthjt.xinjiang.gov.cn/xjepd/zrstswdyx/201110/554d26de77504cd19b7ac61e4691dfd9.shtml. [22] 新疆植物志编辑委员会, 1992—2011. 新疆植物志: 第1-6卷[M]. 乌鲁木齐: 新疆科技卫生出版社. [23] 熊嘉武, 2017. 新疆天山西部山地综合科学考察[M]. 北京: 中国林业出版社. [24] 徐远杰, 陈亚宁, 李卫红, 等, 2010. 中国伊犁河谷种子植物区系分析[J]. 干旱区研究, 27(3): 331-337. doi: 10.13866/j.azr.2010.03.002 [25] 颜瑜严, 杨辽, 王伟胜, 等, 2020. 伊犁河谷景观生态风险时空变化及其地形梯度分析[J]. 生态科学, 39(4): 125-136. doi: 10.14108/j.cnki.1008-8873.2020.04.017 [26] 于非, 王晗, 王绍坤, 等, 2012. 阿波罗绢蝶种群数量和垂直分布变化及其对气候变暖的响应[J]. 生态学报, 32(19): 6203-6209. doi: 10.5846/stxb201107281107 [27] 竹效民, 2017. 伊犁河谷生态文明建设基本发展思路[J]. 中共伊犁州委党校学报, (1): 39-46. doi: 10.3969/j.issn.1674-6287.2017.01.10 [28] Butchart S H M, Walpole M, Collen B, et al, 2010. Global biodiversity: indicators of recent declines[J]. Science, 328(5982): 1164-1168. doi: 10.1126/science.1187512 [29] Ceballos G, Ehrlich P R, Barnosky A D, et al, 2015. Accelerated modern human-induced species losses: entering the sixth mass extinction[J]. Science Advances, 1(5): e1400253. doi: 10.1126/sciadv.1400253 [30] Clark W C, Richards J, Flint E, 1986. Human transformations of the earth's vegetation cover: past and future impacts of agricultural development and climatic change[C]//Climatic-Vegetation Interactions. Proceedings of a workshop held at NASA/Goddard Space Flight Center. Greenbelt, MD, 27(29): 54-59. [31] Dobson A P, Rodriguez J P, Roberts W M, et al, 1997. Geographic distribution of endangered species in the United States[J]. Science, 275(5299): 550-553. doi: 10.1126/science.275.5299.550 [32] Gaston K J, 2000. Global patterns in biodiversity[J]. Nature, 405(6783): 220-227. doi: 10.1038/35012228 [33] Gillson L, Willis K J, 2004. 'As Earth's testimonies tell': wilderness conservation in a changing world[J]. Ecology Letters, 7(10): 990-998. doi: 10.1111/j.1461-0248.2004.00658.x [34] Mace G M, Barrett M, Burgess N D, et al, 2018. Aiming higher to bend the curve of biodiversity loss[J]. Nature Sustainability, 1(9): 448-451. doi: 10.1038/s41893-018-0130-0 [35] Margules C R, Nicholls A O, Pressey R L, 1988. Selecting networks of reserves to maximise biological diversity[J]. Biological Conservation, 43(1): 63-76. doi: 10.1016/0006-3207(88)90078-X [36] Mi X C, Feng G, Hu Y B, et al, 2021. The global significance of biodiversity science in China: an overview[J]. National Science Review, 8(7): nwab32. doi: 10.1093/nsr/nwab032 [37] Nielsen K S, Marteau T M, Bauer J M, et al, 2021. Biodiversity conservation as a promising frontier for behavioural science[J]. Nature Human Behaviour, 5(5): 550-556. doi: 10.1038/s41562-021-01109-5 [38] Noss R F, Cooperrider A, 1994. Saving nature's legacy: protecting and restoring biodiversity[M]. Washington DC: Island Press. [39] Prendergast J R, Quinn R M, Lawton J H, et al, 1993. Rare species, the coincidence of diversity hotspots and conservation strategies[J]. Nature, 365(6444): 335-337. doi: 10.1038/365335a0 [40] Scott J M, Davis F, Csuti B, et al, 1993. Gap analysis: a geographic approach to protection of biological diversity[J]. Wildlife Monographs, (123): 3-41. [41] Whittaker R J, Araújo M B, Jepson P, et al, 2005. Conservation Biogeography: assessment and prospect[J]. Diversity and Distributions, 11(1): 3-23. doi: 10.1111/j.1366-9516.2005.00143.x [42] Wilson E O, 2016. Half-earth: our planet's fight for life[M]. New York: Liveright Publishing Corporation. [43] Yang W J, Ma K P, Kreft H, 2014. Environmental and socio-economic factors shaping the geography of floristic collections in China[J]. Global Ecology and Biogeography, 23(11): 1284-1292. doi: 10.1111/geb.12225 -