生物多样性 ›› 2018, Vol. 26 ›› Issue (11): 1180-1189. DOI: 10.17520/biods.2018167
和梅香1, 陈俪心1, 罗概1, 古晓东2, 王戈3, 冉江洪1,*()
收稿日期:
2018-06-13
接受日期:
2018-09-03
出版日期:
2018-11-20
发布日期:
2019-01-08
通讯作者:
冉江洪
作者简介:
# 共同第一作者
基金资助:
Meixiang He1, Lixin Chen1, Gai Luo1, Xiaodong Gu2, Ge Wang3, Jianghong Ran1,*()
Received:
2018-06-13
Accepted:
2018-09-03
Online:
2018-11-20
Published:
2019-01-08
Contact:
Ran Jianghong
About author:
# Co-first authors
摘要:
研究同域物种的分布格局及重叠状况对物种的区域整合保护管理及区域生物多样性保护具有重要实践价值。本研究基于全国第四次大熊猫调查及长期野外调查数据, 利用MaxEnt模型预测了凉山山系两种同域分布的熊科动物——大熊猫(Ailuropoda melanoleuca)和黑熊(Ursus thibetanus)的适宜生境, 基于适宜生境预测结果, 分析了两个物种的生境需求因子、生境破碎化现状及重叠状况。结果显示: (1)大熊猫和黑熊的适宜生境分布格局相似, 主要分布在凉山山系的山脊地带, 适宜生境面积分别为1,383.84 km2和2,411.49 km2; (2)两个物种的适宜生境都较为破碎, 且存在一些隔离分布区, 相较而言, 黑熊适宜生境的连通性要优于大熊猫; (3)两个物种生态位重叠度较高(D = 0.654, I = 0.901), 适宜生境重叠面积为958.29 km2, 分别占大熊猫和黑熊适宜生境总面积的69.25%和39.74%; (4)两个物种对环境因子的选择和响应表现出了相似性和差异性。相似性在于对两个物种生境分布影响最大的两个因子均为距居民点距离和海拔; 差异性在于对大熊猫生境分布影响次之的因子是植被类型和最冷季均温, 而黑熊的是年最大EVI指数和距道路距离。为了更有效地保护两个物种, 应加强对人类干扰的控制和植被的恢复, 对栖息地实行连通管理, 并建立多物种保护规划。
和梅香, 陈俪心, 罗概, 古晓东, 王戈, 冉江洪 (2018) 凉山山系大熊猫和黑熊适宜生境预测及重叠分析. 生物多样性, 26, 1180-1189. DOI: 10.17520/biods.2018167.
Meixiang He, Lixin Chen, Gai Luo, Xiaodong Gu, Ge Wang, Jianghong Ran (2018) Suitable habitat prediction and overlap analysis of two sympatric species, giant panda (Ailuropoda melanoleuca) and Asiatic black bear (Ursus thibetanus) in Liangshan Mountains. Biodiversity Science, 26, 1180-1189. DOI: 10.17520/biods.2018167.
景观指数 Landscape pattern index | 大熊猫 Ailuropoda melanoleuca | 黑熊 Ursus thibetanus |
---|---|---|
斑块数目 Number of patches (NP) | 5,340 | 5,983 |
斑块密度 Patch density (PD, ind./km2) | 0.340 | 0.381 |
平均斑块面积 Mean patch size (MPS, km2) | 0.26 | 0.40 |
最大斑块面积 Largest patch size (LPS, km2) | 339.535 | 1,115.759 |
最大斑块指数 Largest patch index (LPI, %) | 2.160 | 7.097 |
斑块结合度指数 Patch cohesion index (COHESION) | 99.506 | 99.822 |
分割指数 Segmentation index (DIVISION) | 0.999 | 0.994 |
分离度指数 Separation index (SPLIT) | 1,552.672 | 166.004 |
表1 大熊猫和黑熊的适宜生境景观指数
Table 1 Landscape pattern indices of suitable habitat for Ailuropoda melanoleuca and Ursus thibetanus
景观指数 Landscape pattern index | 大熊猫 Ailuropoda melanoleuca | 黑熊 Ursus thibetanus |
---|---|---|
斑块数目 Number of patches (NP) | 5,340 | 5,983 |
斑块密度 Patch density (PD, ind./km2) | 0.340 | 0.381 |
平均斑块面积 Mean patch size (MPS, km2) | 0.26 | 0.40 |
最大斑块面积 Largest patch size (LPS, km2) | 339.535 | 1,115.759 |
最大斑块指数 Largest patch index (LPI, %) | 2.160 | 7.097 |
斑块结合度指数 Patch cohesion index (COHESION) | 99.506 | 99.822 |
分割指数 Segmentation index (DIVISION) | 0.999 | 0.994 |
分离度指数 Separation index (SPLIT) | 1,552.672 | 166.004 |
区县 County | 大熊猫适宜生境面积 Suitable habitat area of giant panda (km2) | 黑熊适宜生境面积 Suitable habitat area of black bear (km2) | 重叠的栖息地 Overlap habitat | ||
---|---|---|---|---|---|
面积 Area (km2) | 占大熊猫适宜生境比例 Percent of giant panda suitable habitat area (%) | 占黑熊适宜生境比例 Percent of black bear suitable habitat area (%) | |||
峨边县 Ebian County | 459.81 | 846.91 | 369.38 | 80.33 | 43.62 |
金口河区 Jinkouhe District | 12.73 | 66.68 | 11.18 | 87.83 | 16.77 |
甘洛县 Ganluo County | 159.94 | 254.95 | 105.10 | 65.71 | 41.22 |
马边县 Mabian County | 155.45 | 492.47 | 129.16 | 83.09 | 26.23 |
沐川县 Muchuan County | 0 | 15.64 | 0 | - | 0 |
屏山县 Pingshan County | 0 | 32.50 | 0 | - | 0 |
美姑县 Meigu County | 290.02 | 239.89 | 175.86 | 60.64 | 73.31 |
雷波县 Leibo County | 214.56 | 427.38 | 148.41 | 69.17 | 34.73 |
越西县 Yuexi County | 91.33 | 35.07 | 19.20 | 21.02 | 54.74 |
总计 Total | 1,383.84 | 2,411.49 | 958.29 | 69.25 | 39.74 |
表2 凉山山系大熊猫和黑熊适宜生境重叠区域面积统计
Table 2 The overlap habitat area of Ailuropoda melanoleuca and Ursus thibetanus in Liangshan Mountains
区县 County | 大熊猫适宜生境面积 Suitable habitat area of giant panda (km2) | 黑熊适宜生境面积 Suitable habitat area of black bear (km2) | 重叠的栖息地 Overlap habitat | ||
---|---|---|---|---|---|
面积 Area (km2) | 占大熊猫适宜生境比例 Percent of giant panda suitable habitat area (%) | 占黑熊适宜生境比例 Percent of black bear suitable habitat area (%) | |||
峨边县 Ebian County | 459.81 | 846.91 | 369.38 | 80.33 | 43.62 |
金口河区 Jinkouhe District | 12.73 | 66.68 | 11.18 | 87.83 | 16.77 |
甘洛县 Ganluo County | 159.94 | 254.95 | 105.10 | 65.71 | 41.22 |
马边县 Mabian County | 155.45 | 492.47 | 129.16 | 83.09 | 26.23 |
沐川县 Muchuan County | 0 | 15.64 | 0 | - | 0 |
屏山县 Pingshan County | 0 | 32.50 | 0 | - | 0 |
美姑县 Meigu County | 290.02 | 239.89 | 175.86 | 60.64 | 73.31 |
雷波县 Leibo County | 214.56 | 427.38 | 148.41 | 69.17 | 34.73 |
越西县 Yuexi County | 91.33 | 35.07 | 19.20 | 21.02 | 54.74 |
总计 Total | 1,383.84 | 2,411.49 | 958.29 | 69.25 | 39.74 |
环境因子 Variables | 大熊猫 Ailuropoda melanoleuca | 黑熊 Ursus thibetanus | 环境因子 Variables | 大熊猫 Ailuropoda melanoleuca | 黑熊 Ursus thibetanus |
---|---|---|---|---|---|
距居民点距离 Distance to residents | 31.8 | 59.7 | 坡度 Slope | 4.2 | 1.7 |
距道路距离 Distance to roads | 4.9 | 6.4 | 坡向 Aspect | 1.5 | 2.3 |
植被类型 Vegetation types | 10.9 | 2.5 | 坡位 Position on slope | 1.1 | 2.8 |
年最大EVI指数 Annual maximum EVI | 1.9 | 6.9 | 距河流距离 Distance to rivers | 2.8 | 1.6 |
年平均EVI指数 Annual average EVI | 1.7 | 1.4 | 最干季降水量 Percipitation of driest quarter (Bio17) | 4.8 | 3.7 |
海拔 Altitude | 26.4 | 9.6 | 最冷季均温 Mean temperature of coldest quarter (Bio11) | 8 | 1.5 |
表3 环境因子对物种分布模型的置换重要性(%)
Table 3 The permutation importance of environmental variables for species distribution models (%)
环境因子 Variables | 大熊猫 Ailuropoda melanoleuca | 黑熊 Ursus thibetanus | 环境因子 Variables | 大熊猫 Ailuropoda melanoleuca | 黑熊 Ursus thibetanus |
---|---|---|---|---|---|
距居民点距离 Distance to residents | 31.8 | 59.7 | 坡度 Slope | 4.2 | 1.7 |
距道路距离 Distance to roads | 4.9 | 6.4 | 坡向 Aspect | 1.5 | 2.3 |
植被类型 Vegetation types | 10.9 | 2.5 | 坡位 Position on slope | 1.1 | 2.8 |
年最大EVI指数 Annual maximum EVI | 1.9 | 6.9 | 距河流距离 Distance to rivers | 2.8 | 1.6 |
年平均EVI指数 Annual average EVI | 1.7 | 1.4 | 最干季降水量 Percipitation of driest quarter (Bio17) | 4.8 | 3.7 |
海拔 Altitude | 26.4 | 9.6 | 最冷季均温 Mean temperature of coldest quarter (Bio11) | 8 | 1.5 |
环境因子 Environmental variables | 适宜范围 Suitable ranges | |
---|---|---|
大熊猫 Ailuropoda melanoleuca | 黑熊 Ursus thibetanus | |
距居民点距离 Distance to residents (km) | 4-8 | > 3 |
距道路距离 Distance to roads (km) | 4-9 | > 3 |
海拔 Altitude (m) | 2,500-3,600 | 2,000-3,250 |
最冷季均温 Mean temperature of coldest quarter (℃, Bio11) | -4至1 | -3至3 |
年最大EVI Annual maximum EVI | 0.46-0.55 | 0.56-0.65 |
植被类型 Vegetation types | 物种在针叶林中分布概率最大, 其次是阔叶林, 在其他植被类型中的分布概率较小 The most important vegetation types for this species is coniferous forest, followed by broadleaf forest. The distribution probability in other vegetation types is low. | 物种在针叶林中分布概率最大, 其次是阔叶林, 在其他植被类型中的分布概率较小 The most important vegetation types for this species is coniferous forest, followed by broadleaf forest. The distribution probability in other vegetation types is low. |
表4 物种潜在分布对应的主导环境因子适宜范围
Table 4 The suitable ranges of dominant environmental variables affecting the potential distribution of species
环境因子 Environmental variables | 适宜范围 Suitable ranges | |
---|---|---|
大熊猫 Ailuropoda melanoleuca | 黑熊 Ursus thibetanus | |
距居民点距离 Distance to residents (km) | 4-8 | > 3 |
距道路距离 Distance to roads (km) | 4-9 | > 3 |
海拔 Altitude (m) | 2,500-3,600 | 2,000-3,250 |
最冷季均温 Mean temperature of coldest quarter (℃, Bio11) | -4至1 | -3至3 |
年最大EVI Annual maximum EVI | 0.46-0.55 | 0.56-0.65 |
植被类型 Vegetation types | 物种在针叶林中分布概率最大, 其次是阔叶林, 在其他植被类型中的分布概率较小 The most important vegetation types for this species is coniferous forest, followed by broadleaf forest. The distribution probability in other vegetation types is low. | 物种在针叶林中分布概率最大, 其次是阔叶林, 在其他植被类型中的分布概率较小 The most important vegetation types for this species is coniferous forest, followed by broadleaf forest. The distribution probability in other vegetation types is low. |
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