生物多样性 ›› 2024, Vol. 32 ›› Issue (3): 23359. DOI: 10.17520/biods.2023359 cstr: 32101.14.biods.2023359
王鹏1,2,3, 隋佳容1, 丁欣瑶1, 王伟中1, 曹雪倩1, 赵海鹏1,4,*(), 王彦平5,*()()
收稿日期:
2023-09-26
接受日期:
2023-12-15
出版日期:
2024-03-20
发布日期:
2024-02-27
通讯作者:
*E-mail: hpzhao1980@qq.com;
wangyanping@njnu.edu.cn
基金资助:
Peng Wang1,2,3, Jiarong Sui1, Xinyao Ding1, Weizhong Wang1, Xueqian Cao1, Haipeng Zhao1,4,*(), Yanping Wang5,*()()
Received:
2023-09-26
Accepted:
2023-12-15
Online:
2024-03-20
Published:
2024-02-27
Contact:
*E-mail: hpzhao1980@qq.com;
wangyanping@njnu.edu.cn
摘要:
为了探究郑州城市公园鸟类群落是否符合嵌套分布格局及其影响因素, 本研究从中国观鸟记录中心收集了2019-2022年每年3-7月河南省郑州市15个城市公园的鸟类记录数据。使用WNODF (weighted nestedness metric based on overlap and decreasing fill)分别计算郑州城市公园全部鸟类、林鸟和水鸟群落的嵌套分布格局, 采用Spearman偏相关检验分析了公园嵌套序列与公园特征参数(公园面积、隔离度、生境类型数量和建筑指数)的关系, 以及物种嵌套序列与物种生态学特征(体长、地理分布范围、窝卵数和最小面积需求)的关系。WNODF分析结果显示, 郑州城市公园全部鸟类、林鸟和水鸟群落均是显著嵌套的。Spearman偏相关分析结果显示, 公园面积和最小面积需求与鸟类群落嵌套程度显著相关, 生境地点矩阵分析结果显示为显著嵌套, 建筑指数也会影响水鸟群落的嵌套分布格局, 但随机放置模型结果显示城市公园鸟类不符合被动取样假说。因此, 选择性灭绝与生境嵌套是郑州城市公园全部鸟类、林鸟和水鸟群落嵌套分布格局的主要驱动因素。研究结果表明, 为了更好地保护郑州城市公园的鸟类多样性, 应优先保护面积较大和生境类型多的公园, 以及最小面积需求大的鸟类; 同时由于水鸟与林鸟对城市化的反应不同, 在制定保护策略时应区别对待。
王鹏, 隋佳容, 丁欣瑶, 王伟中, 曹雪倩, 赵海鹏, 王彦平 (2024) 郑州城市公园鸟类群落嵌套分布格局及其影响因素. 生物多样性, 32, 23359. DOI: 10.17520/biods.2023359.
Peng Wang, Jiarong Sui, Xinyao Ding, Weizhong Wang, Xueqian Cao, Haipeng Zhao, Yanping Wang (2024) Nested distribution patterns of bird assemblages and their influencing factors in Zhengzhou urban parks. Biodiversity Science, 32, 23359. DOI: 10.17520/biods.2023359.
图1 郑州市15个城市公园的位置。XS: 须水河滨河公园; HH: 黄河滩; XL: 西流湖; JL: 贾鲁河公园; BS: 碧沙岗公园; ZD: 郑州大学; RM: 人民公园; DF: 东风渠; LH: 龙湖湿地; ZZ: 郑州之林; SX: 索须河; QL: 七里河; LZ: 龙子湖; XH: 象湖湿地; CH: 潮河湿地。
Fig. 1 The location of 15 urban parks in Zhengzhou City, China. XS, Xushui River Riverside Park; HH, Yellow River Beach; XL, Xiliu Lake; JL, Jialu River Park; BS, Bishagang Park; ZD, Zhengzhou University; RM, People’s Park; DF, Dongfeng River; LH, Longhu Wetland; ZZ, Zhengzhou Forest; SX, Suoxu River; QL, Qili River; LZ, Longzi Lake; XH, Xianghu Wetland; CH, Chaohe Wetland.
编号 Code | 名称 Name | 面积 Area (ha) | 隔离度1 Isolation 1 (m) | 隔离度2 Isolation 2 (m) | 生境类型 数量 No. of habitat types | 调查完整度 Survey completeness | 物种数 Species richness | 期望物 种数 Expected richness | 建筑指数 Building index | 全部鸟类 嵌套序列 Nested matrix rank of all birds | 林鸟嵌套 序列 Nested matrix rank of forest birds | 水鸟嵌套序列 Nested matrix rank of water birds |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | 须水河滨河公园 XS | 17.10 | 2,010 | 18,171 | 4 | 0.92 | 33 | 36.00 | 189 | 14 | 14 | 12 |
2 | 黄河滩 HH | 56.65 | 3,216 | 15,737 | 7 | 0.93 | 108 | 116.25 | 29 | 3 | 4 | 2 |
3 | 西流湖 XL | 60.22 | 3,792 | 11,547 | 7 | 0.86 | 134 | 156.67 | 173 | 1 | 1 | 3 |
4 | 贾鲁河公园 JL | 60.57 | 3,792 | 14,930 | 6 | 0.93 | 83 | 89.86 | 101 | 5 | 7 | 5 |
5 | 碧沙岗公园 BS | 21.71 | 3,792 | 8,994 | 7 | 0.99 | 55 | 54.46 | 204 | 11 | 6 | 15 |
6 | 郑州大学 ZD | 81.60 | 2,010 | 16,178 | 4 | 0.89 | 96 | 107.67 | 269 | 4 | 2 | 13 |
7 | 人民公园 RM | 11.26 | 3,202 | 5,893 | 6 | 0.88 | 37 | 44.50 | 259 | 13 | 12 | 14 |
8 | 东风渠 DF | 30.08 | 3,108 | 2,677 | 2 | 0.84 | 78 | 78.09 | 112 | 6 | 8 | 4 |
9 | 龙湖湿地 LH | 73.33 | 3,108 | 1,048 | 6 | 0.87 | 121 | 138.77 | 95 | 2 | 3 | 1 |
10 | 郑州之林 ZZ | 23.83 | 3,440 | 2,533 | 6 | 0.89 | 69 | 77.75 | 147 | 7 | 5 | 11 |
11 | 索须河 SX | 15.78 | 3,216 | 12,865 | 4 | 0.94 | 53 | 56.50 | 42 | 10 | 10 | 9 |
12 | 七里河 QL | 10.79 | 3,589 | 5,628 | 6 | 0.86 | 19 | 22.00 | 183 | 15 | 15 | 8 |
13 | 龙子湖 LZ | 28.11 | 4,788 | 8,184 | 9 | 0.91 | 56 | 61.50 | 266 | 9 | 11 | 6 |
14 | 象湖湿地 XH | 22.78 | 5,017 | 14,300 | 4 | 0.85 | 40 | 47.00 | 59 | 12 | 13 | 10 |
15 | 潮河湿地 CH | 3.70 | 16,142 | 21,427 | 5 | 0.97 | 68 | 70.33 | 67 | 8 | 9 | 7 |
表1 郑州市15个城市公园的生境变量与特征
Table 1 Habitat variables and characteristics of the 15 urban parks in Zhengzhou City, China
编号 Code | 名称 Name | 面积 Area (ha) | 隔离度1 Isolation 1 (m) | 隔离度2 Isolation 2 (m) | 生境类型 数量 No. of habitat types | 调查完整度 Survey completeness | 物种数 Species richness | 期望物 种数 Expected richness | 建筑指数 Building index | 全部鸟类 嵌套序列 Nested matrix rank of all birds | 林鸟嵌套 序列 Nested matrix rank of forest birds | 水鸟嵌套序列 Nested matrix rank of water birds |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | 须水河滨河公园 XS | 17.10 | 2,010 | 18,171 | 4 | 0.92 | 33 | 36.00 | 189 | 14 | 14 | 12 |
2 | 黄河滩 HH | 56.65 | 3,216 | 15,737 | 7 | 0.93 | 108 | 116.25 | 29 | 3 | 4 | 2 |
3 | 西流湖 XL | 60.22 | 3,792 | 11,547 | 7 | 0.86 | 134 | 156.67 | 173 | 1 | 1 | 3 |
4 | 贾鲁河公园 JL | 60.57 | 3,792 | 14,930 | 6 | 0.93 | 83 | 89.86 | 101 | 5 | 7 | 5 |
5 | 碧沙岗公园 BS | 21.71 | 3,792 | 8,994 | 7 | 0.99 | 55 | 54.46 | 204 | 11 | 6 | 15 |
6 | 郑州大学 ZD | 81.60 | 2,010 | 16,178 | 4 | 0.89 | 96 | 107.67 | 269 | 4 | 2 | 13 |
7 | 人民公园 RM | 11.26 | 3,202 | 5,893 | 6 | 0.88 | 37 | 44.50 | 259 | 13 | 12 | 14 |
8 | 东风渠 DF | 30.08 | 3,108 | 2,677 | 2 | 0.84 | 78 | 78.09 | 112 | 6 | 8 | 4 |
9 | 龙湖湿地 LH | 73.33 | 3,108 | 1,048 | 6 | 0.87 | 121 | 138.77 | 95 | 2 | 3 | 1 |
10 | 郑州之林 ZZ | 23.83 | 3,440 | 2,533 | 6 | 0.89 | 69 | 77.75 | 147 | 7 | 5 | 11 |
11 | 索须河 SX | 15.78 | 3,216 | 12,865 | 4 | 0.94 | 53 | 56.50 | 42 | 10 | 10 | 9 |
12 | 七里河 QL | 10.79 | 3,589 | 5,628 | 6 | 0.86 | 19 | 22.00 | 183 | 15 | 15 | 8 |
13 | 龙子湖 LZ | 28.11 | 4,788 | 8,184 | 9 | 0.91 | 56 | 61.50 | 266 | 9 | 11 | 6 |
14 | 象湖湿地 XH | 22.78 | 5,017 | 14,300 | 4 | 0.85 | 40 | 47.00 | 59 | 12 | 13 | 10 |
15 | 潮河湿地 CH | 3.70 | 16,142 | 21,427 | 5 | 0.97 | 68 | 70.33 | 67 | 8 | 9 | 7 |
编号 Code | 名称 Name | 建筑 Building | 稀疏树林 Sparse wood | 稠密树林 Dense wood | 池塘 Pond | 湖泊 Lake | 河流 River | 草地 Grassland | 道路设施 Road facility | 灌丛 Shrub | 空地 Bare ground |
---|---|---|---|---|---|---|---|---|---|---|---|
1 | 须水河滨河公园 XS | 0 | 1 | 0 | 0 | 1 | 0 | 0 | 1 | 0 | 1 |
2 | 黄河滩 HH | 0 | 1 | 1 | 0 | 0 | 1 | 1 | 1 | 1 | 1 |
3 | 西流湖 XL | 0 | 1 | 0 | 0 | 1 | 1 | 1 | 1 | 1 | 1 |
4 | 贾鲁河公园 JL | 1 | 1 | 0 | 0 | 0 | 1 | 1 | 1 | 0 | 1 |
5 | 碧沙岗公园 BS | 1 | 0 | 1 | 1 | 0 | 0 | 1 | 1 | 1 | 1 |
6 | 郑州大学 ZD | 1 | 1 | 0 | 0 | 0 | 1 | 1 | 0 | 0 | 0 |
7 | 人民公园 RM | 1 | 0 | 1 | 1 | 1 | 1 | 0 | 1 | 0 | 0 |
8 | 东风渠 DF | 0 | 0 | 1 | 0 | 0 | 1 | 0 | 0 | 0 | 0 |
9 | 龙湖湿地 LH | 0 | 0 | 1 | 1 | 1 | 0 | 1 | 1 | 0 | 1 |
10 | 郑州之林 ZZ | 0 | 1 | 1 | 0 | 0 | 1 | 1 | 1 | 1 | 0 |
11 | 索须河 SX | 1 | 1 | 0 | 0 | 0 | 1 | 0 | 1 | 0 | 0 |
12 | 七里河 QL | 0 | 1 | 0 | 0 | 0 | 1 | 1 | 1 | 1 | 1 |
13 | 龙子湖 LZ | 1 | 1 | 1 | 0 | 1 | 1 | 1 | 1 | 1 | 1 |
14 | 象湖湿地 XH | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 1 | 1 | 1 |
15 | 潮河湿地 CH | 0 | 1 | 0 | 1 | 0 | 1 | 1 | 0 | 1 | 0 |
表2 郑州市15个城市公园的生境地点矩阵
Table 2 Habitat-by-site matrix for birds in 15 urban parks in Zhengzhou City, China
编号 Code | 名称 Name | 建筑 Building | 稀疏树林 Sparse wood | 稠密树林 Dense wood | 池塘 Pond | 湖泊 Lake | 河流 River | 草地 Grassland | 道路设施 Road facility | 灌丛 Shrub | 空地 Bare ground |
---|---|---|---|---|---|---|---|---|---|---|---|
1 | 须水河滨河公园 XS | 0 | 1 | 0 | 0 | 1 | 0 | 0 | 1 | 0 | 1 |
2 | 黄河滩 HH | 0 | 1 | 1 | 0 | 0 | 1 | 1 | 1 | 1 | 1 |
3 | 西流湖 XL | 0 | 1 | 0 | 0 | 1 | 1 | 1 | 1 | 1 | 1 |
4 | 贾鲁河公园 JL | 1 | 1 | 0 | 0 | 0 | 1 | 1 | 1 | 0 | 1 |
5 | 碧沙岗公园 BS | 1 | 0 | 1 | 1 | 0 | 0 | 1 | 1 | 1 | 1 |
6 | 郑州大学 ZD | 1 | 1 | 0 | 0 | 0 | 1 | 1 | 0 | 0 | 0 |
7 | 人民公园 RM | 1 | 0 | 1 | 1 | 1 | 1 | 0 | 1 | 0 | 0 |
8 | 东风渠 DF | 0 | 0 | 1 | 0 | 0 | 1 | 0 | 0 | 0 | 0 |
9 | 龙湖湿地 LH | 0 | 0 | 1 | 1 | 1 | 0 | 1 | 1 | 0 | 1 |
10 | 郑州之林 ZZ | 0 | 1 | 1 | 0 | 0 | 1 | 1 | 1 | 1 | 0 |
11 | 索须河 SX | 1 | 1 | 0 | 0 | 0 | 1 | 0 | 1 | 0 | 0 |
12 | 七里河 QL | 0 | 1 | 0 | 0 | 0 | 1 | 1 | 1 | 1 | 1 |
13 | 龙子湖 LZ | 1 | 1 | 1 | 0 | 1 | 1 | 1 | 1 | 1 | 1 |
14 | 象湖湿地 XH | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 1 | 1 | 1 |
15 | 潮河湿地 CH | 0 | 1 | 0 | 1 | 0 | 1 | 1 | 0 | 1 | 0 |
图2 郑州市15个城市公园全部鸟类(A)、林鸟(B)和水鸟(C)的物种累积曲线
Fig. 2 Species accumulation curve for all birds (A), forest birds (B) and water birds (C) in 15 urban parks in Zhengzhou City, China
全部鸟类 All birds | 林鸟 Forest birds | 水鸟 Water birds | 栖息地 Habitat | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
观测值Observed | 期望值Expected | P | 观测值Observed | 期望值Expected | P | 观测值Observed | 期望值Expected | P | 观测值Observed | 期望值Expected | P | |
NODF | 51.02 | 76.97 | < 0.001 | 58.10 | 80.09 | < 0.001 | 48.28 | 86.79 | < 0.001 | 59.27 | 21.47 | < 0.001 |
NODFc | 63.66 | 93.68 | < 0.001 | 61.61 | 94.26 | < 0.001 | 68.87 | 92.88 | < 0.001 | 57.48 | 19.81 | < 0.005 |
NODFr | 50.97 | 76.91 | < 0.001 | 58.06 | 79.95 | < 0.001 | 47.30 | 86.51 | < 0.001 | 63.45 | 25.32 | < 0.001 |
WNODF | 33.93 | 68.27 | < 0.001 | 40.67 | 71.31 | < 0.001 | 29.83 | 74.57 | < 0.001 | |||
WNODFc | 41.18 | 80.50 | < 0.001 | 41.97 | 83.33 | < 0.001 | 44.46 | 82.95 | < 0.001 | |||
WNODFr | 33.91 | 68.23 | < 0.001 | 40.66 | 71.20 | < 0.001 | 29.14 | 74.21 | < 0.001 |
表3 NODF软件对郑州市城市公园全部鸟类、林鸟、水鸟群落多度地点矩阵和栖息地地点矩阵嵌套分析的结果
Table 3 Results of nestedness analyses using the software NODF conducted on the species-site abundance matrix for all birds, forest birds and water birds and the habitat-site matrix on 15 urban parks in Zhengzhou City, China
全部鸟类 All birds | 林鸟 Forest birds | 水鸟 Water birds | 栖息地 Habitat | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
观测值Observed | 期望值Expected | P | 观测值Observed | 期望值Expected | P | 观测值Observed | 期望值Expected | P | 观测值Observed | 期望值Expected | P | |
NODF | 51.02 | 76.97 | < 0.001 | 58.10 | 80.09 | < 0.001 | 48.28 | 86.79 | < 0.001 | 59.27 | 21.47 | < 0.001 |
NODFc | 63.66 | 93.68 | < 0.001 | 61.61 | 94.26 | < 0.001 | 68.87 | 92.88 | < 0.001 | 57.48 | 19.81 | < 0.005 |
NODFr | 50.97 | 76.91 | < 0.001 | 58.06 | 79.95 | < 0.001 | 47.30 | 86.51 | < 0.001 | 63.45 | 25.32 | < 0.001 |
WNODF | 33.93 | 68.27 | < 0.001 | 40.67 | 71.31 | < 0.001 | 29.83 | 74.57 | < 0.001 | |||
WNODFc | 41.18 | 80.50 | < 0.001 | 41.97 | 83.33 | < 0.001 | 44.46 | 82.95 | < 0.001 | |||
WNODFr | 33.91 | 68.23 | < 0.001 | 40.66 | 71.20 | < 0.001 | 29.14 | 74.21 | < 0.001 |
生境变量 Habitat variable | 物种生态学特征 Species ecological traits | ||||||||
---|---|---|---|---|---|---|---|---|---|
面积 Area (ha) | 隔离度1 Isolation 1 (m) | 隔离度2 Isolation 2 (m) | 生境类型的数量 No. of habitat types | 建筑指数Building index | 体长 Body length (mm) | 地理分布范围Geographic range size (km2) | 窝卵数Clutch size | 最小面积需求Minimum area requirement (ha) | |
全部鸟类 All birds | -0.909** | -0.600 | 0.446 | -0.112 | 0.428 | -0.093 | -0.055 | 0.095 | 0.735** |
林鸟 Forest birds | -0.817* | -0.386 | 0.293 | -0.100 | 0.081 | -0.135 | -0.109 | 0.042 | 0.739** |
水鸟 Water birds | -0.609* | -0.325 | 0.427 | -0.323 | 0.650* | -0.049 | -0.164 | 0.192 | 0.664** |
表4 NODF软件重排后地点的嵌套序列与生境变量的Spearman偏相关分析结果以及NODF软件重排后物种的嵌套序列与物种生态学特征的Spearman偏相关分析结果
Table 4 Results of partial Spearman rank correlations between rank orders of sites and species in the maximally nested matrix using the software NODF and orders of sites and species after rearranging the matrix according to each explanatory variable
生境变量 Habitat variable | 物种生态学特征 Species ecological traits | ||||||||
---|---|---|---|---|---|---|---|---|---|
面积 Area (ha) | 隔离度1 Isolation 1 (m) | 隔离度2 Isolation 2 (m) | 生境类型的数量 No. of habitat types | 建筑指数Building index | 体长 Body length (mm) | 地理分布范围Geographic range size (km2) | 窝卵数Clutch size | 最小面积需求Minimum area requirement (ha) | |
全部鸟类 All birds | -0.909** | -0.600 | 0.446 | -0.112 | 0.428 | -0.093 | -0.055 | 0.095 | 0.735** |
林鸟 Forest birds | -0.817* | -0.386 | 0.293 | -0.100 | 0.081 | -0.135 | -0.109 | 0.042 | 0.739** |
水鸟 Water birds | -0.609* | -0.325 | 0.427 | -0.323 | 0.650* | -0.049 | -0.164 | 0.192 | 0.664** |
图3 郑州市城市公园全部鸟类(A)、林鸟(B)和水鸟(C)群落随机放置模型的观测值与期望值比较。期望值(实线)和标准差(±1SD; 虚线)。黑色圆点代表观察到的物种丰富度。
Fig. 3 Comparison of observed data to expected values under the random placement models for all birds (A), forest birds (B) and waterbirds (C) in 15 urban parks in Zhengzhou City, China. Expected values (solid line) and associated standard deviations (±1SD; dashed lines) are shown. The black dots represent observed species richness.
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