生物多样性 ›› 2022, Vol. 30 ›› Issue (6): 21424. DOI: 10.17520/biods.2021424
田璐嘉, 杨小波(), 李东海, 李龙, 陈琳, 梁彩群, 张培春, 李晨笛
收稿日期:
2021-10-25
接受日期:
2022-02-10
出版日期:
2022-06-20
发布日期:
2022-02-28
通讯作者:
杨小波
作者简介:
* E-mail: yanfengxb@163.com基金资助:
Lujia Tian, Xiaobo Yang(), Donghai Li, Long Li, Lin Chen, Caiqun Liang, Peichun Zhang, Chendi Li
Received:
2021-10-25
Accepted:
2022-02-10
Online:
2022-06-20
Published:
2022-02-28
Contact:
Xiaobo Yang
摘要:
城市化是生物多样性快速丧失的主要原因之一。鸟类作为城市生态系统的重要组成部分, 其生物多样性格局和物种保护已成为城市生态学研究的热点。为揭示城市化过程中城区和郊区破碎化林地中鸟类群落的多样性差异和嵌套格局, 本研究于2021年春、夏季鸟类繁殖期采用样线法对海口和三亚市的城区、郊区共13个林地斑块中的鸟类群落进行调查。使用NODF (nestedness metric based on overlap and decreasing fill)和WNODF (weighted nestedness metric based on overlap and decreasing fill)方法进行嵌套格局分析。研究发现: (1)共记录到林鸟100种, 隶属于11目39科, 其中三亚郊区的鸟类丰富度最高, 共8目29科68种。记录到国家重点保护鸟类共18种, 其中两城市郊区的国家重点保护鸟类物种数均多于城区, 海口郊区还记录到国家I级重点保护鸟类黄胸鹀(Emberiza aureola)。(2)鸟类群落多度、物种丰富度、Pielou均匀度指数和Shannon-Wiener多样性指数在不同区域中均存在差异。海口城区的鸟类群落多度显著高于海口郊区(P < 0.05), 三亚郊区的鸟类群落物种丰富度、Pielou均匀度指数和Shannon-Wiener多样性指数均显著高于三亚城区和海口郊区(P < 0.05)。(3)嵌套分析结果表明, 海口和三亚市的城区、郊区林地鸟类群落均呈现反嵌套分布格局。线性回归分析显示, 三亚市城区和郊区的斑块面积与鸟类物种丰富度呈显著正相关, 而物种丰富度与斑块距最近大面积林地的距离之间无显著相关性。研究表明, 两城市鸟类群落多样性都表现出郊区高于城区的特点, 少数优势种(如白头鹎 Pycnonotus sinensis)占据了城市中的主要生态位。受城市化的影响, 海口郊区与城区鸟类群落有同质化的趋势。鸟类在城区和郊区斑块间的高流动性、种间竞争和斑块中资源的可利用性等因素可能导致斑块间鸟类群落的反嵌套分布格局。我们建议应加强城区和郊区鸟类的保护, 减少对林地的破坏, 提高城市鸟类多样性。
田璐嘉, 杨小波, 李东海, 李龙, 陈琳, 梁彩群, 张培春, 李晨笛 (2022) 海口和三亚两城市破碎化林地中鸟类群落多样性与嵌套分布格局. 生物多样性, 30, 21424. DOI: 10.17520/biods.2021424.
Lujia Tian, Xiaobo Yang, Donghai Li, Long Li, Lin Chen, Caiqun Liang, Peichun Zhang, Chendi Li (2022) Species diversity and nestedness of bird assemblages in the forest fragments of Haikou and Sanya cities. Biodiversity Science, 30, 21424. DOI: 10.17520/biods.2021424.
图1 研究区域的位置和编号。1-13代表各林地斑块的编号(1-3: 海口城区; 4-7: 海口郊区; 8-10: 三亚城区; 11-13: 三亚郊区)。
Fig. 1 The location and number of the study regions. 1-13 represent the number of the fragmented woodlot (1-3, Haikou urban; 4-7, Haikou suburb; 8-10, Sanya urban; 11-13: Sanya suburb).
图3 不同区域间鸟类群落多度、物种丰富度、Pielou均匀度指数和Shannon-Wiener多样性指数的差异。* P < 0.05; ** P < 0.01。
Fig. 3 The differences in the abundance, species richness, Pielou evenness index and Shannon-Wiener diversity index of bird communities in different regions. * P < 0.05; ** P < 0.01.
图4 海口和三亚城区和郊区各林地斑块中记录到的鸟类数量(前10名)
Fig. 4 The number of individuals of the recorded bird species in each fragmented woodlots of Haikou and Sanya cities’ urban and suburb (top 10)
区域 Sites | 嵌套度量化 Nestedness metric | 观测值 Observed | 期望值 Expected | 标准差 SD | Z | P |
---|---|---|---|---|---|---|
海口市 Haikou | 零模型 Null model: pp | |||||
NODF | 52.38 | 54.89 | 2.19 | -1.14 | 0.13 | |
NODFc | 60.85 | 67.81 | 4.57 | -1.52 | 0.06 | |
NODFr | 52.30 | 54.76 | 2.18 | -1.13 | 0.13 | |
零模型 Null model: rc | ||||||
WNODF | 34.14 | 54.23 | 1.92 | -10.49 | < 0.001 | |
WNODFc | 32.86 | 61.34 | 4.37 | -6.51 | < 0.001 | |
WNODFr | 34.16 | 54.19 | 1.91 | -10.46 | < 0.001 | |
三亚市 Sanya | 零模型 Null model: pp | |||||
NODF | 58.55 | 60.52 | 2.36 | -0.83 | 0.19 | |
NODFc | 69.50 | 72.74 | 3.71 | -0.87 | 0.20 | |
NODFr | 58.50 | 60.46 | 2.36 | -0.83 | 0.16 | |
零模型 Null model: rc | ||||||
WNODF | 38.37 | 49.25 | 1.70 | -6.40 | < 0.001 | |
WNODFc | 35.41 | 46.53 | 4.32 | -2.57 | < 0.01 | |
WNODFr | 38.38 | 49.27 | 1.70 | -6.40 | < 0.001 |
表1 海口和三亚城市林地斑块鸟类嵌套格局分析
Table 1 Analysis of nested pattern of birds in different woodlot patches of Haikou and Sanya cities
区域 Sites | 嵌套度量化 Nestedness metric | 观测值 Observed | 期望值 Expected | 标准差 SD | Z | P |
---|---|---|---|---|---|---|
海口市 Haikou | 零模型 Null model: pp | |||||
NODF | 52.38 | 54.89 | 2.19 | -1.14 | 0.13 | |
NODFc | 60.85 | 67.81 | 4.57 | -1.52 | 0.06 | |
NODFr | 52.30 | 54.76 | 2.18 | -1.13 | 0.13 | |
零模型 Null model: rc | ||||||
WNODF | 34.14 | 54.23 | 1.92 | -10.49 | < 0.001 | |
WNODFc | 32.86 | 61.34 | 4.37 | -6.51 | < 0.001 | |
WNODFr | 34.16 | 54.19 | 1.91 | -10.46 | < 0.001 | |
三亚市 Sanya | 零模型 Null model: pp | |||||
NODF | 58.55 | 60.52 | 2.36 | -0.83 | 0.19 | |
NODFc | 69.50 | 72.74 | 3.71 | -0.87 | 0.20 | |
NODFr | 58.50 | 60.46 | 2.36 | -0.83 | 0.16 | |
零模型 Null model: rc | ||||||
WNODF | 38.37 | 49.25 | 1.70 | -6.40 | < 0.001 | |
WNODFc | 35.41 | 46.53 | 4.32 | -2.57 | < 0.01 | |
WNODFr | 38.38 | 49.27 | 1.70 | -6.40 | < 0.001 |
图5 海口和三亚林地中鸟类物种数调查值与随机分布模型预测曲线结果比较。圆圈表示观测到的物种丰富度; 实线表示期望值; 虚线表示期望值标准曲线。
Fig. 5 Comparison of observed data to expected values under the random placement models for birds in Haikou and Sanya woodlots. The dots represent the observed species richness; The solid line represents the expected value; The dashed lines represent the standard deviation of the expected value (± 1SD).
图6 海口和三亚林地中鸟类物种丰富度(10为底对数转换)与林地斑块面积(10为底对数转换; 单位: km2)关系图。灰色区域表示95%置信区间。
Fig. 6 The relationship of species richness (Lg transformed) and woodlots area (Lg transformed; unit: km2) in Haikou and Sanya woodlots. The grey bands represent 95% confidence intervals.
图7 海口和三亚林地中鸟类物种丰富度(10为底对数转换)与距最近大面积林地的距离(10为底对数转换; 单位: m)关系图。灰色区域表示95%置信区间。
Fig. 7 The relationship of species richness (Lg transformed) and the distance to the nearest larger woodlot (Lg transformed; unit: m) in Haikou and Sanya woodlots. The grey bands represent 95% confidence intervals.
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