生物多样性 ›› 2022, Vol. 30 ›› Issue (1): 21176. DOI: 10.17520/biods.2021176
张晨1,2,3,4, 马伟5, 陈晨1,2,3,4, 汪沐阳1,2,3, 徐文轩1,2,3, 杨维康1,2,3,*()
收稿日期:
2021-05-07
接受日期:
2021-08-26
出版日期:
2022-01-20
发布日期:
2022-01-29
通讯作者:
杨维康
作者简介:
* E-mail: yangwk@ms.xjb.ac.cn基金资助:
Chen Zhang1,2,3,4, Wei Ma5, Chen Chen1,2,3,4, Muyang Wang1,2,3, Wenxuan Xu1,2,3, Weikang Yang1,2,3,*()
Received:
2021-05-07
Accepted:
2021-08-26
Online:
2022-01-20
Published:
2022-01-29
Contact:
Weikang Yang
摘要:
生境评价对物种保护具有重要意义。鹅喉羚(Gazella subgutturosa)是新疆卡拉麦里山有蹄类野生动物自然保护区的代表性物种, 开展其生境适宜性评价可以为该物种的保护和管理提供科学依据。作者基于2005-2019年采用样线法在保护区开展野外调查所获鹅喉羚的分布点数据, 利用最大熵(MaxEnt)模型筛选环境变量, 评估鹅喉羚在矿业开发前(2005年)、矿业开发顶峰时(2011年)和矿区生态修复后(2019年) 3个时期的生境质量; 采用质心转移和景观格局指数分析近15年鹅喉羚的生境空间格局变化特征。结果表明模型预测结果准确性较高, 3个时期鹅喉羚的潜在适宜生境面积波动较大, Jackknife检验结果表明在任一时期水源点对鹅喉羚生境选择的影响均最大。矿业开发前鹅喉羚适宜生境分布于保护区中部, 主要特征为面积大、生境斑块集中、破碎化程度低; 矿业开发顶峰时鹅喉羚的适宜生境面积较矿业开发前减少2.39%, 尤其是保护区南部大面积适宜生境丧失, 质心转移和景观格局指数分析结果显示适宜生境向保护区北部转移, 生境斑块离散破碎程度高; 实施矿区生态修复后鹅喉羚的适宜生境面积较矿业开发顶峰时增加了3.50%, 因矿业开发丧失的生境重新成为鹅喉羚的适宜生境。与2005年以前相比, 2019年鹅喉羚生境斑块仍离散化严重, 部分适宜生境因新修建的高速公路和铁路而重新丧失。基于以上研究结果, 我们从保护水源、控制交通建设、修复矿区和加强野生动物通道监测等4个方面对鹅喉羚种群保护管理提出了建议。
张晨, 马伟, 陈晨, 汪沐阳, 徐文轩, 杨维康 (2022) 重大工程影响下新疆卡拉麦里山有蹄类野生动物自然保护区鹅喉羚的生境格局变化. 生物多样性, 30, 21176. DOI: 10.17520/biods.2021176.
Chen Zhang, Wei Ma, Chen Chen, Muyang Wang, Wenxuan Xu, Weikang Yang (2022) Changes of habitat pattern for goitered gazelle in the Xinjiang Kalamaili Mountain Ungulate Nature Reserve under the influence of major projects. Biodiversity Science, 30, 21176. DOI: 10.17520/biods.2021176.
图2 新疆卡拉麦里山有蹄类野生动物自然保护区调查样线及鹅喉羚2005年(a)、2011年(b)和2019年(c)分布位点图
Fig. 2 Transect and occurrence of goitered gazelle in 2005(a), 2011(b), and 2019(c) in the Xinjiang Kalamaili Mountain Ungulate Nature Reserve
序号 No. | 2005 | 2011 | 2019 | |||
---|---|---|---|---|---|---|
变量 Variable | 贡献率 Contribution | 变量 Variable | 贡献率 Contribution | 变量 Variable | 贡献率 Contribution | |
1 | 距水源点距离 Distance to water source | 32.9% | 距水源点距离 Distance to water source | 22.5% | 距水源点距离 Distance to water source | 23.2% |
2 | 海拔 Altitude | 13.3% | 最暖季平均温 Mean temperature of warmest quarter (Bio 10) | 19.9% | 最暖季平均温 Mean temperature of warmest quarter (Bio 10) | 18.9% |
3 | 距216国道距离 Distance to national road 216 | 7.3% | 距矿点距离 Distance to mining | 11.6% | 距阿富准铁路距离 Distance to Altay-Zhundong railway | 12.3% |
4 | 年降水量 Annual precipitation (Bio 12) | 6.8% | 年均温 Annual mean temperature (Bio 1) | 7.7% | 距矿点距离 Distance to mining | 11.8% |
5 | 月均温范围 Mean diurnal range (Bio 2) | 4.9% | 距216国道距离 Distance to national road 216 | 6.4% | 年均温 Annual mean temperature (Bio 1) | 4.9% |
6 | 最湿季降水量 Precipitation of wettest quarter (Bio 16) | 4.7% | 最暖月最高温 Max. temperature of warmest month (Bio 5) | 5.8% | 最干季平均温 Mean temperature of driest quarter (Bio 9) | 4.0% |
表1 2005、2011和2019年主要环境变量的贡献率
Table 1 Major environmental variables and their contributions in 2005, 2011, and 2019
序号 No. | 2005 | 2011 | 2019 | |||
---|---|---|---|---|---|---|
变量 Variable | 贡献率 Contribution | 变量 Variable | 贡献率 Contribution | 变量 Variable | 贡献率 Contribution | |
1 | 距水源点距离 Distance to water source | 32.9% | 距水源点距离 Distance to water source | 22.5% | 距水源点距离 Distance to water source | 23.2% |
2 | 海拔 Altitude | 13.3% | 最暖季平均温 Mean temperature of warmest quarter (Bio 10) | 19.9% | 最暖季平均温 Mean temperature of warmest quarter (Bio 10) | 18.9% |
3 | 距216国道距离 Distance to national road 216 | 7.3% | 距矿点距离 Distance to mining | 11.6% | 距阿富准铁路距离 Distance to Altay-Zhundong railway | 12.3% |
4 | 年降水量 Annual precipitation (Bio 12) | 6.8% | 年均温 Annual mean temperature (Bio 1) | 7.7% | 距矿点距离 Distance to mining | 11.8% |
5 | 月均温范围 Mean diurnal range (Bio 2) | 4.9% | 距216国道距离 Distance to national road 216 | 6.4% | 年均温 Annual mean temperature (Bio 1) | 4.9% |
6 | 最湿季降水量 Precipitation of wettest quarter (Bio 16) | 4.7% | 最暖月最高温 Max. temperature of warmest month (Bio 5) | 5.8% | 最干季平均温 Mean temperature of driest quarter (Bio 9) | 4.0% |
图3 2005年(a)、2011年(b)和2019年(c)鹅喉羚适宜生境分布图。蓝色表示适宜度较低区域,红色表示适宜度最高区域。
Fig. 3 Distribution of suitable habitat of goitered gazelle in 2005 (a), 2011 (b), and 2019 (c). Unsuitable habitat is shown in blue, and red areas represent suitable habitat.
年 Year | 适宜生境 Suitable habitat | 不适宜生境 Unsuitable habitat | ||||
---|---|---|---|---|---|---|
面积 Area (km2) | 占比 Percentage (%) | 变化率 Variation (%) | 面积 Area (km2) | 占比 Percentage (%) | 变化率 Variation (%) | |
2005 | 4,267 | 28.78 | - | 10,557 | 71.22 | - |
2011 | 3,914 | 26.39 | -8.27 | 10,917 | 73.61 | 3.41 |
2019 | 4,434 | 29.89 | 13.28 | 10,397 | 70.10 | -4.76 |
表2 2005、2011和2019年鹅喉羚适宜生境面积及变化
Table 2 Suitable habitat area and changes of goitered gazelle in 2005, 2011, and 2019
年 Year | 适宜生境 Suitable habitat | 不适宜生境 Unsuitable habitat | ||||
---|---|---|---|---|---|---|
面积 Area (km2) | 占比 Percentage (%) | 变化率 Variation (%) | 面积 Area (km2) | 占比 Percentage (%) | 变化率 Variation (%) | |
2005 | 4,267 | 28.78 | - | 10,557 | 71.22 | - |
2011 | 3,914 | 26.39 | -8.27 | 10,917 | 73.61 | 3.41 |
2019 | 4,434 | 29.89 | 13.28 | 10,397 | 70.10 | -4.76 |
图4 不同时期鹅喉羚适宜生境空间格局变化及质心转移
Fig. 4 The spatial pattern changes and centroid transfer of the suitable habitat of goitered gazelle under different periods
年 Year | 生境类型 Habitat type | 斑块面积 Patch area (km2) | 斑块数量 Number of patches (n) | 斑块密度 Patch density (n/km2) | 最大斑块指数 Largest patch index (%) | 景观形状指数 Landscape shape index | 相似临近比度 Proportion of like adjacencies | 聚集度指数 Aggregation index (%) | 斑块类型占总面积的比例 Percentage of Landscape (%) |
---|---|---|---|---|---|---|---|---|---|
2005 | 不适宜 Unsuitable | 10,557 | 33 | 0.0033 | 70.57 | 5.97 | 94.17 | 95.10 | 71.20 |
适宜 Suitable | 4,267 | 49 | 0.0022 | 26.26 | 7.09 | 89.10 | 90.49 | 28.79 | |
2011 | 不适宜 Unsuitable | 10917 | 51 | 0.0034 | 72.03 | 7.71 | 92.62 | 93.51 | 73.61 |
适宜 Suitable | 3914 | 48 | 0.0032 | 24.63 | 10.56 | 82.99 | 84.35 | 26.39 | |
2019 | 不适宜 Unsuitable | 10,397 | 39 | 0.0026 | 65.57 | 5.30 | 94.79 | 95.73 | 70.10 |
适宜 Suitable | 4,434 | 29 | 0.0020 | 16.50 | 5.90 | 91.08 | 92.47 | 28.89 |
表3 2005年、2011年和2019年鹅喉羚景观格局指数
Table 3 Landscape index of goitered gazelle in 2005, 2011, and 2019
年 Year | 生境类型 Habitat type | 斑块面积 Patch area (km2) | 斑块数量 Number of patches (n) | 斑块密度 Patch density (n/km2) | 最大斑块指数 Largest patch index (%) | 景观形状指数 Landscape shape index | 相似临近比度 Proportion of like adjacencies | 聚集度指数 Aggregation index (%) | 斑块类型占总面积的比例 Percentage of Landscape (%) |
---|---|---|---|---|---|---|---|---|---|
2005 | 不适宜 Unsuitable | 10,557 | 33 | 0.0033 | 70.57 | 5.97 | 94.17 | 95.10 | 71.20 |
适宜 Suitable | 4,267 | 49 | 0.0022 | 26.26 | 7.09 | 89.10 | 90.49 | 28.79 | |
2011 | 不适宜 Unsuitable | 10917 | 51 | 0.0034 | 72.03 | 7.71 | 92.62 | 93.51 | 73.61 |
适宜 Suitable | 3914 | 48 | 0.0032 | 24.63 | 10.56 | 82.99 | 84.35 | 26.39 | |
2019 | 不适宜 Unsuitable | 10,397 | 39 | 0.0026 | 65.57 | 5.30 | 94.79 | 95.73 | 70.10 |
适宜 Suitable | 4,434 | 29 | 0.0020 | 16.50 | 5.90 | 91.08 | 92.47 | 28.89 |
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