生物多样性 ›› 2019, Vol. 27 ›› Issue (10): 1101-1111. DOI: 10.17520/biods.2019213
所属专题: 昆虫多样性与生态功能
收稿日期:
2019-07-03
接受日期:
2019-09-10
出版日期:
2019-10-20
发布日期:
2019-10-20
通讯作者:
丁平
基金资助:
Haonan Zhou, Yuhao Zhao, Di Zeng, Juan Liu, Tinghao Jin, Ping Ding*()
Received:
2019-07-03
Accepted:
2019-09-10
Online:
2019-10-20
Published:
2019-10-20
Contact:
Ping Ding
摘要:
为了探讨千岛湖岛屿景观参数对地表蚂蚁群落物种α和β多样性空间格局的影响, 作者分别于2017和2018年的5-8月, 采用陷阱法、凋落物分拣法和手捡法调查了千岛湖33个岛屿上的地表蚂蚁群落, 并依据食性将其划分为捕食性蚂蚁和杂食性蚂蚁。利用回归模型分析了全部蚂蚁、捕食性蚂蚁和杂食性蚂蚁群落α和β多样性与岛屿景观参数的关系。结果表明, 岛屿面积对全部蚂蚁、捕食性蚂蚁和杂食性蚂蚁的物种丰富度均有显著的正向影响, 而隔离度则无显著作用。蚂蚁群落的β多样性由空间周转组分主导。岛屿面积差对全部蚂蚁、捕食性蚂蚁和杂食性蚂蚁群落β多样性的嵌套组分有正向影响, 隔离度差只对杂食性蚂蚁的总体β多样性有正向影响。因此, 岛屿面积是影响千岛湖地表蚂蚁群落物种丰富度的主要因素, 并且岛屿面积通过嵌套组分来影响蚂蚁群落的β多样性, 表现出选择性灭绝过程。此外, 不同食性蚂蚁可能因为扩散能力的差异对岛屿景观参数产生不同的响应。
周浩楠, 赵郁豪, 曾頔, 刘娟, 金挺浩, 丁平 (2019) 千岛湖陆桥岛屿地表蚂蚁群落物种多样性空间格局及其影响因素. 生物多样性, 27, 1101-1111. DOI: 10.17520/biods.2019213.
Haonan Zhou, Yuhao Zhao, Di Zeng, Juan Liu, Tinghao Jin, Ping Ding (2019) Spatial patterns and influencing factors of ground ant species diversity on the land-bridge islands in the Thousand Island Lake, China. Biodiversity Science, 27, 1101-1111. DOI: 10.17520/biods.2019213.
图2 全部蚂蚁、捕食性蚂蚁和杂食性蚂蚁的物种丰富度与岛屿面积和隔离度的关系。有显著作用(P < 0.05)以实线表示, 无显著作用以虚线表示。Slope: 斜率。
Fig. 2 Relationship of island area and isolation with species richness of total ants, predator ants and omnivore ants. Solid line indicates significant relationship at P < 0.05. Dashed line indicates no significant relationship.
图3 千岛湖调查岛屿上全部蚂蚁、捕食性蚂蚁和杂食性蚂蚁的总体β多样性指数及其组分分解。βsor表示Sørensen多岛屿相异性指数, βsne表示嵌套组分, βsim表示空间周转组分, βratio表示嵌套组分占总体β多样性指数的比例。
Fig. 3 The multiple-site Sørensen dissimilarity (βsor) and its components of turnover (βsim) and nestedness-resultant (βsne) of total ants, predator ants and omnivore ants on the study islands in the Thousand Island Lake. βratio = βsne/βsor.
图4 岛屿参数对全部蚂蚁的β多样性(βsor)、空间周转组分(βsim)和嵌套组分(βsne)的影响。显著性结果(P < 0.05)以实线表示, 无显著结果以虚线表示。a: 回归模型的斜率; b: 回归模型的截距; r: Pearson相关系数; p: mantel替代检验的p值。
Fig. 4 The relationship of overall beta diversity (βsor) and its components of turnover (βsim) and nestedness-resultant (βsne), with difference in island area and isolation of total ant communities on study islands in Thousand Island Lake. Solid line shows the significant relationship at P < 0.05, and dashed line shows no significant relationship. a, slope of multiple regression model; b, intercept of multiple regression model; r, Pearson correlation coefficient; p, p-value of Mantel permutation test.
图5 岛屿参数对捕食性蚂蚁的β多样性(βsor)、空间周转组分(βsim)和嵌套组分(βsne)的影响。显著性结果(P < 0.05)以实线表示, 无显著结果以虚线表示。a: 回归模型的斜率; b: 回归模型的截距; r: Pearson相关系数; p: mantel替代检验的p值。
Fig. 5 The relationship of overall beta diversity (βsor) and its components of turnover (βsim) and nestedness-resultant (βsne), with difference in island area and isolation of predator ant communities on study islands in Thousand Island Lake. Solid line shows the significant relationship at P < 0.05, and dashed line shows no significant relationship. a, slope of multiple regression model; b, intercept of multiple regression model; r, Pearson correlation coefficient; p, p-value of Mantel permutation test.
图6 岛屿参数对杂食性蚂蚁的β多样性(βsor)、空间周转组分(βsim)和嵌套组分(βsne)的影响。显著性结果(P < 0.05)以实线表示, 无显著结果以虚线表示。a: 回归模型的斜率; b: 回归模型的截距; r: Pearson相关系数; p: mantel替代检验的p值。
Fig. 6 The relationship of overall beta diversity (βsor) and its components of turnover (βsim) and nestedness-resultant (βsne), with difference in island area and isolation of omnivore ant communities on study islands in Thousand Island Lake. Solid line shows the significant relationship at P < 0.05, and dashed line shows no significant relationship. a, slope of multiple regression model; b, intercept of multiple regression model; r, Pearson correlation coefficient; p, p-value of Mantel permutation test.
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