
生物多样性 ›› 2026, Vol. 34 ›› Issue (6): 25501. DOI: 10.17520/biods.2025501 cstr: 32101.14.biods.2025501
郭画1(
), 罗雨甜2, 董译莉3(
), 周铝1(
), 姚世贸1, 朱旭飞1, 田成1,*(
)(
)
收稿日期:2025-12-18
接受日期:2026-03-19
出版日期:2026-06-20
发布日期:2026-07-30
通讯作者:
*E-mail: tiancheng@sxau.edu.cn
基金资助:
Hua Guo1(
), Yutian Luo2, Yili Dong3(
), Lü Zhou1(
), Shimao Yao1, Xufei Zhu1, Cheng Tian1,*(
)(
)
Received:2025-12-18
Accepted:2026-03-19
Online:2026-06-20
Published:2026-07-30
Contact:
*E-mail: tiancheng@sxau.edu.cn
Supported by:摘要:
家畜放牧是威胁野生动物的重要因素之一, 明确野生动物对放牧干扰的响应对物种保护意义重大。自然保护区中散养的牛、马等家畜会破坏野生动物栖息地, 但关于家畜如何影响雉类时空分布格局的相关定量评估仍十分有限。本研究于2011-2015年选取四川王朗国家级自然保护区为研究区域, 以红腹角雉(Tragopan temminckii)和家畜(牛、马)为研究对象开展红外相机监测, 采用多物种占域模型(multi-species occupancy models)、核密度估计方法(kernel density estimation)和回避-吸引指数(avoidance-attraction ratios, AAR)探究家畜放牧对红腹角雉栖息地活动节律及占域的影响。结果显示, 在时间维度上, 红腹角雉的活动模式与家畜高度重叠(重叠系数∆4 = 0.74, 95% CI: 0.73-0.95), 行为上显著回避家畜(AAR = 3.17)。在空间维度上, 红腹角雉的边际占域率与灌木盖度(β = 0.16)、郁闭度(β = 0.06)呈正相关, 与凋落物(β = -0.36)、草本盖度(β = -0.41)、海拔(β = -0.20)、竹子盖度(β = -0.10)呈负相关; 家畜的边际占域率与郁闭度(β = 0.39)呈正相关, 与凋落物(β = -0.10)、距最近河流距离(β = -0.15)、海拔(β = -0.33)、灌木盖度(β = -0.54)、竹子盖度(β = -0.25)呈负相关。红腹角雉的栖息地利用同时受家畜以及其他生态因子的共同影响。家畜的存在改变了红腹角雉对竹子盖度、海拔和距最近河流距离的占域响应, 使其更倾向于利用竹子盖度较高、海拔较低且距最近河流较远的栖息地。我们建议对家畜放牧进行管控, 以促进王朗国家级自然保护区雉类种群及栖息地的恢复。
郭画, 罗雨甜, 董译莉, 周铝, 姚世贸, 朱旭飞, 田成 (2026) 放牧干扰对王朗国家级自然保护区红腹角雉时空分布的影响. 生物多样性, 34, 25501. DOI: 10.17520/biods.2025501.
Hua Guo, Yutian Luo, Yili Dong, Lü Zhou, Shimao Yao, Xufei Zhu, Cheng Tian (2026) Effects of livestock grazing on the spatio-temporal distribution of Tragopan temminckii in Wanglang National Nature Reserve. Biodiversity Science, 34, 25501. DOI: 10.17520/biods.2025501.
| 环境协变量 Environmental covariates | 描述 Description | 协变量类型 Covariate type |
|---|---|---|
| 相机监测天数 Camera monitoring days (d) | 每个相机的监测天数 Monitoring days of each camera | 探测协变量(p) |
| 海拔 Altitude (m) | 每个相机位点的海拔高度 Altitude of each camera | 占域协变量(ψ) |
| 郁闭度 Canopy closure (%) | 20 m × 20 m样方中乔木树冠比例 Proportion of tree crowns in a 20 m × 20 m quadrat | 占域协变量(ψ) |
| 草本盖度 Herbaceous coverage (%) | 20 m × 20 m样方中草本覆盖比例 Proportion of herbaceous coverage in a 20 m × 20 m quadrat | 占域协变量(ψ) |
| 灌木盖度 Shrub coverage (%) | 20 m × 20 m样方中灌木覆盖比例 Proportion of shrub coverage in a 20 m × 20 m quadrat | 占域协变量(ψ) |
| 竹子盖度 Bamboo coverage (%) | 20 m × 20 m样方中竹子覆盖比例 Proportion of bamboo coverage in a 20 m × 20 m quadrat | 占域协变量(ψ) |
| 凋落物 Litter layer (cm) | 20 m × 20 m样方中凋落物的厚度 Thickness of litter in a 20 m × 20 m quadrat | 占域协变量(ψ) |
| 距最近河流距离 Distance to the nearest river (m) | 基于ArcGIS 10.8提取相机监测点位距最近水源的距离 The distance from the camera monitoring point to the nearest water source (extracted using ArcGIS 10.8) | 占域协变量(ψ) |
表1 8种用于建模的环境协变量
Table 1 Eight environmental covariates used for modelling purposes
| 环境协变量 Environmental covariates | 描述 Description | 协变量类型 Covariate type |
|---|---|---|
| 相机监测天数 Camera monitoring days (d) | 每个相机的监测天数 Monitoring days of each camera | 探测协变量(p) |
| 海拔 Altitude (m) | 每个相机位点的海拔高度 Altitude of each camera | 占域协变量(ψ) |
| 郁闭度 Canopy closure (%) | 20 m × 20 m样方中乔木树冠比例 Proportion of tree crowns in a 20 m × 20 m quadrat | 占域协变量(ψ) |
| 草本盖度 Herbaceous coverage (%) | 20 m × 20 m样方中草本覆盖比例 Proportion of herbaceous coverage in a 20 m × 20 m quadrat | 占域协变量(ψ) |
| 灌木盖度 Shrub coverage (%) | 20 m × 20 m样方中灌木覆盖比例 Proportion of shrub coverage in a 20 m × 20 m quadrat | 占域协变量(ψ) |
| 竹子盖度 Bamboo coverage (%) | 20 m × 20 m样方中竹子覆盖比例 Proportion of bamboo coverage in a 20 m × 20 m quadrat | 占域协变量(ψ) |
| 凋落物 Litter layer (cm) | 20 m × 20 m样方中凋落物的厚度 Thickness of litter in a 20 m × 20 m quadrat | 占域协变量(ψ) |
| 距最近河流距离 Distance to the nearest river (m) | 基于ArcGIS 10.8提取相机监测点位距最近水源的距离 The distance from the camera monitoring point to the nearest water source (extracted using ArcGIS 10.8) | 占域协变量(ψ) |
| 模型选择 Model selection | 参数个数 (K) | 似然对数 (logLik) | 基于小样本量修正的赤池信息量准则(AICc) | AICc差值 AICc differences | 权重 Weight |
|---|---|---|---|---|---|
| 红腹角雉 Tragopan temminckii | |||||
| p(day), ψ(herb) | 4 | -365.39 | 738.95 | 0.00 | 0.12 |
| p(day), ψ(litter + herb + shrub) | 6 | -358.53 | 739.13 | 0.17 | 0.11 |
| p(day), ψ(litter + herb) | 5 | -361.88 | 739.16 | 0.21 | 0.11 |
| p(day), ψ(litter + herb + altitude) | 6 | -358.53 | 739.16 | 0.21 | 0.11 |
| p(day), ψ(herb + altitude) | 5 | -362.10 | 739.65 | 0.69 | 0.09 |
| p(day), ψ(herb + bamboo) | 5 | -362.11 | 739.68 | 0.72 | 0.08 |
| p(day), ψ(litter + herb + bamboo) | 6 | -358.73 | 740.15 | 1.19 | 0.07 |
| p(day), ψ(herb + shrub) | 5 | -362.40 | 740.21 | 1.26 | 0.06 |
| p(day), ψ(litter + herb + altitude + shrub) | 7 | -352.34 | 740.40 | 1.45 | 0.06 |
| p(day), ψ(litter+ herb + altitude + bamboo) | 7 | -352.43 | 740.56 | 1.61 | 0.05 |
| p(day), ψ(herb +bamboo +altitude) | 6 | -358.90 | 740.68 | 1.73 | 0.05 |
| p(day), ψ(litter + herb + bamboo + shrub) | 7 | -352.54 | 740.86 | 1.91 | 0.05 |
| p(day), ψ(herb + canopy) | 5 | -362.66 | 740.89 | 1.93 | 0.05 |
| 家畜 Livestock | |||||
| p(.), ψ(canopy + altitude + shrub) | 5 | -184.68 | 394.67 | 0.00 | 0.12 |
| p(.), ψ(canopy + shrub) | 4 | -188.38 | 395.04 | 0.37 | 0.10 |
| p(.), ψ(shrub) | 3 | -191.91 | 395.15 | 0.48 | 0.10 |
| p(.), ψ(altitude + shrub) | 4 | -188.47 | 395.33 | 0.66 | 0.09 |
| p(.), ψ(canopy + bamboo + altitude + shrub) | 6 | -181.72 | 395.53 | 0.86 | 0.08 |
| p(.), ψ(canopy) | 3 | -192.00 | 395.68 | 1.01 | 0.07 |
| p(.), ψ(canopy + bamboo + shrub) | 5 | -184.85 | 395.75 | 1.08 | 0.07 |
| p(.), ψ(bamboo + shrub) | 4 | -188.58 | 395.93 | 1.26 | 0.07 |
| p(.), ψ(bamboo + altitude + shrub) | 5 | -185.04 | 396.23 | 1.56 | 0.06 |
| p(.), ψ(litter + canopy + altitude + shrub) | 6 | -181.82 | 396.29 | 1.62 | 0.05 |
| p(.), ψ(.) | 2 | -195.33 | 396.37 | 1.70 | 0.05 |
| p(.), ψ(canopy + altitude + river + shrub) | 6 | -181.93 | 396.57 | 1.90 | 0.05 |
| p(.), ψ(canopy + river + shrub) | 5 | -185.11 | 396.63 | 1.96 | 0.04 |
| p(.), ψ(litter + canopy) | 4 | -188.66 | 396.65 | 1.98 | 0.04 |
表2 单物种占域模型选择结果
Table 2 Single-species occupancy model selection results
| 模型选择 Model selection | 参数个数 (K) | 似然对数 (logLik) | 基于小样本量修正的赤池信息量准则(AICc) | AICc差值 AICc differences | 权重 Weight |
|---|---|---|---|---|---|
| 红腹角雉 Tragopan temminckii | |||||
| p(day), ψ(herb) | 4 | -365.39 | 738.95 | 0.00 | 0.12 |
| p(day), ψ(litter + herb + shrub) | 6 | -358.53 | 739.13 | 0.17 | 0.11 |
| p(day), ψ(litter + herb) | 5 | -361.88 | 739.16 | 0.21 | 0.11 |
| p(day), ψ(litter + herb + altitude) | 6 | -358.53 | 739.16 | 0.21 | 0.11 |
| p(day), ψ(herb + altitude) | 5 | -362.10 | 739.65 | 0.69 | 0.09 |
| p(day), ψ(herb + bamboo) | 5 | -362.11 | 739.68 | 0.72 | 0.08 |
| p(day), ψ(litter + herb + bamboo) | 6 | -358.73 | 740.15 | 1.19 | 0.07 |
| p(day), ψ(herb + shrub) | 5 | -362.40 | 740.21 | 1.26 | 0.06 |
| p(day), ψ(litter + herb + altitude + shrub) | 7 | -352.34 | 740.40 | 1.45 | 0.06 |
| p(day), ψ(litter+ herb + altitude + bamboo) | 7 | -352.43 | 740.56 | 1.61 | 0.05 |
| p(day), ψ(herb +bamboo +altitude) | 6 | -358.90 | 740.68 | 1.73 | 0.05 |
| p(day), ψ(litter + herb + bamboo + shrub) | 7 | -352.54 | 740.86 | 1.91 | 0.05 |
| p(day), ψ(herb + canopy) | 5 | -362.66 | 740.89 | 1.93 | 0.05 |
| 家畜 Livestock | |||||
| p(.), ψ(canopy + altitude + shrub) | 5 | -184.68 | 394.67 | 0.00 | 0.12 |
| p(.), ψ(canopy + shrub) | 4 | -188.38 | 395.04 | 0.37 | 0.10 |
| p(.), ψ(shrub) | 3 | -191.91 | 395.15 | 0.48 | 0.10 |
| p(.), ψ(altitude + shrub) | 4 | -188.47 | 395.33 | 0.66 | 0.09 |
| p(.), ψ(canopy + bamboo + altitude + shrub) | 6 | -181.72 | 395.53 | 0.86 | 0.08 |
| p(.), ψ(canopy) | 3 | -192.00 | 395.68 | 1.01 | 0.07 |
| p(.), ψ(canopy + bamboo + shrub) | 5 | -184.85 | 395.75 | 1.08 | 0.07 |
| p(.), ψ(bamboo + shrub) | 4 | -188.58 | 395.93 | 1.26 | 0.07 |
| p(.), ψ(bamboo + altitude + shrub) | 5 | -185.04 | 396.23 | 1.56 | 0.06 |
| p(.), ψ(litter + canopy + altitude + shrub) | 6 | -181.82 | 396.29 | 1.62 | 0.05 |
| p(.), ψ(.) | 2 | -195.33 | 396.37 | 1.70 | 0.05 |
| p(.), ψ(canopy + altitude + river + shrub) | 6 | -181.93 | 396.57 | 1.90 | 0.05 |
| p(.), ψ(canopy + river + shrub) | 5 | -185.11 | 396.63 | 1.96 | 0.04 |
| p(.), ψ(litter + canopy) | 4 | -188.66 | 396.65 | 1.98 | 0.04 |
图4 最优占域协变量分别对红腹角雉和家畜边际占域率的影响。阴影是95%的置信区间。
Fig. 4 Marginal occupancy probability of Tragopan temminckii and livestock are influenced by optimal occupancy covariates. The shaded areas are 95% credible intervals.
图5 家畜存在/不存在条件下红腹角雉的占域率随竹子盖度、海拔和距最近河流距离的变化情况。阴影是95%的置信区间。
Fig. 5 Under the presence and absence of livestock, the occupancy probability of Tragopan temminckii varies along the gradients of bamboo coverage, altitude, and distance to the nearest river. The shaded areas are 95% credible intervals.
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