赤水河流域样点独特性对鱼类β多样性的贡献
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S 931

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农业农村部财政专项“长江渔业资源与环境调查 (2017—2021)”;云南省科技厅科技计划项目“赤水河流域绿色治理和发展技术研究及应用示范” (202203AC100001);生态环境部生物多样性调查评估项目 (2019HJ2096001006);中国长江三峡集团公司科研项目(0799574)


Site uniqueness contributions to fish β diversity in the Chishui River basin, Southwestern China
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    摘要:

    分析了赤水河流域鱼类多维度β多样性的纵向空间格局,以期为鱼类资源的保护和科学管理提供依据。基于2019和2020年赤水河流域40个样点的调查数据,研究了各个样点对鱼类物种、功能、分类和环境β多样性的贡献程度 (又称样点独特性),同时对各个指数间的互补和冗余程度进行了分析。结果显示,调查期间赤水河共采集到鱼类125 (亚)种,隶属于7目20科80属,其中土著鱼类112 (亚)种,外来鱼类13 (亚)种。鱼类物种β多样性的值为0.719,样点S1、S2、S22和S27的物种独特性显著不同于其他样点。鱼类功能β多样性的值为0.009,样点S10、S20、S21、S28和S36功能独特性与其他样点存在显著差异。鱼类分类β多样性的值为0.004,样点S20、S21、S28和S32的分类独特性显著高于其他样点。样点环境独特性的变异范围为0.010~0.058,最高的4个点为S22、S29、S33和S34样点。随着鱼类丰富度的增加,样点物种独特性呈现出先降低再增加的U型变化趋势。不同维度的样点独特性指数间互补程度较高,然而样点功能独特性和样点分类独特性比样点物种独特性解释了较多的多样性变异。研究表明,β多样性能够揭示淡水鱼类群落结构的时空变化格局及维持机制,鱼类多样性评估需要综合考虑不同维度的生物和非生物多样性。

    Abstract:

    Understanding the patterns and ecological determinants of β diversity is critical for community ecology and conservation biology. However, only few studies have investigated fish β diversity in large rivers, and even fewer have included multiple facets of biotic and abiotic diversity indices simultaneously. Based on sampling data from the Chishui River basin in 2019 and 2020, we calculated fish species, functional, taxonomic, and environmental β diversity, as well as the relative contribution of individual sampling site to each facet of β diversity (also known as site uniqueness). Further, we assessed the degree of complementarity and redundancy between the calculated indices of site uniqueness. By doing these, we tried to provide a scientific basis for the conservation and management of fish resources in the Chishui River basin, which is a pioneer area for the protection of the upper Yangtze River. The results showed that a total of 125 fish (sub) species belonging to 7 orders, 20 families and 80 genera were collected from the Chishui River basin, including 112 native fish (sub) species and 13 exotic (sub) species. Species β diversity of fish assemblages were 0.719, and species uniqueness of sampling sites S1, S2, S22 and S27 was significantly different from other sites. Functional β diversity of fish assemblages were 0.009, with sampling sites S10, S20, S21, S28 and S36 having significantly different functional uniqueness values compared with other sites. Taxonomic β diversity of fish assemblages were 0.004, with sample sites S20, S21, S28 and S32 having significantly higher taxonomic uniqueness in comparison with other sites. Environmental uniqueness of sampling sites ranged from 0.010 to 0.058, and the four highest sites were S22, S29, S33 and S34. Fish species uniqueness of sampling sites showed a significant U-shaped relationship with fish richness, that is, species uniqueness of sampling sites firstly decreased and then increased with fish richness. There was a high degree of complementarity between different facets of diversity indices, and functional and taxonomic uniqueness of sampling sites explained more diversity variation than species uniqueness of sampling sites. This study suggests that fish diversity assessments need to integrate different facets of biotic and abiotic diversity indices, as they can be useful in revealing spatial and temporal variation of freshwater fish community structure and the underlying mechanisms.

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夏治俊,余梵冬,唐永忠,张友钊,邓伯龙,刘定明,刘飞,王剑伟.赤水河流域样点独特性对鱼类β多样性的贡献[J].水产学报,2023,47(2):029309

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  • 收稿日期:2022-09-30
  • 最后修改日期:2023-01-09
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  • 在线发布日期: 2023-03-01
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