生物多样性 ›› 2023, Vol. 31 ›› Issue (6): 22554. DOI: 10.17520/biods.2022554
黄中鸿1, 陈嘉珈1, 温立嘉1, 蒲真1, 马存新2, 高雅月2, 郭玉民1,*()
收稿日期:
2022-09-25
接受日期:
2022-11-15
出版日期:
2023-06-20
发布日期:
2023-01-01
通讯作者:
* E-mail: bird168@126.com
基金资助:
Zhonghong Huang1, Jiajia Chen1, Lijia Wen1, Zhen Pu1, Cunxin Ma2, Yayue Gao2, Yumin Guo1,*()
Received:
2022-09-25
Accepted:
2022-11-15
Online:
2023-06-20
Published:
2023-01-01
Contact:
* E-mail: bird168@126.com
摘要:
祁连山是中国重要的天然牧场及畜牧业基地, 密布的围栏虽然方便了牧民管理, 但也给野生动物带来了安全隐患。为了解网围栏对黑颈鹤(Grus nigricollis)的影响, 2020-2021年, 我们共对祁连山南麓的38只黑颈鹤幼鸟安装卫星跟踪器, 实时监测幼鸟存活状态, 发现跟踪个体活动异常后, 立即前往异常点进行排查, 确定异常原因。通过时序聚类法确认黑颈鹤出羽后期和完全出羽期。并利用核密度分析法和最小凸多边形法估算黑颈鹤出羽后期和完全出羽期在有围栏以及无围栏生境中的家域及核域。通过Mann-Whitney U检验判断两种生境中黑颈鹤家域及核域的差异。结果表明, 祁连山南麓黑颈鹤幼鸟2020年的死亡率为26.67% (N = 15), 2021年为20.00% (N = 20)。其中50%的死亡个体都是由于网围栏导致的。乱海子湿地是出现死亡个体的主要区域。网围栏不仅会导致黑颈鹤幼鸟受伤甚至死亡, 还使处于出羽后期的黑颈鹤家域及核域受到明显限制, 但对于完全出羽期的黑颈鹤的限制却大大减小。为了降低黑颈鹤幼鸟的死亡率, 应改善网围栏的固定方式, 减少刺线及刺状结构, 及时对旧的网围栏进行回收处理。建议在适当位置加上警示物, 保护黑颈鹤种群健康。
黄中鸿, 陈嘉珈, 温立嘉, 蒲真, 马存新, 高雅月, 郭玉民 (2023) 祁连山南麓网围栏对黑颈鹤的影响. 生物多样性, 31, 22554. DOI: 10.17520/biods.2022554.
Zhonghong Huang, Jiajia Chen, Lijia Wen, Zhen Pu, Cunxin Ma, Yayue Gao, Yumin Guo (2023) The influence of fence on black-necked crane (Grus nigricollis) in southern foothills of Qilian Mountains. Biodiversity Science, 31, 22554. DOI: 10.17520/biods.2022554.
图2 网围栏类型、结构以及黑颈鹤主要致危因子。A: 单层围栏; B: 双层围栏; C: 多层围栏; D: 围栏上部横向铁丝上的刺线; E: 交叉处的刺状结构; F: 纵向铁丝上部的游离端; G、H、I: 被猞猁捕食的B39个体(图源: 中国猫科动物保护联盟); J: 挂在网围栏上的W27个体; K: B34个体撞击输配电线的瞬间(张景元摄)。
Fig. 2 The type and structure of fence and main risk factors of black-necked crane. A, Single fence; B, Double fence; C, Multiple fence; D, The barbed wire of the horizontal wire on the upper of the fence; E, The barbed wire at the intersection; F, The free end of the longitudinal wire on the upper of the fence; G, H, I, B39 is preyed by lynx (from Chinese Felid Conservation Alliance); J, W27 is hanging on the fence; K, The moment of B34 collision with wire (from Zhang JY)
环志地点 Installation location | 2020 | 2021 | 平均死亡率 Average mortality rate (%) | ||||
---|---|---|---|---|---|---|---|
环志数 Installation number | 死亡数 Death number | 死亡率 Mortality rate (%) | 环志数 Installation number | 死亡数 Death number | 死亡率 Mortality rate (%) | ||
乱海子湿地 Luanhaizi Wetland | 4 | 3 | 75 | 8 | 3 | 37.5 | 56.25 |
野牛沟乡 Yeniugou Township | 2 | 0 | 0 | 0 | 0 | 0 | 0 |
央隆乡 Yanglong Township | 4 | 1 | 25 | 3 | 0 | 0 | 12.5 |
峨堡镇 Ebao Town | 0 | 0 | 0 | 2 | 0 | 0 | 0 |
木里镇 Muli Town | 0 | 0 | 0 | 1 | 0 | 0 | 0 |
天棚湿地 Tianpeng Wetland | 5 | 0 | 0 | 6 | 1 | 16.67 | 8.34 |
总计 Total | 15 | 4 | 26.67 | 20 | 4 | 20 | 23.34 |
表1 2020-2021年祁连山南麓黑颈鹤幼鸟死亡数据
Table 1 Death data of black-necked crane juvenile on the southern foothills of Qilian Mountains from 2020 to 2021
环志地点 Installation location | 2020 | 2021 | 平均死亡率 Average mortality rate (%) | ||||
---|---|---|---|---|---|---|---|
环志数 Installation number | 死亡数 Death number | 死亡率 Mortality rate (%) | 环志数 Installation number | 死亡数 Death number | 死亡率 Mortality rate (%) | ||
乱海子湿地 Luanhaizi Wetland | 4 | 3 | 75 | 8 | 3 | 37.5 | 56.25 |
野牛沟乡 Yeniugou Township | 2 | 0 | 0 | 0 | 0 | 0 | 0 |
央隆乡 Yanglong Township | 4 | 1 | 25 | 3 | 0 | 0 | 12.5 |
峨堡镇 Ebao Town | 0 | 0 | 0 | 2 | 0 | 0 | 0 |
木里镇 Muli Town | 0 | 0 | 0 | 1 | 0 | 0 | 0 |
天棚湿地 Tianpeng Wetland | 5 | 0 | 0 | 6 | 1 | 16.67 | 8.34 |
总计 Total | 15 | 4 | 26.67 | 20 | 4 | 20 | 23.34 |
生境类型 Habitat type | 时期 Period | 方法 Method | 家域 Home range (km2) | 核域 Core area (km2) | 家域面积范围 Minimum to maximum (km2) | 样本量 Sample size |
---|---|---|---|---|---|---|
有围栏 Fence | 出羽后期 Post-fledging period | 核密度分析法 KDE | 0.924 ± 0.590 | 0.141 ± 0.101 | 0.275-2.312 | 16 |
最小凸多边形法 MCP | 0.902 ± 0.640 | 0.199 ± 0.192 | 0.255-2.747 | |||
完全出羽期 Fully-fledged period | 核密度分析法 KDE | 5.090 ± 4.756 | 0.602 ± 0.612 | 0.710-16.291 | 16 | |
最小凸多边形法 MCP | 9.510 ± 11.556 | 1.540 ± 2.232 | 0.605-36.707 | |||
无围栏 Non-fenced | 出羽后期 Post-fledging period | 核密度分析法 KDE | 2.483 ± 1.619 | 0.423 ± 0.294 | 1.316-4.878 | 4 |
最小凸多边形法 MCP | 2.701 ± 2.269 | 0.552 ± 0.348 | 1.214-6.803 | |||
完全出羽期 Fully-fledged period | 核密度分析法 KDE | 7.629 ± 3.857 | 1.183 ± 0.462 | 4.502-13.117 | 4 | |
最小凸多边形法 MCP | 14.551 ± 11.189 | 1.885 ± 0.777 | 3.852-40.213 |
表2 两种方法评估黑颈鹤幼鸟在有围栏与无围栏生境中家域和核域平均面积(km2)
Table 2 Average areas (km2) of black-necked crane juvenile’s home range and core area in fence habitat and non-fenced habitat
生境类型 Habitat type | 时期 Period | 方法 Method | 家域 Home range (km2) | 核域 Core area (km2) | 家域面积范围 Minimum to maximum (km2) | 样本量 Sample size |
---|---|---|---|---|---|---|
有围栏 Fence | 出羽后期 Post-fledging period | 核密度分析法 KDE | 0.924 ± 0.590 | 0.141 ± 0.101 | 0.275-2.312 | 16 |
最小凸多边形法 MCP | 0.902 ± 0.640 | 0.199 ± 0.192 | 0.255-2.747 | |||
完全出羽期 Fully-fledged period | 核密度分析法 KDE | 5.090 ± 4.756 | 0.602 ± 0.612 | 0.710-16.291 | 16 | |
最小凸多边形法 MCP | 9.510 ± 11.556 | 1.540 ± 2.232 | 0.605-36.707 | |||
无围栏 Non-fenced | 出羽后期 Post-fledging period | 核密度分析法 KDE | 2.483 ± 1.619 | 0.423 ± 0.294 | 1.316-4.878 | 4 |
最小凸多边形法 MCP | 2.701 ± 2.269 | 0.552 ± 0.348 | 1.214-6.803 | |||
完全出羽期 Fully-fledged period | 核密度分析法 KDE | 7.629 ± 3.857 | 1.183 ± 0.462 | 4.502-13.117 | 4 | |
最小凸多边形法 MCP | 14.551 ± 11.189 | 1.885 ± 0.777 | 3.852-40.213 |
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