生物多样性 ›› 2023, Vol. 31 ›› Issue (3): 22399. DOI: 10.17520/biods.2022399
所属专题: 生物入侵
收稿日期:
2022-07-13
接受日期:
2022-11-24
出版日期:
2023-03-20
发布日期:
2023-01-01
通讯作者:
王楠
作者简介:
* E-mail: wangnan761227@bjfu.edu.cn基金资助:
Yexi Zhao, Jiayu Zhang, Zihan Li, Qinmijia Xie, Xin Deng, Nan Wang()
Received:
2022-07-13
Accepted:
2022-11-24
Online:
2023-03-20
Published:
2023-01-01
Contact:
Nan Wang
摘要:
随着城市化进程的加剧, 城市鸟类愈加依赖园林植物提供的栖息环境。与此同时, 外来植物在城市园林建设中的比例逐渐增加, 成为城市鸟类栖息地的重要组成部分。园林植物是城市鸟类的主要夜栖场所, 其合理配置可以为鸟类提供适宜的夜栖环境, 并维持城市鸟类多样性。研究城市鸟类对夜栖植物的利用, 可以为城市园林建设提供参考依据。2021-2022年, 我们通过红外热成像仪观察北京城市鸟类夜栖行为, 并对夜栖植物的种类、胸径、树高、冠幅和鸟类的栖枝高度进行测量与记录。共记录夜栖鸟类12科23种1,865只次, 夜栖植物22科45种。调查地的本土植物数量占45.08%, 外来植物数量占54.92%。夜栖于外来植物的鸟类数量约为本土植物的4倍。夜栖鸟类数量最多的植物为圆柏(Juniperus chinensis), 之后依次为美国红梣(Fraxinus pennsylvanica)、早园竹(Phyllostachys propinqua)、一球悬铃木(Platanus occidentalis)、旱柳(Salix matsudana)等。夜栖鸟类稀有度加权丰富度(rarity-weighted richness, RWR)最高的植物为圆柏, 之后依次为美国红梣、早园竹、油松(Pinus tabuliformis)、榆树(Ulmus pumila)等。本土夜栖植物的胸径、树高、冠幅和夜栖鸟类的栖枝高度显著高于外来植物。鸟类在冬季夜栖时对外来植物的利用比例(95.44%)显著高于其他季节(75.37%)。本研究结果表明, 北京城市园林建设中的外来植物丰富了鸟类的夜栖环境。
赵也茜, 张家语, 李子涵, 解秦米佳, 邓歆, 王楠 (2023) 北京城市鸟类夜栖时对本土和外来植物的利用. 生物多样性, 31, 22399. DOI: 10.17520/biods.2022399.
Yexi Zhao, Jiayu Zhang, Zihan Li, Qinmijia Xie, Xin Deng, Nan Wang (2023) Use of native and alien plants during night roosting by urban birds in Beijing. Biodiversity Science, 31, 22399. DOI: 10.17520/biods.2022399.
图2 夜栖鸟类与夜栖植物的关系。左侧鸟类名后的数字表示记录到此夜栖鸟类的个体数量, 右侧植物名前的数字表示夜栖于该种植物的鸟类个体数量。线条的宽度表示鸟类数量, 鸟类个体数量越多, 线条越宽。
Fig. 2 The relationship between night-roosting birds and plants. The number after the name of the bird on the left indicates the number of individuals recorded to this night-roosting bird. The number before the name of the plant on the right indicates the number of individual birds nocturnally inhabiting the plant. The width of the line indicates the number of birds, and the wider the line, the greater the number of birds.
图3 夜栖鸟类利用植物种数。1: 灰喜鹊; 2: 麻雀; 3: 喜鹊; 4: 珠颈斑鸠; 5: 乌鸫; 6: 白头鹎; 7: 黑尾蜡嘴雀; 8: 山斑鸠; 9: 燕雀; 10: 北灰鹟; 11: 赤颈鸫; 12: 红喉姬鹟; 13: 红尾斑鸫; 14: 红胸姬鹟; 15: 虎斑地鸫; 16: 灰背鸫; 17: 灰椋鸟; 18: 家燕; 19: 煤山雀; 20: 乌鹟; 21: 沼泽山雀; 22: 棕头鸦雀; 23: 纵纹腹小鸮。
Fig. 3 Number of plant species used by night-roosting birds. 1, Cyanopica cyanus; 2, Passer montanus; 3, Pica pica; 4, Streptopelia chinensis; 5, Turdus mandarinus; 6, Pycnonotus sinensis; 7, Eophona migratoria; 8, Streptopelia orientalis; 9, Fringilla montifringilla; 10, Muscicapa dauurica; 11, Turdus ruficollis; 12, Ficedula albicilla; 13, Turdus naumanni; 14, Ficedula parva; 15, Zoothera aurea; 16, Turdus hortulorum; 17, Spodiopsar cineraceus; 18, Hirundo rustica; 19, Periparus ater; 20, Muscicapa sibirica; 21, Poecile palustris; 22, Sinosuthora webbiana; 23, Athene noctua.
本土植物 Native plants | 外来植物 Alien plants | χ2 | P | |
---|---|---|---|---|
胸径 Diameter at breast height (cm) | 39.28 ± 0.78 | 33.80 ± 0.52 | 71.115 | < 0.01 |
树高 Tree height (m) | 14.65 ± 0.15 | 12.84 ± 0.11 | 147.18 | < 0.01 |
冠幅 Canopy (m) | 10.44 ± 0.16 | 8.03 ± 0.11 | 167.71 | < 0.01 |
栖枝高度 Perch height (m) | 10.41 ± 0.15 | 8.46 ± 0.08 | 147.18 | < 0.01 |
表1 本土和外来夜栖植物的比较(Kruskal-Wallis检验) (平均值 ± 标准误)
Table 1 Comparison of native and alien night roosting plants (Kruskal-Wallis test) (mean ± SE)
本土植物 Native plants | 外来植物 Alien plants | χ2 | P | |
---|---|---|---|---|
胸径 Diameter at breast height (cm) | 39.28 ± 0.78 | 33.80 ± 0.52 | 71.115 | < 0.01 |
树高 Tree height (m) | 14.65 ± 0.15 | 12.84 ± 0.11 | 147.18 | < 0.01 |
冠幅 Canopy (m) | 10.44 ± 0.16 | 8.03 ± 0.11 | 167.71 | < 0.01 |
栖枝高度 Perch height (m) | 10.41 ± 0.15 | 8.46 ± 0.08 | 147.18 | < 0.01 |
图5 各季节夜栖植物的胸径(A)、树高(B)、冠幅(C)和栖枝高度(D)
Fig. 5 Diameter at breast height (A), tree height (B), canopy (C) and perch height (D) of night roosting plants in different season
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