生物多样性 ›› 2023, Vol. 31 ›› Issue (5): 22473. DOI: 10.17520/biods.2022473
收稿日期:
2022-08-18
接受日期:
2022-11-15
出版日期:
2023-05-20
发布日期:
2023-01-01
通讯作者:
* E-mail: 基金资助:
Luqin Yin1,2, Cheng Wang1,2,*(), Wenjing Han1,2
Received:
2022-08-18
Accepted:
2022-11-15
Online:
2023-05-20
Published:
2023-01-01
Contact:
* E-mail: 摘要:
城市是鸟类的重要栖息地, 城市绿地中占比最大的为居住绿地, 是容纳鸟类的重要生境。对于鸟类生存来说, 食物的种类和数量是关键的限制因子。本研究从鸟类的食物偏好入手, 旨在构建北京居住区鸟类的食源关系, 探究鸟类在居住区中取食的影响因素。研究选取40个居住小区作为调查样地, 于2020年6月至2021年5月每月调查1次, 采用广义线性模型评估鸟类在居住区中取食的影响因素, 并对鸟类的食源多样性指数与多度、分布范围进行线性回归。结果表明: (1)本研究共记录到取食行为的鸟种共14科35种2,242只, 丰富度为春季 > 秋季 > 冬季 > 夏季, 多度为春季 > 冬季 > 秋季 > 夏季, Shannon-Wiener多样性指数为秋季 > 春季 > 冬季 > 夏季。(2)鸟类的食源依次为昆虫(33.87%)、翅果(18.33%)、浆果(9.77%)、球果(8.16%)、草籽(5.17%)等。(3)鸟类对植物的直接利用高达60.4%, 间接利用为39.6%, 食源植物Shannon-Wiener多样性指数为秋季(3.1612) > 冬季(2.9651) > 春季(2.9203) > 夏季(2.1763)。(4)食源树种是影响鸟类在居住区中取食最关键的外界环境因素, 食源越丰富的鸟种, 其种群数量越大, 分布范围越广泛。居住区的食源植物具有类型丰富、种类繁多、从早春到晚秋覆盖全物候的特点, 在规划设计时应多配置北京乡土树种以及金银木(Lonicera maackii)等观果植物, 减少绿篱配置, 倡导低干扰的近自然园林养护管理措施。
殷鲁秦, 王成, 韩文静 (2023) 基于取食行为探究北京居民区鸟类的食源特征及多样性. 生物多样性, 31, 22473. DOI: 10.17520/biods.2022473.
Luqin Yin, Cheng Wang, Wenjing Han (2023) Food source characteristics and diversity of birds based on feeding behavior in residential areas of Beijing. Biodiversity Science, 31, 22473. DOI: 10.17520/biods.2022473.
图2 北京居住区鸟类食源关系图。图中的数字表示取食行为频次。
Fig. 2 Relationship between birds and food sources in residential areas of Beijing. The number indicates the feeding frequency.
图3 北京居住区不同季节鸟类食源关系图。图中的数字表示取食行为频次。
Fig. 3 Relationship between birds and food sources in residential areas of Beijing in different seasons. The number indicates the feeding frequency.
季节 Season | 食源植物 Food source plant | 鸟类 Bird | ||||
---|---|---|---|---|---|---|
夏季 Summer | 秋季 Autumn | 冬季 Winter | 夏季 Summer | 秋季 Autumn | 冬季 Winter | |
春季 Spring | 0.0738 | 0.4725 | 0.4655 | 0.1389 | 0.5756 | 0.4789 |
夏季 Summer | 0.1524 | 0.1115 | 0.2641 | 0.2027 | ||
秋季 Autumn | 0.4291 | 0.4789 |
表1 北京居住区不同季节食源植物、鸟类的Bray-Curtis相似性系数
Table 1 Bray-Curtis similarity coefficients of food source plants or birds during different seasons in residential areas of Beijing
季节 Season | 食源植物 Food source plant | 鸟类 Bird | ||||
---|---|---|---|---|---|---|
夏季 Summer | 秋季 Autumn | 冬季 Winter | 夏季 Summer | 秋季 Autumn | 冬季 Winter | |
春季 Spring | 0.0738 | 0.4725 | 0.4655 | 0.1389 | 0.5756 | 0.4789 |
夏季 Summer | 0.1524 | 0.1115 | 0.2641 | 0.2027 | ||
秋季 Autumn | 0.4291 | 0.4789 |
图5 不同季节鸟类对不同生活型植物的利用方式关系图。图中的数字刻度表示取食行为的频次。
Fig. 5 Plant utilization of different life forms by birds in different seasons. The numerical scale in the figure indicates the feeding frequency.
响应变量 Response variables | 模型 Model | 自由度 df | ΔAICc | 权重 Weight | R2 |
---|---|---|---|---|---|
物种丰富度 Species richness | CFST + SFST | 3 | 0 | 0.1518 | 0.5729 |
CFST + SFST + PAR | 4 | 0.0188 | 0.1504 | 0.5936 | |
CFST + SFST + CY | 4 | 1.2920 | 0.0796 | 0.5786 | |
CFST + SFST + AREA | 4 | 1.3209 | 0.0784 | 0.5692 | |
物种密度 Species density | CFST | 3 | 0 | 0.1447 | 0.2352 |
CFST + SFST | 4 | 0.5466 | 0.1101 | 0.2516 | |
CFST + SFST + AREA | 5 | 1.7703 | 0.0597 | 0.2572 | |
Shannon-Wiener多样性指数 Shannon-Wiener diversity index | CFST + SFST | 4 | 0 | 0.1129 | 0.2516 |
CFST + SFST + CY | 5 | 0.9647 | 0.0697 | 0.2516 | |
SFST | 3 | 1.1036 | 0.0650 | 0.0358 | |
CFST + SFST + PAR | 5 | 1.2596 | 0.0601 | 0.2431 | |
CFST + SFST + CY | 5 | 1.9831 | 0.0419 | 0.2431 | |
CFST + SFST + BD | 6 | 1.9843 | 0.0419 | 0.2253 |
表2 基于取食行为的鸟类多样性与环境因子的模型选择
Table 2 Model selection relating bird diversity based on feeding behavior and environmental factors
响应变量 Response variables | 模型 Model | 自由度 df | ΔAICc | 权重 Weight | R2 |
---|---|---|---|---|---|
物种丰富度 Species richness | CFST + SFST | 3 | 0 | 0.1518 | 0.5729 |
CFST + SFST + PAR | 4 | 0.0188 | 0.1504 | 0.5936 | |
CFST + SFST + CY | 4 | 1.2920 | 0.0796 | 0.5786 | |
CFST + SFST + AREA | 4 | 1.3209 | 0.0784 | 0.5692 | |
物种密度 Species density | CFST | 3 | 0 | 0.1447 | 0.2352 |
CFST + SFST | 4 | 0.5466 | 0.1101 | 0.2516 | |
CFST + SFST + AREA | 5 | 1.7703 | 0.0597 | 0.2572 | |
Shannon-Wiener多样性指数 Shannon-Wiener diversity index | CFST + SFST | 4 | 0 | 0.1129 | 0.2516 |
CFST + SFST + CY | 5 | 0.9647 | 0.0697 | 0.2516 | |
SFST | 3 | 1.1036 | 0.0650 | 0.0358 | |
CFST + SFST + PAR | 5 | 1.2596 | 0.0601 | 0.2431 | |
CFST + SFST + CY | 5 | 1.9831 | 0.0419 | 0.2431 | |
CFST + SFST + BD | 6 | 1.9843 | 0.0419 | 0.2253 |
响应变量 Response variables | 环境因子 Environmental factors | 参数估计 Estimate | 标准误 SE | P |
---|---|---|---|---|
物种丰富度 Species richness | CFST | 0.3885 | 0.1141 | < 0.001*** |
SFST | 0.5979 | 0.1749 | < 0.001*** | |
PAR | -0.0918 | 0.1684 | 0.5909 | |
CY | 0.0227 | 0.0707 | 0.7528 | |
AREA | 0.0248 | 0.0776 | 0.7538 | |
物种密度 Species density | CFST | 8.9247 | 2.5447 | < 0.001*** |
SFST | 2.1968 | 2.9115 | 0.4577 | |
AREA | -0.6399 | 1.8525 | 0.7342 | |
Shannon-Wiener多样性指数 Shannon-Wiener diversity index | CFST | 0.2340 | 0.1696 | 0.1768 |
SFST | 0.5013 | 0.1594 | 0.0023** | |
CY | 0.0322 | 0.0928 | 0.7326 | |
PAR | -0.0665 | 0.1527 | 0.6672 | |
AREA | 0.0138 | 0.0681 | 0.8434 | |
BD | 0.0282 | 0.1034 | 0.7877 |
表3 基于取食行为的鸟类多样性与环境因子平均模型的参数估计
Table 3 Parameter estimation of the average model relating bird diversity based on feeding behavior to environmental factors
响应变量 Response variables | 环境因子 Environmental factors | 参数估计 Estimate | 标准误 SE | P |
---|---|---|---|---|
物种丰富度 Species richness | CFST | 0.3885 | 0.1141 | < 0.001*** |
SFST | 0.5979 | 0.1749 | < 0.001*** | |
PAR | -0.0918 | 0.1684 | 0.5909 | |
CY | 0.0227 | 0.0707 | 0.7528 | |
AREA | 0.0248 | 0.0776 | 0.7538 | |
物种密度 Species density | CFST | 8.9247 | 2.5447 | < 0.001*** |
SFST | 2.1968 | 2.9115 | 0.4577 | |
AREA | -0.6399 | 1.8525 | 0.7342 | |
Shannon-Wiener多样性指数 Shannon-Wiener diversity index | CFST | 0.2340 | 0.1696 | 0.1768 |
SFST | 0.5013 | 0.1594 | 0.0023** | |
CY | 0.0322 | 0.0928 | 0.7326 | |
PAR | -0.0665 | 0.1527 | 0.6672 | |
AREA | 0.0138 | 0.0681 | 0.8434 | |
BD | 0.0282 | 0.1034 | 0.7877 |
图6 基于取食行为的北京居住区鸟种排序图。图中数字表示前10位的取食地点, 椭圆表示95%的置信区间。1: 元宝枫; 2: 国槐; 3: 草地; 4: 榆树; 5: 绦柳; 6: 白蜡; 7: 裸土地; 8: 侧柏; 9: 重瓣粉海棠; 10: 栾树。
Fig. 6 Ranking map of bird species based on feeding behavior in residential areas of Beijing. Number indicates top 10 feeding sites, and ovals indicate 95% confidence intervals. 1, Acer truncatum; 2, Styphnolobium japonicum; 3, Lawn; 4, Ulmus pumila; 5, Salix matsudana ?Pendula?; 6, Fraxinus chinensis; 7, Bare land; 8, Platycladus orientalis; 9, Malus spectabilis var. riversii; 10, Koelreuteria paniculata.
图7 北京居住区鸟类多度(A)、分布小区数(B)与食源多样性指数的线性回归。灰色区域表示拟合线的置信区间。
Fig. 7 Relationship between bird abundance (A), number of residential areas (B) and Shannon-Wiener diversity index of food source in residential areas of Beijing. Gray areas indicate confidence intervals for the fitted lines.
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