期刊文献+

地形因素对羚牛家域估算的影响分析——以固定核域法与最小凸边形法为例 被引量:2

Analysis of terrain induced impact on Takin(Budorcas taxicolor) home range estimation:an example from Fixed kernel estimator and Minimum convex polygon
下载PDF
导出
摘要 家域特征对物种基础生物学的认识和提出相关管理及保护对策有重要作用。本研究利用地理信息系统相关软件,以4只(2♀、2♂)佩戴GPS无线电颈圈的四川羚牛定位数据使用固定核域法(FKE)和最小凸多边形法(MEP)对春季(2007年和2008年)家域特征进行了估算,显示地形因素对家域估算结果影响显著,表面家域(FKE95%=7.50±2.27,MCP=7.01±1.99)要显著大于平面家域(FKE95%=5.94±1.54,t=3.31,df=3,P=0.045,MCP=5.47±1.52,df=3,t=3.43,P=0.041)。其次,固定核域法(95%)与最小凸多边形法所获得的平面家域(t=0.718,df=3,P=0.524)和表面家域(t=0.612,df=3,P=0.584)差异不显著。个体间家域差异显著(df=3,F=7.226,P=0.001),组间两两比较显示,M1与F1(P=0.001)、F2(P=0.031)、M2(P=0.02),F1与F2(P=0.044)间的家域均有显著差异,而M2与F2(P=0.221)、M2与F1(P=0.598)间差异不显著。两种家域估算方法对计算羚牛的家域重叠程度没有明显优劣之分(95%KernelVS100%MCP),但不同密度的核域可能得出不同的甚至是完全相反的结论,因此在选择核域密度时应尽量同时参照其他数据和其他估算方法。 Knowledge of the home range of wildlife is the basis of effective conservation and management.We studied takin(Budorcas taxicolor tibetana) home range in spring with two widely applied methods using GIS related software,where we compared differences between the home range estimates with and without terrain information.All four takin(2♀2♂) were fixed with GPS radio collars and the data were obtained in the spring of 2007 and of 2008.The results showed home range size derived with terrain information(FKE95%=7.50±2.27,MCP=7.01±1.99) was significantly larger than that derived without topographic information(FKE95%=5.94±1.54,t=3.31,df=3,P=0.045,MCP=5.47±1.52,df=3,t=3.34,P=0.041).The difference between estimates based on 95% Fixed kernel home range and Minimum convex polygon home range were not significant regardless of including terrain information(t=0.612,df=3,P=0.584) or not(t=0.718,df=3,P=0.524).However,we also found significant differences of home range size between individuals(One way ANOVA,df=3,F=7.226,P=0.001).The post hoc test between individuals found significant differences between M1 and F1(P=0.001),M1 and F2(P=0.031),M1 and M2(P=0.02),F1 and F2(P=0.044),whereas no significant difference was detected between M2 and F2(P=0.221),M2 and F1(P=0.598).We also tested the difference of the two methods on the results of spatial overlap between individuals,but no significant difference was detected.Researchers should select appropriate smooth parameters(h)/bandwidth,because different bandwidth may derive different conclusions of the degree of home range overlap,or even contradictory results.
出处 《兽类学报》 CAS CSCD 北大核心 2012年第2期110-117,共8页 Acta Theriologica Sinica
基金 中国科学院创新工程重要方向性项目(KSCX2-YW-Z0959)
关键词 羚牛 无线电颈圈 GPS GIS GIS GPS Radio collar Takin(Budorcas taxicolor tibetana)
  • 相关文献

参考文献10

二级参考文献73

共引文献162

同被引文献47

  • 1葛桃安,胡锦矗,江明道,邓启涛.唐家河自然保护区扭角羚的兽群结构及数量分布[J].兽类学报,1989,9(4):262-268. 被引量:23
  • 2胡锦矗,周材权,魏辅文,等.2007.哺乳动物学[M].深圳:中国教育文化出版社:199-200.
  • 3汪松,解焱.中国物种红色名录[M].北京:高等教育出版社.2009.
  • 4IUCN.The IUCN Red List of Threatened Species[DB/OL].http://www.iucnredlist.org/details/3160/0,2014.12.
  • 5Neas,J.F.,Hoffmann,R.S..Budorcas taxicolor[J].Mammalian Species,1987(277):1-7.
  • 6Groves P,Shields G F.Cytochrome B Sequences Suggest Convergent Evolution of the Asian Takin and Arctic Muskox[J].Molecular Phylogenetics and Evolution,1997,8(3):363-374.
  • 7葛宝明.羚牛行为时间分配、集群、家域、监测评价和地震对羚牛的影响[D].北京:中国科学院研究生院,2010.
  • 8邓其祥.天全县蜂子河羚牛生态调查[J].动物学杂志,1984,19(6):30-33.
  • 9胡锦矗,王酉之.四川资源动物调查(第二卷兽类)[M].成都:四川科学技术出版社,1984.
  • 10宋延龄,曾治高.秦岭羚牛的生存现状及其面临的问题[J].生物多样性(香港),2001(2):94-100.

引证文献2

二级引证文献1

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部