
生物多样性 ›› 2025, Vol. 33 ›› Issue (12): 25265. DOI: 10.17520/biods.2025265 cstr: 32101.14.biods.2025265
汪锦辉1, 刘宝权1, 周晓2, 梁子安2, 孔令伟3, 方卫军4, 孙晗靖5, 金挺浩1(
), 厉亮6, 何珂7,*(
)(
), 朱振贤1,*(
)
收稿日期:2025-07-10
接受日期:2025-10-11
出版日期:2025-12-20
发布日期:2026-01-09
通讯作者:
* 共同通讯作者:E-mail: heke@zafu.edu.cn;
sinpig@163.com
基金资助:
Jinhui Wang1, Baoquan Liu1, Xiao Zhou2, Zi’an Liang2, Lingwei Kong3, Weijun Fang4, Hanjing Sun5, Tinghao Jin1(
), Liang Li6, Ke He7,*(
)(
), Zhenxian Zhu1,*(
)
Received:2025-07-10
Accepted:2025-10-11
Online:2025-12-20
Published:2026-01-09
Supported by:摘要:
了解区域内物种的空间分布格局和种群数量, 是制定科学有效保护策略的关键依据, 城市生物多样性更是城市自然生产力和生态系统稳定的重要基础。本研究基于杭州市全域红外相机监测数据, 系统分析区域内物种的空间分布格局, 利用随机相遇模型估算种群密度, 占域模型评价栖息地利用影响生态因素, Zonation评估杭州市珍稀濒危物种保护优先区。结果显示: (1)共记录到147个物种, 包括兽类7目18科30种, 鸟类11目36科117种, 其中兽类以小麂(Muntiacus reevesi)、花面狸(Paguma larvata)、鼬獾(Melogale moschata)和猪獾(Arctonyx collaris)数量较高, 鸟类则以白鹇(Lophura nycthemera)数量最高。(2)物种多样性空间分布呈现明显异质性, 临安和淳安是重点保护物种的主要分布区, 黑麂(Muntiacus crinifrons)、中华鬣羚(Capricornis milneedwardsii)等珍稀物种集中分布于此, 而梅花鹿(Cervus nippon)仅见于临安的自然保护区内; 淳安发现了具有重要生态意义的豹猫(Prionailurus bengalensis)种群, 余杭区则分布有貉(Nyctereutes procyonoides)和亚洲狗獾(Meles leucurus)等适应城市周边生态系统的食肉目物种。(3)对于广泛分布的物种, 海拔是影响其在杭州市分布的重要因素。(4)基于红外相机监测到的小型兽类和地栖性鸟类数据, 系统评估识别出优先区总面积5,068.85 km2; 现有自然保护地有54.3%位于该30%优先区内, 覆盖了目标优先区的20.74%, 主要为国家级保护体系(天目山国家级自然保护区、清凉峰国家级自然保护区和富春江-新安江国家级风景名胜区)。在淳安西部和西北部的山区、萧山湘湖、临安岛石镇和清凉峰镇及桐庐百江镇山区存在保护空缺。这些发现为优化杭州市生物多样性保护网络、完善保护地体系建设提供了科学依据, 特别是对临安和淳安等关键区域的保护管理具有重要指导意义。
汪锦辉, 刘宝权, 周晓, 梁子安, 孔令伟, 方卫军, 孙晗靖, 金挺浩, 厉亮, 何珂, 朱振贤 (2025) 基于红外相机监测的杭州市鸟兽多样性分析与优先保护关键区域评估. 生物多样性, 33, 25265. DOI: 10.17520/biods.2025265.
Jinhui Wang, Baoquan Liu, Xiao Zhou, Zi’an Liang, Lingwei Kong, Weijun Fang, Hanjing Sun, Tinghao Jin, Liang Li, Ke He, Zhenxian Zhu (2025) Analyzing bird and mammal diversity and identifying key protection zones in Hangzhou based on infrared camera traps. Biodiversity Science, 33, 25265. DOI: 10.17520/biods.2025265.
| 调查区域 Region | 实施时间 Monitoring period (year) | 样区网格划分 Grid-based sampling (km × km) | 红外相机数 Number of infrared camera | 有效相机日 Effective camera-day (day) | 抽样 Sampling | 采样饱和度 Sampling saturation (%) |
|---|---|---|---|---|---|---|
| 临安区 Lin’an District | 2021-2023 | 2 × 2 | 204 | 63,940 | 按25%网格抽样调查 Sampling 25% of the grid | 89.3 |
| 桐庐县 Tonglu County | 2023-2024 | 3 × 3 | 197 | 65,207 | 全查 All | 97.1 |
| 萧山区 Xiaoshan District | 2023-2024 | 3 × 3 | 49 | 16,225 | 全查 All | 89.5 |
| 主城区 Urban area | 2023-2025 | 3 × 3 | 25 | 9,250 | 全查 All | 100 |
| 淳安县 Chun’an County | 2023-2025 | 3 × 3 | 426 | 148,758 | 全查 All | 98.0 |
| 余杭区 Yuhang District | 2022-2023 | 2 × 2 | 100 | 41,250 | 按25%网格抽样调查 Sampling 25% of the grid | 97.3 |
| 富阳区 Fuyang District | 2023-2024 | 3 × 3 | 120 | 47,400 | 全查 All | 93.8 |
| 建德市 Jiande City | 2021-2023 | 未划网格 Undefined | 103 | 36,720 | 无固定方法 Undefined | |
表1 杭州市红外相机布设和调查情况
Table 1 Camera-trapping deployment and survey parameters in Hangzhou City
| 调查区域 Region | 实施时间 Monitoring period (year) | 样区网格划分 Grid-based sampling (km × km) | 红外相机数 Number of infrared camera | 有效相机日 Effective camera-day (day) | 抽样 Sampling | 采样饱和度 Sampling saturation (%) |
|---|---|---|---|---|---|---|
| 临安区 Lin’an District | 2021-2023 | 2 × 2 | 204 | 63,940 | 按25%网格抽样调查 Sampling 25% of the grid | 89.3 |
| 桐庐县 Tonglu County | 2023-2024 | 3 × 3 | 197 | 65,207 | 全查 All | 97.1 |
| 萧山区 Xiaoshan District | 2023-2024 | 3 × 3 | 49 | 16,225 | 全查 All | 89.5 |
| 主城区 Urban area | 2023-2025 | 3 × 3 | 25 | 9,250 | 全查 All | 100 |
| 淳安县 Chun’an County | 2023-2025 | 3 × 3 | 426 | 148,758 | 全查 All | 98.0 |
| 余杭区 Yuhang District | 2022-2023 | 2 × 2 | 100 | 41,250 | 按25%网格抽样调查 Sampling 25% of the grid | 97.3 |
| 富阳区 Fuyang District | 2023-2024 | 3 × 3 | 120 | 47,400 | 全查 All | 93.8 |
| 建德市 Jiande City | 2021-2023 | 未划网格 Undefined | 103 | 36,720 | 无固定方法 Undefined | |
| 序号 No. | 物种 Species | 保护等级 Protect level | 独立照片数 Independent detections | 网格占有率 Grid occupancy (%) | 点位数量 Number of record sites | 全域RAI Region-wide relative abundance index | 调查区域种群密度和95%置信 区间 Population density with 95% confidence interval (ind./km2) | 变异系数 Coefficient of variation (%) |
|---|---|---|---|---|---|---|---|---|
| 1 | 猕猴 Macaca mulatta | II | 80 | 2.43 | 27 | 7.01 | 0.20 (0.17-0.25) | 38.93 |
| 2 | 马来豪猪 Hystrix brachyura | ZJ | 136 | 2.43 | 27 | 7.01 | 0.54 (0.42-0.70) | 52.59 |
| 3 | 毛冠鹿 Elaphodus cephalophus | II | 9 | 0.36 | 4 | 1.04 | 点位过少未计算 Insufficient number of points for calculation | |
| 4 | 黑麂 Muntiacus crinifrons | I | 206 | 2.96 | 33 | 8.57 | 0.76 (0.70-0.83) | 16.27 |
| 5 | 梅花鹿 Cervus nippon | I | 4 | 0.36 | 4 | 1.04 | 点位过少未计算 Insufficient number of points for calculation | |
| 6 | 中华鬣羚 Capricornis milneedwardsii | II | 55 | 2.79 | 31 | 8.05 | 0.22 (0.20-0.24) | 16.27 |
| 7 | 中华穿山甲 Manis pentadactyla | I | 3 | 0.27 | 3 | 0.78 | 点位过少未计算 Insufficient number of points for calculation | |
| 8 | 豹猫 Prionailurus bengalensis | II | 380 | 10.33 | 115 | 29.87 | 0.32 (0.25-0.41) | 48.98 |
| 9 | 花面狸 Paguma larvata | ZJ | 2,868 | 56.51 | 629 | 163.38 | 0.53 (0.49-0.57) | 15.22 |
| 10 | 食蟹獴 Herpestes urva | ZJ | 49 | 1.98 | 22 | 5.71 | 0.26 (0.24-0.28) | 15.22 |
| 11 | 貉 Nyctereutes procyonoides | II | 94 | 1.26 | 14 | 3.64 | 0.78 (0.72-0.84) | 15.22 |
| 12 | 黄腹鼬 Mustela kathiah | ZJ | 192 | 11.23 | 125 | 32.47 | 0.18 (0.17-0.19) | 15.22 |
| 13 | 黄鼬 Mustela sibirica | ZJ | 197 | 8.54 | 95 | 24.68 | 0.24 (0.22-0.26) | 15.22 |
| 14 | 鼬獾 Melogale moschata | ZJ | 3,175 | 48.97 | 545 | 141.56 | 0.68 (0.63-0.73) | 15.22 |
| 15 | 亚洲狗獾 Meles leucurus | ZJ | 130 | 1.53 | 17 | 4.42 | 0.89 (0.83-0.96) | 15.22 |
| 16 | 猪獾 Arctonyx collaris | ZJ | 2,717 | 61.01 | 679 | 176.36 | 0.47 (0.43-0.50) | 15.22 |
| 17 | 勺鸡 Pucrasia macrolopha | II | 421 | 17.43 | 194 | 50.39 | 1.51 (1.27-1.82) | 36.73 |
| 18 | 白颈长尾雉 Syrmaticus ellioti | I | 321 | 16.26 | 181 | 47.01 | 1.24 (1.04-1.49) | 36.73 |
| 19 | 白鹇 Lophura nycthemera | II | 15,327 | 81.31 | 905 | 235.06 | 11.81 (9.88-14.22) | 36.73 |
表2 重点监测物种相关数据
Table 2 Data summary of focal monitoring species
| 序号 No. | 物种 Species | 保护等级 Protect level | 独立照片数 Independent detections | 网格占有率 Grid occupancy (%) | 点位数量 Number of record sites | 全域RAI Region-wide relative abundance index | 调查区域种群密度和95%置信 区间 Population density with 95% confidence interval (ind./km2) | 变异系数 Coefficient of variation (%) |
|---|---|---|---|---|---|---|---|---|
| 1 | 猕猴 Macaca mulatta | II | 80 | 2.43 | 27 | 7.01 | 0.20 (0.17-0.25) | 38.93 |
| 2 | 马来豪猪 Hystrix brachyura | ZJ | 136 | 2.43 | 27 | 7.01 | 0.54 (0.42-0.70) | 52.59 |
| 3 | 毛冠鹿 Elaphodus cephalophus | II | 9 | 0.36 | 4 | 1.04 | 点位过少未计算 Insufficient number of points for calculation | |
| 4 | 黑麂 Muntiacus crinifrons | I | 206 | 2.96 | 33 | 8.57 | 0.76 (0.70-0.83) | 16.27 |
| 5 | 梅花鹿 Cervus nippon | I | 4 | 0.36 | 4 | 1.04 | 点位过少未计算 Insufficient number of points for calculation | |
| 6 | 中华鬣羚 Capricornis milneedwardsii | II | 55 | 2.79 | 31 | 8.05 | 0.22 (0.20-0.24) | 16.27 |
| 7 | 中华穿山甲 Manis pentadactyla | I | 3 | 0.27 | 3 | 0.78 | 点位过少未计算 Insufficient number of points for calculation | |
| 8 | 豹猫 Prionailurus bengalensis | II | 380 | 10.33 | 115 | 29.87 | 0.32 (0.25-0.41) | 48.98 |
| 9 | 花面狸 Paguma larvata | ZJ | 2,868 | 56.51 | 629 | 163.38 | 0.53 (0.49-0.57) | 15.22 |
| 10 | 食蟹獴 Herpestes urva | ZJ | 49 | 1.98 | 22 | 5.71 | 0.26 (0.24-0.28) | 15.22 |
| 11 | 貉 Nyctereutes procyonoides | II | 94 | 1.26 | 14 | 3.64 | 0.78 (0.72-0.84) | 15.22 |
| 12 | 黄腹鼬 Mustela kathiah | ZJ | 192 | 11.23 | 125 | 32.47 | 0.18 (0.17-0.19) | 15.22 |
| 13 | 黄鼬 Mustela sibirica | ZJ | 197 | 8.54 | 95 | 24.68 | 0.24 (0.22-0.26) | 15.22 |
| 14 | 鼬獾 Melogale moschata | ZJ | 3,175 | 48.97 | 545 | 141.56 | 0.68 (0.63-0.73) | 15.22 |
| 15 | 亚洲狗獾 Meles leucurus | ZJ | 130 | 1.53 | 17 | 4.42 | 0.89 (0.83-0.96) | 15.22 |
| 16 | 猪獾 Arctonyx collaris | ZJ | 2,717 | 61.01 | 679 | 176.36 | 0.47 (0.43-0.50) | 15.22 |
| 17 | 勺鸡 Pucrasia macrolopha | II | 421 | 17.43 | 194 | 50.39 | 1.51 (1.27-1.82) | 36.73 |
| 18 | 白颈长尾雉 Syrmaticus ellioti | I | 321 | 16.26 | 181 | 47.01 | 1.24 (1.04-1.49) | 36.73 |
| 19 | 白鹇 Lophura nycthemera | II | 15,327 | 81.31 | 905 | 235.06 | 11.81 (9.88-14.22) | 36.73 |
图1 杭州市红外相机点位监测动物物种数量(A)和保护价值量化值(B)。为减少不同区域调查的差异, 仅采用部分兽类(排除鼠类和松鼠类)和鸟类中的地栖性鸟类(鸡形目)。
Fig. 1 Species richness (A) and quantified conservation value (B) based on infrared camera monitoring in Hangzhou City. Only species of certain mammals (excluding rodents and squirrels) and Galliformes were included (B).
图2 杭州市不同行政区划的物种数量(A)、Shannon指数(B)和保护价值量化值(C)在保护区内外的比较。P为FDR校正后数值, * P < 0.05, ** P < 0.01。Cliff δ值为可忽略(|δ| < 0.147)和小效应(|δ| < 0.330)的未列出。
Fig. 2 Comparisons between protected and unprotected areas in Hangzhou for species richness (A), Shannon index (B), and protection value (C) across different regions. P-values were adjusted using FDR correction. * P < 0.05, ** P < 0.01. Cliff δ values indicating negligible effect (|δ| < 0.147) or small effect (|δ| < 0.330) are not shown.
图3 杭州市不同区域的物种丰富度(物种数量)、生物多样性指数(Shannon指数)、保护价值量化值3个参数前10%的点位分布情况(A)和重点保护物种分布点位受保护情况(B)
Fig. 3 Spatial distribution of top 10% sampling sites for three parameters: species richness (number of species), biodiversity index (Shannon index), and protection value in Hangzhou (A) and protection status of key species occurrence sites across different regions (B)
| 序号 No. | 物种 Species | 估计占域率ψ及范围 Estimated occupancy rate (ψ) and range | 探测率 Detection probability (p) | 模型选择 Model | 影响是否显著 Significance |
|---|---|---|---|---|---|
| 1 | 猕猴 Macaca mulatta | 0.034 (0.026-0.052) | 0.079 | 海拔 Elevation | |
| 2 | 马来豪猪 Hystrix brachyura | 0.035 (0.020-0.081) | 0.272 | 海拔 Elevation | ** |
| 4 | 黑麂 Muntiacus crinifrons | 0.033 (0.021-0.040) | 0.109 | 海拔 Elevation | |
| 6 | 中华鬣羚 Capricornis milneedwardsii | 0.051 (0.037-0.088) | 0.031 | 海拔 Elevation | |
| 8 | 豹猫 Prionailurus bengalensis | 0.122 (0.090-0.211) | 0.065 | 海拔 + NDVI Elevation + NDVI | 海拔 Elevation* |
| 9 | 花面狸 Paguma larvata | 0.633 (0.595-0.657) | 0.050 | 道路 Road | |
| 10 | 食蟹獴 Herpestes urva | 0.025 (0.017-0.057) | 0.102 | NDVI | * |
| 11 | 貉 Nyctereutes procyonoides | 0.015 (0.000-0.052) | 0.125 | 海拔 + 道路 Elevation + Road | 海拔 Elevation**, 道路 Road*** |
| 12 | 黄腹鼬 Mustela kathiah | 0.256 (0.142-0.373) | 0.020 | 海拔 + NDVI Elevation + NDVI | |
| 13 | 黄鼬 Mustela sibirica | 0.157 (0.123-0.169) | 0.026 | 三者单因子无差异 No difference between three factors | |
| 14 | 鼬獾 Melogale moschata | 0.550 (0.512-0.622) | 0.046 | 海拔 Elevation | |
| 15 | 亚洲狗獾 Meles leucurus | 0.023 (0.017-0.042) | 0.057 | NDVI | |
| 16 | 猪獾 Arctonyx collaris | 0.742 (0.717-0.813) | 0.040 | 道路 Road | |
| 17 | 勺鸡 Pucrasia macrolopha | 0.263 (0.189-0.292) | 0.029 | NDVI | |
| 18 | 白颈长尾雉 Syrmaticus ellioti | 0.345 (0.265-0.516) | 0.021 | 海拔 Elevation | * |
| 19 | 白鹇 Lophura nycthemera | 1.000 | 0.068 | ΔAICc > 2 | |
表3 占域模型分析结果
Table 3 Results of occupancy model analysis
| 序号 No. | 物种 Species | 估计占域率ψ及范围 Estimated occupancy rate (ψ) and range | 探测率 Detection probability (p) | 模型选择 Model | 影响是否显著 Significance |
|---|---|---|---|---|---|
| 1 | 猕猴 Macaca mulatta | 0.034 (0.026-0.052) | 0.079 | 海拔 Elevation | |
| 2 | 马来豪猪 Hystrix brachyura | 0.035 (0.020-0.081) | 0.272 | 海拔 Elevation | ** |
| 4 | 黑麂 Muntiacus crinifrons | 0.033 (0.021-0.040) | 0.109 | 海拔 Elevation | |
| 6 | 中华鬣羚 Capricornis milneedwardsii | 0.051 (0.037-0.088) | 0.031 | 海拔 Elevation | |
| 8 | 豹猫 Prionailurus bengalensis | 0.122 (0.090-0.211) | 0.065 | 海拔 + NDVI Elevation + NDVI | 海拔 Elevation* |
| 9 | 花面狸 Paguma larvata | 0.633 (0.595-0.657) | 0.050 | 道路 Road | |
| 10 | 食蟹獴 Herpestes urva | 0.025 (0.017-0.057) | 0.102 | NDVI | * |
| 11 | 貉 Nyctereutes procyonoides | 0.015 (0.000-0.052) | 0.125 | 海拔 + 道路 Elevation + Road | 海拔 Elevation**, 道路 Road*** |
| 12 | 黄腹鼬 Mustela kathiah | 0.256 (0.142-0.373) | 0.020 | 海拔 + NDVI Elevation + NDVI | |
| 13 | 黄鼬 Mustela sibirica | 0.157 (0.123-0.169) | 0.026 | 三者单因子无差异 No difference between three factors | |
| 14 | 鼬獾 Melogale moschata | 0.550 (0.512-0.622) | 0.046 | 海拔 Elevation | |
| 15 | 亚洲狗獾 Meles leucurus | 0.023 (0.017-0.042) | 0.057 | NDVI | |
| 16 | 猪獾 Arctonyx collaris | 0.742 (0.717-0.813) | 0.040 | 道路 Road | |
| 17 | 勺鸡 Pucrasia macrolopha | 0.263 (0.189-0.292) | 0.029 | NDVI | |
| 18 | 白颈长尾雉 Syrmaticus ellioti | 0.345 (0.265-0.516) | 0.021 | 海拔 Elevation | * |
| 19 | 白鹇 Lophura nycthemera | 1.000 | 0.068 | ΔAICc > 2 | |
图4 杭州市基于红外相机监测的目标优先区与现有自然保护地空间布局
Fig. 4 Spatial layout of target priority areas based on infrared camera monitoring and natural protected areas in Hangzhou City
| 已建保护体系 Established protection system | 总面积 Area (km2) | 30%目标区域 30% of the target area | 20%目标区域 20% of the target area | 10%目标区域 10% of the target area | |||
|---|---|---|---|---|---|---|---|
| 面积 Area | 占比 Proportion (%) | 面积 Area | 占比 Proportion (%) | 面积 Area | 占比 Proportion (%) | ||
| 天目山国家级自然保护区 Tianmu Mountain National Nature Reserve | 42.8 | 39.7 | 92.8 | 39.4 | 92.2 | 38.6 | 90.1 |
| 清凉峰国家级自然保护区 Qingliangfeng National Nature Reserve | 112.5 | 92.6 | 82.3 | 87.4 | 77.7 | 42.1 | 37.4 |
| 富春江-新安江国家级风景名胜区* Fuchun River-Xin’an River National Scenic Area | 1,339.6 | 853.5 | 63.7 | 525.8 | 39.3 | 359.1 | 26.8 |
| 大明山省级地质公园 Daming Mountain Provincial Geological Park | 30.3 | 26.3 | 86.9 | 11.0 | 36.2 | - | - |
| 昌化省级森林公园 Changhua Provincial Forest Park | 22.9 | 18.5 | 80.4 | 18.2 | 79.3 | 14.4 | 62.5 |
| 太湖源风景区 Taihuyuan Scenic Area | 115.2 | 15.3 | 13.3 | 4.8 | 4.1 | 6.3 | 5.4 |
| 全部保护地体系* Entire protected area system | 1,925.2 | 1,045.9 | 54.3 | 686.6 | 35.7 | 460.4 | 23.9 |
表4 杭州市已建保护体系在目标区域的占比情况。在30%目标区域中占比未超过5%的保护地体系未列出。
Table 4 Proportion of the established protection system in the target area of Hangzhou City. Regions covering less than 5% of any 30% target region are excluded from the list.
| 已建保护体系 Established protection system | 总面积 Area (km2) | 30%目标区域 30% of the target area | 20%目标区域 20% of the target area | 10%目标区域 10% of the target area | |||
|---|---|---|---|---|---|---|---|
| 面积 Area | 占比 Proportion (%) | 面积 Area | 占比 Proportion (%) | 面积 Area | 占比 Proportion (%) | ||
| 天目山国家级自然保护区 Tianmu Mountain National Nature Reserve | 42.8 | 39.7 | 92.8 | 39.4 | 92.2 | 38.6 | 90.1 |
| 清凉峰国家级自然保护区 Qingliangfeng National Nature Reserve | 112.5 | 92.6 | 82.3 | 87.4 | 77.7 | 42.1 | 37.4 |
| 富春江-新安江国家级风景名胜区* Fuchun River-Xin’an River National Scenic Area | 1,339.6 | 853.5 | 63.7 | 525.8 | 39.3 | 359.1 | 26.8 |
| 大明山省级地质公园 Daming Mountain Provincial Geological Park | 30.3 | 26.3 | 86.9 | 11.0 | 36.2 | - | - |
| 昌化省级森林公园 Changhua Provincial Forest Park | 22.9 | 18.5 | 80.4 | 18.2 | 79.3 | 14.4 | 62.5 |
| 太湖源风景区 Taihuyuan Scenic Area | 115.2 | 15.3 | 13.3 | 4.8 | 4.1 | 6.3 | 5.4 |
| 全部保护地体系* Entire protected area system | 1,925.2 | 1,045.9 | 54.3 | 686.6 | 35.7 | 460.4 | 23.9 |
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