生物多样性 ›› 2022, Vol. 30 ›› Issue (9): 21510. DOI: 10.17520/biods.2021510
王一晴1, 马子驭1, 王刚2, 刘炎林1, 宋大昭1, 刘蓓蓓1, 李露1, 范新国3, 黄巧雯1,*(), 李晟4,5,*()
收稿日期:
2021-12-10
接受日期:
2022-03-24
出版日期:
2022-09-20
发布日期:
2022-04-06
通讯作者:
黄巧雯,李晟
作者简介:
* E-mail: office@felidchina.org;Yiqing Wang1, Ziyu Ma1, Gang Wang2, Yanlin Liu1, Dazhao Song1, Beibei Liu1, Lu Li1, Xinguo Fan3, Qiaowen Huang1,*(), Sheng Li4,5,*()
Received:
2021-12-10
Accepted:
2022-03-24
Online:
2022-09-20
Published:
2022-04-06
Contact:
Qiaowen Huang,Sheng Li
摘要:
人兽冲突是全球野生动物保护面临的共同挑战。袭击家畜是大型食肉动物引发人兽冲突的主要原因之一, 如果管理不当还会导致针对大型食肉动物的报复性猎杀等严重威胁。冲突的缓解需要深入了解冲突发生的规律与原因, 评估当地社区与居民的态度与看法, 以采取因地制宜的管理措施。太行山是华北豹(Panthera pardus japonensis)的核心分布区, 华北豹袭击家牛的问题是该区域野生华北豹保护中面临的一大挑战。本研究以山西省和顺县为研究区域, 在多方联合发起的“和顺县华北豹袭击家牛肇事补偿项目”实施过程中, 系统收集了2015-2019年期间华北豹袭击家畜事件的记录, 结合同期的红外相机监测数据, 探究了袭击事件的时空分布格局, 并从生境和猎物的角度分析了背后的原因。本文还评估了豹肇事造成的经济损失, 以及受损农户对华北豹的态度和对补偿的满意度。2015-2019年, 项目区域内共记录到华北豹袭击家牛事件195起, 向116户受损农户提供补偿资金共27.05万元。分析结果显示, 华北豹袭击家牛事件在夏季最多, 时间上与家牛上山散放的季节重叠; 袭击风险随狍(Capreolus pygargus)相对多度的上升而下降, 随家牛相对多度和距村庄距离的增加而上升, 但保护区内外和华北豹相对多度对袭击风险的影响不显著。对107名受损农户的访谈结果显示, 华北豹袭击家牛事件虽然对当地畜牧业所造成的整体损失较小, 但对受损农户而言其家庭收入损失严重, 因此导致受损农户对华北豹持负面态度, 且认为现有的补偿金额偏低。基于本研究的结果, 我们提出如下管理建议以期缓解未来该地区华北豹带来的人兽冲突: (1)加强放牧管理、改进管理方式, 特别是限制牛群离开村庄的距离, 以及在家牛散放期间将牛群每晚赶回牛圈以降低家畜被袭击的风险; (2)开展禁牧试点, 严格划分允许放牧与禁止放牧的区域; (3)继续开展华北豹袭击家牛的定损与补偿工作, 降低当地农户的经济损失, 同时开展社区走访、自然教育, 提升当地居民对华北豹的容忍度; (4)加强野生动物种群的监测与保护, 促进人与野生动物的和谐共存。
王一晴, 马子驭, 王刚, 刘炎林, 宋大昭, 刘蓓蓓, 李露, 范新国, 黄巧雯, 李晟 (2022) 太行山华北豹袭击家畜的时空特点与管理建议: 以山西省和顺县为例. 生物多样性, 30, 21510. DOI: 10.17520/biods.2021510.
Yiqing Wang, Ziyu Ma, Gang Wang, Yanlin Liu, Dazhao Song, Beibei Liu, Lu Li, Xinguo Fan, Qiaowen Huang, Sheng Li (2022) Spatiotemporal patterns of cattle depredation by the North Chinese leopard in Taihang Mountains and its management strategy: A case study in Heshun, Shanxi Province. Biodiversity Science, 30, 21510. DOI: 10.17520/biods.2021510.
图1 山西省和顺县2015-2019年华北豹袭击家牛肇事补偿项目覆盖行政村及豹肇事事件发生位点分布(a), 以及2016-2019年红外相机监测位点及华北豹探测位点分布(b)
Fig. 1 The spatial distribution of villages covered by the cattle depredation compensation project and depredation events from 2015 to 2019 (a), and the spatial distribution of camera traps and locations with leopard captures from 2016 to 2019 (b) in Heshun County, Shanxi Province
类别 Category | 变量 Predictor | 缩写 Abbreviation | 数据类型 Data type | 数据来源 Data source | 分辨率 Resolution |
---|---|---|---|---|---|
生境 Habitat | 海拔 Elevation (m) | Ele | 连续 Continuous | Shuttle Radar Topography Mission (SRTM) | 30 m |
地形崎岖度指数 Topographic ruggedness index | TRI | 连续 Continuous | Shuttle Radar Topography Mission (SRTM) | 30 m | |
森林覆盖度 Tree cover (%) | TrC | 连续 Continuous | University of Maryland Global Land Analysis and Discovery (GLAD) | 30 m | |
人为 Human | 距村庄距离 Distance to village (m) | dVi | 连续 Continuous | 本研究 This study | 30 m |
保护区内外 Protected area (Inside/Outside) | PA | 分类 Categorical | 本研究 This study | 30 m | |
动物 Animal | 家牛相对多度指数 Relative abundance index of cattle | Ctl | 连续 Continuous | 本研究 This study | 30 m |
豹相对多度指数 Relative abundance index of leopard | Lpd | 连续 Continuous | 本研究 This study | 30 m | |
狍相对多度指数 Relative abundance index of Siberian roe deer | RDr | 连续 Continuous | 本研究 This study | 30 m | |
野猪相对多度指数 Relative abundance index of wild boar | WBr | 连续 Continuous | 本研究 This study | 30 m |
表1 华北豹袭击家牛空间风险模型中使用的预测变量
Table 1 Predicting variables used in the spatial risk modelling of cattle depredation by North Chinese leopards
类别 Category | 变量 Predictor | 缩写 Abbreviation | 数据类型 Data type | 数据来源 Data source | 分辨率 Resolution |
---|---|---|---|---|---|
生境 Habitat | 海拔 Elevation (m) | Ele | 连续 Continuous | Shuttle Radar Topography Mission (SRTM) | 30 m |
地形崎岖度指数 Topographic ruggedness index | TRI | 连续 Continuous | Shuttle Radar Topography Mission (SRTM) | 30 m | |
森林覆盖度 Tree cover (%) | TrC | 连续 Continuous | University of Maryland Global Land Analysis and Discovery (GLAD) | 30 m | |
人为 Human | 距村庄距离 Distance to village (m) | dVi | 连续 Continuous | 本研究 This study | 30 m |
保护区内外 Protected area (Inside/Outside) | PA | 分类 Categorical | 本研究 This study | 30 m | |
动物 Animal | 家牛相对多度指数 Relative abundance index of cattle | Ctl | 连续 Continuous | 本研究 This study | 30 m |
豹相对多度指数 Relative abundance index of leopard | Lpd | 连续 Continuous | 本研究 This study | 30 m | |
狍相对多度指数 Relative abundance index of Siberian roe deer | RDr | 连续 Continuous | 本研究 This study | 30 m | |
野猪相对多度指数 Relative abundance index of wild boar | WBr | 连续 Continuous | 本研究 This study | 30 m |
图2 2015-2019年山西省和顺县因华北豹袭击造成的家牛死伤数量逐月分布曲线(2016年的肇事事件无月份记录, 因此未在图中显示)
Fig. 2 Monthly changes in the number of cattle injured or killed due to leopard predation in Heshun from 2015 to 2019 (No date records for depredation events in 2016, therefore not shown in the figure)
估计 Estimate | 标准差 SE | z | P | ||
---|---|---|---|---|---|
截距 Intercept | -0.6647 | 2.3756 | 0.2800 | 0.7796 | |
Ctl | 0.0088 | 0.0114 | 0.7720 | 0.4400 | |
dVi | 0.0010 | 0.0002 | 4.0410 | 0.0001 | *** |
RDr | -0.4539 | 0.1183 | 3.8350 | 0.0001 | *** |
TRI | -0.0093 | 0.0165 | 0.5640 | 0.5729 | |
TrC | -0.0067 | 0.0117 | 0.5730 | 0.5666 | |
WBr | 0.0430 | 0.0970 | 0.4430 | 0.6579 | |
Ele | 0.0004 | 0.0013 | 0.2730 | 0.7849 |
表2 华北豹袭击家牛空间风险最优模型及参数
Table 2 The best performed model and its parameters in predicting the spatial risk of cattle depredation by North Chinese leopards
估计 Estimate | 标准差 SE | z | P | ||
---|---|---|---|---|---|
截距 Intercept | -0.6647 | 2.3756 | 0.2800 | 0.7796 | |
Ctl | 0.0088 | 0.0114 | 0.7720 | 0.4400 | |
dVi | 0.0010 | 0.0002 | 4.0410 | 0.0001 | *** |
RDr | -0.4539 | 0.1183 | 3.8350 | 0.0001 | *** |
TRI | -0.0093 | 0.0165 | 0.5640 | 0.5729 | |
TrC | -0.0067 | 0.0117 | 0.5730 | 0.5666 | |
WBr | 0.0430 | 0.0970 | 0.4430 | 0.6579 | |
Ele | 0.0004 | 0.0013 | 0.2730 | 0.7849 |
图3 山西省和顺县华北豹袭击家牛的空间风险地图。(a)概率; (b)二值化结果。
Fig. 3 The spatial risk map of cattle depredation by North Chinese leopards in Heshun County, Shanxi Province. (a) Probability; (b) Binary results.
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