Reserve gap analysis of endangered brown eared pheasant (Crossoptilon mantchuricum) through GIS and MaxEnt technology.
-
摘要: 自然保护区网络的设计对濒危物种及其生境的保护至关重要。地理信息系统(GIS)和MaxEnt模型作为一种有效而可靠的工具已广泛应用在野生动物的管理和自然保护区设计中。褐马鸡是中国特有的濒危雉类,当前存在3个分隔的地理种群。由当前已知分布点,采用最小凸多边形法(MCP)分别划定3个分布区,并设计分布区外20 km的缓冲距离为研究区域。在研究区内,针对褐马鸡及其生境的保护已建立8个国家级和8个省级自然保护区网络。根据褐马鸡栖息地特征选择11个生境因子为预测背景,基于45个当前分布点利用MaxEnt模型预测褐马鸡当前的潜在适宜生境。由MaxEnt模型检验可知,训练集和测试集的平均遗漏率(OR)分别0.10和<0.35。训练集和测试集的AUC 均值分别为0.957 5和0.898 5,AUC标准偏差为0.040 6,模型预测精确度较高。在GIS10.0软件中,由所选的10%TPLT阈值(0.30)将预测概率图转化为Presence/Absence二值图,并分析当前自然保护区对适宜生境的保护状况。研究发现当前自然保护区存在一定的保护空缺,有18 896 km2适宜生境未受保护;省级自然保护区在适宜生境保护中起到关键的连接作用,在保持褐马鸡适宜生境的完整性和连通性中不可或缺。建议相关保护部门明确省级自然保护区的边界,制定可供GIS分析的省级自然保护区的数字图层,为今后自然保护区网络的规划和设计提供技术支撑。Abstract: The nature reserve design and networks are all important for wildlife and habitat conservation. Geographical information system (GIS) and MaxEnt model are efficient and most reliable tool in setting habitat conservation priorities for nature specially endangered species. Brown eared pheasant is an endangered mountain pheasant endemic in China. Presently, the brown eared pheasant has three isolated populations,which were the western population in Shaanxi Province, the central population in Shanxi Province, and the eastern population in Hebei Province and Beijing. The current distribution area of three populations of brown eared pheasant were delimited by the minimum convex polygon method (MCP) base on current distribution points, and set the 20 km buffer distance outside the distribution region as the study area. Eight national nature reserves and eight provincial nature reserves were instituted for protecting brown eared pheasant and its habitat in the study area. MaxEnt model was used to obtain the current potential suitable habitat base on 11 environmental variables and 45 current distributing sites. All of the training OR was 0.10, and all of the test OR was 0.35. The AUC results revealed a training average AUC of 0.957 5, test average AUC of 0.898 5, and AUC standard deviation of 0.040 6, indicative of good model prediction performance. 10th percentile training presence logistic threshold (0.30) was used to divide the Presence/Absence map. Then we analyzed the protection condition of reserves for suitable habitat in the GIS10.0 software. The suitable habitat of 18 896 km2 located outside the reserves, which should be considered for protection. The provincial nature reserves play the crucial link roles, and to keep the integrity and continuity of the suitable habitat for brown eared pheasant is important. Local conservation departments should confirm reserve boundary and set GIS analysis layer of provincial nature reserves for reserves network planning and design to provide technical support in the future.
-
Keywords:
- provincial nature reserve /
- brown eared pheasant /
- GIS /
- MaxEnt model
-
-
[1] [1] IUCN (World Conservation Union). The IUCN red list of threatened species[R/OL]. (2015-04) [2016-02-22]. http:∥www.iucnredlist.org.
[2] ZHANG Z W, ZHANG G G, SONG J. The population status and conservation strategy of Brown eared-pheasant[C]∥China Ornithological Society. Studies on Chinese ornithology: proceedings of the 4th ornithological symposium of mainland Taiwan, China. Beijing: China Forestry Publishing House, 2000: 49-55.
[2] JOHNSGARD P A. The pheasants of the World[M]. Washington D C: Smithsonian Institution Press, 1999.
[3] 张正旺, 张国刚, 宋杰. 褐马鸡的种群现状和保护对策[C]∥中国鸟类学会. 中国鸟类学研究:第四届海峡两岸鸟类学术研讨会. 北京:中国林业出版社, 2000: 49-55. [3] JIANG Z G, GE S.Exploring the mechanism of species endangerment and conservation strategy in the Yangtze River drainage[J]. Biodiversity Science, 2005, 13(5): 367-375.
[4] ZUO W Y, LAO N,GENG Y Y, et al. Predicting species potential distribution, SVM compared with GARP[J]. Journal of Plant Ecology (Chinese Version), 2007,31(4): 711-719.
[4] SEKERCIOGLU C H, SCHNEIDER S H, FAY J P, et al. Climate change, elevational range shifts, and bird extinctions[J]. Conservation biology, 2008, 22(1): 140-150.
[5] ZHANG C A, DING C Q. The site record database for Chinese galliformes and its application[J]. Chinese Journal of Zoology, 2007, 42(3):72-78.
[5] 蒋志刚, 葛颂. 探索长江流域物种濒危机制与保护对策[J]. 生物多样性, 2005, 13(5):367-375. [6] BROWN J H, LOMOLINO M V. Biogeography (2nd edn.)[M]. Sunderland: Sinauer Associates, 1998.
[6] ZHANG Z W. Brown eared pheasant(Crossoptilon mantchuricum) [M]∥ZHENG G M. Pheasants in China. Beijing: Higher Education Press, 2015.
[7] 左闻韵, 劳逆, 耿玉英, 等. 预测物种潜在分布区:比较SVM与GARP[J]. 植物生态学报, 2007, 31(4):711-719. [7] WANG G D, FENG S, LI J Q, et al. The study of move range and dispersal behavior for the Brown eared pheasant[C]∥China Zoological Society. Proceedings of the 3th national academic symposium on wildlife ecology and resource Protection. Beijing: Institute of Zoology, 2006: 13.
[8] ELITH J, GRAHAM C H, ANDERSON R P, et al. Novel methods improve prediction of species distributions from occurrence data[J]. Ecography, 2006, 29(2): 129-151.
[8] LIU H J, SU H L, REN J Q. The China phasianids, brown eared pheasant[M]. Beijing: China Forestry Publishing House, 1991.
[9] ZHAO Z J. A handbook of the birds of China(VolumeⅠ)[M]. Jilin: Jilin Science and Technology Press, 2001.
[9] PETERSON A T. Projected climate change effects on Rocky Mountain and Great Plains birds: generalities of biodiversity consequences[J]. Global Change Biology, 2003, 9(5):647-655.
[10] ZHANG G G, ZHANG Z W, YANG F Y, et al. Habitat selection of brown-eared pheasant at the Wulushan National Nature Reserve of Shanxi, China[J]. Scientia silvae sinicae, 2010, 46(11): 100-103.
[10] QUAN J, OUYANG Z, XU W, et al. Assessment of the effectiveness of nature reserve management in China[J]. Biodiversity and Conservation, 2011, 20(4): 779-792.
[11] JIA N F, DUAN J N, QIAO Z M. Analysis method of spatial distribution of land use in relation to topography[J]. Economic Geography, 2007, 27(2):310-312.
[11] 张成安, 丁长青. 中国鸡形目鸟类分布数据库及其应用[J]. 动物学杂志, 2007, 42(3):73-78. [12] 张正旺. 褐马鸡Crossoptilon mantchuricum[M]∥郑光美主编. 中国雉类. 北京: 高等教育出版社, 2015. [12] XU Z L, PENG H H, PENG S Z. The development and evaluation of species distribution models[J]. Acta Ecologica Sinica, 2015, 35(2): 557-567.
[13] Ministry of Environmental Protection of the People's Republic of China, Data Center. Nature reserve database[DB]. http:∥datacenter.mep.gov.cn.2016.
[13] 王国栋, 冯松, 李建强, 等. 褐马鸡的活动区与扩散行为研究[C]∥中国动物学会. 野生动物生态与资源保护第三届全国学术研讨会论文摘要集. 北京: 中国科学院动物研究所, 2006: 13. [14] PHILLIPS S J. Transferability, sample selection bias and background data in presence-only modelling: a response to Peterson et al.[J]. Ecography, 2008, 31(2): 272-278.
[14] GUO Z L, LI X Y, CUI G F. Construction methods of nature reserve system: research progress[J]. Chinese Journal of Ecology, 2013, 32(8): 2220-2228.
[15] PHILLIPS S J, DUDIK M, ELITH J, et al. Sample selection bias and presence-only distribution models: implications for background and pseudo-absence data[J]. Ecological Applications, 2009, 19(1): 181-197.
[15] Ministry of Environmental Protection of the People’s Republic of China, Department of Nature and Ecology Conservation. The list of nature reserves, 2012[R/OL]. http:∥sts.mep.gov.cn/zrbhq/.2016.
[16] CHEN Y M. Nature reserve ecosystem service evaluation system and case study[M]. Beijing: Science Press, 2014.
[16] 刘焕金, 苏化龙, 任建强. 中国雉类-褐马鸡[M]. 北京: 中国林业出版社, 1991. [17] 赵正阶. 中国鸟类志(上卷)[M]. 吉林: 吉林科学技术出版社, 2001. [18] LI H Q, LIAN Z M, CHEN C G. Winter foraging habitat selection of brown-eared pheasant (Crossoptilon mantchuricum) and the common pheasant (Phasianus colchicus) in Huanglong Mountains, Shaanxi Province[J]. Acta Ecologica Sinica, 2009, 29(6): 335-340.
[19] 张国钢, 张正旺, 杨凤英, 等. 山西五鹿山自然保护区褐马鸡栖息地的选择[J]. 林业科学, 2010, 46(11):100-103. [20] 贾宁凤, 段建南, 乔志敏. 土地利用空间分布与地形因子相关性分析方法[J]. 经济地理, 2007, 27(2): 310-312. [21] PHILLIPS S J, ANDERSON R P, SCHAPIRE R E. Maximum entropy modeling of species geographic distribution[J]. Ecological Modelling, 2006, 190(3): 231-259.
[22] RAES N, TER STEEGE H. A null-model for significance testing of presence-only species distribution models[J]. Ecography, 2007, 30(5): 727-736.
[23] 许仲林, 彭焕华, 彭守璋. 物种分布模型的发展及评价方法[J]. 生态学报, 2015, 35(2): 557-567. [24] FIELDING A H, BELL J F. A review of methods for the assessment of prediction errors in conservation presence/absence models[J]. Environmental Conservation, 1997, 24(1): 38-49.
[25] SWETS J A. Measuring the accuracy of diagnostic systems[J]. Science, 1988, 240:1285-1293..
[26] PEARSON R G, RAXWORTHY C J, NAKAMURS M, et al. Predicting species distributions from small numbers of occurrence records: a test case using cryptic geckos in Madagascar[J]. Journal of Biogeography, 2007, 34(1): 102-117.
[27] 中华人民共和国环境保护部数据中心. 自然保护区数据库.[DB]. http:∥datacenter.mep.gov.cn. 2016. [28] 郭子良, 李霄宇, 崔国发. 自然保护区体系构建方法研究进展[J]. 生态学杂志, 2013, 32(8):2220-2228. [29] JOSHUA G. Global conservation priorities[J]. Conservation Biology, 1999, 13(1):5.
[30] MOCHIZUKI S, LIU D P, SEKIJIMA T, et al. Detecting the nesting suitability of the re-introduced Crested Ibis Nipponia nippon for nature restoration program in Japan[J]. Journal for Nature Conservation, 2015, 28:45-55.
[31] PRESSEY R L. Ad hoc reservations: forward or backward steps in developing representative reserve systems?[J]. Conservation Biology, 2002, 8(3): 662-668.
[32] 环境保护部自然生态保护司. 全国自然保护区名录, 2012版[R/OL]. http:∥sts.mep.gov.cn/zrbhq/.2016. [33] 陈艳梅.自然保护区生态系统服务评估体系及案例研究[M]. 北京: 科学出版社, 2014. [34] MCGOWAN P J K, GARSON P J. Pheasants: status survey and conservation action plan 1995—1999[M]. Switzerland: World Conservaion Union, 1995.
[35] HOCKINGS M. Evaluating protected area management-a review of system for assessing management effectiveness of protected areas[M]. Brisbane: University of Queensland, 2000.
[36] PRENDERGAST J R, QUINN R M, LAWTON J H. The gaps between theory and practice in selecting nature reserves[J]. Conservation Biology, 1999, 13(3): 484-492.
-
期刊类型引用(19)
1. 何兰君,李林霞,欧光龙. 基于标志种分布预测的哀牢山植被潜在分布及气候解释研究. 西南林业大学学报(自然科学). 2024(03): 52-60 . 百度学术
2. 田刘翔宇,张立世,姚纪元,王利民. 基于MaxEnt探究栖息地质量对百灵科鸟类分布影响. 东北师大学报(自然科学版). 2024(02): 106-116 . 百度学术
3. 章蜜,罗伟. 庐山保护区白颈长尾雉生境适宜性评价研究. 湖北林业科技. 2024(05): 44-48 . 百度学术
4. 王佩,李英杰,袁家根,耿盼,李蕊. 基于优化MaxEnt模型的原麝生境适宜性评价. 野生动物学报. 2023(01): 38-45 . 百度学术
5. 富爱华,郜二虎,布日古德,陈敏豪,提杨,栾晓峰. 我国白琵鹭(Platalea leucorodia)越冬地预测与保护现状分析. 生态与农村环境学报. 2022(01): 69-75 . 百度学术
6. 吴艳,王洪峰,穆立蔷. 物种分布模型的研究进展与展望. 高师理科学刊. 2022(05): 66-70 . 百度学术
7. 李鑫泽,冯佳楠,支晓亮,钟林强,刘鑫鑫,张明海. 东北地区三种鹿科动物潜在栖息地预测与保护空缺分析. 野生动物学报. 2021(02): 318-328 . 百度学术
8. 王艳君,高泰,石娟. 基于MaxEnt模型对舞毒蛾全球适生区的预测及分析. 北京林业大学学报. 2021(09): 59-69 . 本站查看
9. 张丽霞,孙冬婷,胡昕,朱向博,张敬,晁青鲜,卫泽珍,张成林. 中国圈养褐马鸡种群和饲养管理现状调查. 野生动物学报. 2021(04): 1123-1130 . 百度学术
10. 李宏群,韩培士,牛常会,袁晓青,邢立刚. 气候变化对我国特有濒危动物褐马鸡潜在生境的影响. 林业科学. 2021(10): 102-110 . 百度学术
11. 刘博,王晔楠,唐超,刘丽,马光昌,彭正强,阎伟. 云斑斜线天蛾在我国的适生性及限制性环境因子分析. 热带作物学报. 2021(12): 3581-3587 . 百度学术
12. 李敏,李秀明,徐家慧,薛琳,武爱明,盘凯筠,闵晓明,李玉太,钱法文. 基于MaxEnt模型预测白琵鹭在中国东北地区的适宜分布区. 生态学杂志. 2020(08): 2691-2703 . 百度学术
13. 张丽霞,王志永. 褐马鸡栖息地保护研究. 特种经济动植物. 2020(12): 3-5 . 百度学术
14. 唐书培,穆丽光,王晓玲,张静,刘波,孟和达来,鲍伟东. 基于MaxEnt模型的赛罕乌拉国家级自然保护区斑羚生境适宜性评价. 北京林业大学学报. 2019(01): 102-108 . 本站查看
15. 吕汝丹,何健,刘慧杰,姚敏,程瑾,谢磊. 羽叶铁线莲的分布区与生态位模型分析. 北京林业大学学报. 2019(02): 70-79 . 本站查看
16. 白雪红,王文杰,蒋卫国,师华定,陈坤,陈民. 气候变化背景下京津冀地区濒危水鸟潜在适宜区模拟及保护空缺分析. 环境科学研究. 2019(06): 1001-1011 . 百度学术
17. 刘博,覃伟权,阎伟. 基于MaxEnt模型的小巢粉虱在中国的潜在地理分布. 环境昆虫学报. 2019(06): 1276-1286 . 百度学术
18. 王浩,杨德宏,满亚洲. 基于GIS技术的动物物种管理及保护. 软件. 2018(12): 111-115 . 百度学术
19. 侯海英. 山西褐马鸡种群分布及特性研究. 山西林业科技. 2018(04): 11-13+72 . 百度学术
其他类型引用(17)
计量
- 文章访问数: 2727
- HTML全文浏览量: 398
- PDF下载量: 75
- 被引次数: 36