尾矿坝改变了上游水源鱼类的组合

IF 5.1 Q1 ENVIRONMENTAL SCIENCES
Gilberto N. Salvador , Robert M. Hughes , Fábio Vieira , Raphael Ligeiro , Luciano F.A. Montag
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引用次数: 1

摘要

河景连通性是决定水系生态条件的重要组成部分。我们评估了尾矿库坝(TSD)失去连通性导致的鱼类群落变化,假设上游鱼类群落由位于下游的TSD重组,即使上游栖息地没有改变。我们使用标准方法在24个一级至三级站点收集鱼类,其中一半排放到TSD(筑坝),另一半没有受到这种影响(未受影响)。为了确定处理之间的差异,我们使用PERMANOVA测试了环境变量和鱼类区系组成(Bray-Curtis相似性指数),并评估了对组合组成变化影响最大的生物指标。正如预期的那样,我们没有观察到环境变量处理之间的差异,但我们确实观察到了鱼类群落组成的差异。我们还观察到在筑坝溪流中具有较低值的五个指标(不耐受物种的丰富度和丰度、siluriform丰富度和Pareiorhaphis的丰度(参见proskynita和Trichomycterus brasiliensis))和在筑坝河流中具有较高值的两个指标(Oligosarcus argeteus的perciform丰富度和丰度)。我们认为,这些变化是由于TSD的溪流破碎以及源汇机制造成的,并得出结论,位于下游的矿山TSD改变了源头鱼类群落,这一影响在生物监测和生物评估研究中经常被忽视。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Mine tailings storage dams modify upstream headwater fish assemblages

Riverscape connectivity is a critically important component determining the ecological condition of lotic ecosystems. We evaluated changes in fish assemblages caused by the loss of connectivity by mine tailings storage dams (TSDs), hypothesizing that headwater fish assemblages are restructured by TSDs located downstream, even though the upstream habitats are not altered. We used standard methods to collect fish in 24 first to third order sites, with half draining to TSDs (dammed) and the other half free from this impact (undammed). To identify differences between treatments, we used PERMANOVA to test both environmental variables and ichthyofauna composition (Bray-Curtis similarity index) and evaluated the biological metrics that most influenced assemblage composition change. As expected, we observed no difference between treatments for environmental variables, but we did observe differences in fish assemblage composition. We also observed five metrics with lower values in dammed streams (richness and abundance of intolerant species, siluriform richness, and abundance of Pareiorhaphis cf. proskynita and Trichomycterus brasiliensis) and two metrics with higher values in dammed streams (perciform richness and abundance of Oligosarcus argenteus). We believe these changes resulted from of stream fragmentation by TSDs, in addition to source-sink mechanisms and conclude that mine TSDs located downstream change headwater fish assemblages, an impact often neglected in biomonitoring and bioassessment studies.

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