Range-wide analysis of wildlife habitat: Implications for conservation

被引:67
作者
Vina, Andres [1 ]
Tuanmu, Mao-Ning [1 ]
Xu, Weihua [2 ]
Li, Yu [1 ]
Ouyang, Zhiyun [2 ]
DeFries, Ruth [3 ]
Liu, Jianguo [1 ]
机构
[1] Michigan State Univ, Ctr Syst Integrat & Sustainabil, Dept Fisheries & Wildlife, E Lansing, MI 48823 USA
[2] Chinese Acad Sci, Ecoenvironm Sci Res Ctr, State Key Lab Urban & Reg Ecol, Beijing, Peoples R China
[3] Columbia Univ, Dept Ecol Evolut & Environm Biol E3B, New York, NY 10027 USA
基金
美国国家科学基金会; 美国国家航空航天局; 中国国家自然科学基金;
关键词
Giant panda; Habitat modeling; MODIS; Nature reserve; Range-wide analysis; WOLONG NATURE-RESERVE; GIANT PANDAS; SPECIES DISTRIBUTIONS; UNDERSTOREY BAMBOO; VEGETATION INDEX; MODIS DATA; CHINA; MOUNTAINS; SELECTION; CLASSIFICATION;
D O I
10.1016/j.biocon.2010.04.046
中图分类号
X176 [生物多样性保护];
学科分类号
090705 ;
摘要
The range-wide habitat status of many endangered species is unclear. We evaluated the status and spatial distribution of the habitat of the endangered giant panda (Ailuropoda melanoleuca) across its entire geographic range (i.e., six mountain regions located in Sichuan. Shaanxi and Gansu provinces, China) by integrating field and remotely sensed data to develop a habitat distribution model. Results suggest that current suitable habitat corresponds to ca. 1/4 of the habitat baseline (i.e., maximum amount of habitat possible). The highest proportion of suitable habitat relative to the baseline is in the Qinling mountain region. Overall, around 40% of the suitable habitat is inside nature reserves, but the proportion of habitat inside them varied among different mountain regions, ranging from ca. 17% (Lesser Xiangling) to ca. 66% (Qinling). The habitat model also predicted the occurrence of potentially suitable habitat outside the currently accepted geographic range of the species, which should be further evaluated as potential panda reintroduction sites. Our approach is valuable for assessing the conservation status of the entire habitat of the species, for identifying areas with significant ecological roles (e.g., corridors), for identifying areas suitable for panda reintroductions, and for establishing specific conservation strategies in different parts of the giant panda geographic range. It might also prove useful for range-wide habitat analyses of many other endangered species around the world. (C) 2010 Elsevier Ltd. All rights reserved.
引用
收藏
页码:1960 / 1969
页数:10
相关论文
共 78 条
  • [1] Characterizing tropical forest spatio-temporal heterogeneity using the Wide Dynamic Range Vegetation Index (WDRVI)
    Aguilar-Amuchastegui, N.
    Henebry, G. M.
    [J]. INTERNATIONAL JOURNAL OF REMOTE SENSING, 2008, 29 (24) : 7285 - 7291
  • [2] Monitoring sustainability in tropical forests: How changes in canopy, spatial pattern, can indicate forest stands for biodiversity surveys
    Aguilar-Amuchastegui, Naikoa
    Henebry, Geoffrey M.
    [J]. IEEE GEOSCIENCE AND REMOTE SENSING LETTERS, 2006, 3 (03) : 329 - 333
  • [3] [Anonymous], [No title captured]
  • [4] [Anonymous], GAP ANAL PROGRAM B
  • [5] Validation of species-climate impact models under climate change
    Araújo, MB
    Pearson, RG
    Thuiller, W
    Erhard, M
    [J]. GLOBAL CHANGE BIOLOGY, 2005, 11 (09) : 1504 - 1513
  • [6] Displaying remotely sensed vegetation dynamics along natural gradients for ecological studies
    Beck, P. S. A.
    Wang, T. J.
    Skidmore, A. K.
    Liu, X. H.
    [J]. INTERNATIONAL JOURNAL OF REMOTE SENSING, 2008, 29 (14) : 4277 - 4283
  • [7] Do habitat corridors provide connectivity?
    Beier, P
    Noss, RF
    [J]. CONSERVATION BIOLOGY, 1998, 12 (06) : 1241 - 1252
  • [8] BENEDETTI R, 1994, INT J REMOTE SENS, V15, P583, DOI 10.1080/01431169408954098
  • [9] Near-global validation of the SRTM DEM using satellite radar altimetry
    Berry, P. A. M.
    Garlick, J. D.
    Smith, R. G.
    [J]. REMOTE SENSING OF ENVIRONMENT, 2007, 106 (01) : 17 - 27
  • [10] Evaluating resource selection functions
    Boyce, MS
    Vernier, PR
    Nielsen, SE
    Schmiegelow, FKA
    [J]. ECOLOGICAL MODELLING, 2002, 157 (2-3) : 281 - 300