基于环境DNA的秦岭南北麓鱼类多样性调查与分析

Investigation and analysis of fish diversity in the northern and southern foothills of Qinling Mountains based on environmental DNA

  • 摘要:目的】掌握秦岭南北麓河源溪流鱼类群落结构及其多样性差异,探究拦河坝对河源溪流上下游鱼类生态的影响,为开展秦岭南北麓鱼类多样性保护提供基础资料。【方法】采集秦岭南北麓河源溪流水样提取环境DNA(eDNA),在Illumina MiSeq 6000测序平台上进行2×250 bp双端测序,然后基于自建的本地化nt数据库及传统鱼类资源历史调查数据,对秦岭南北麓鱼类多样性进行调查分析。【结果】从秦岭南北麓河源溪流的137个采样点共检出94种鱼类,包括11种外来物种,隶属于8目17科64属。其中,在秦岭南麓河源溪流中共检出8目17科63属91种,在北麓河源溪流中共检出8目17科57属79种。秦岭南麓河源溪流的特有鱼类有12种,包括汉江河源溪流的8个特有鱼类、丹江河源溪流的3个特有鱼类及嘉陵江河源溪流特有的方氏白甲鱼;北麓河源溪流的特有鱼类仅有3种。在目分类水平上,鲤形目的相对丰度在秦岭南北麓河源溪流中均最高,为74.58%~78.79%;其次是鲇形目(7.41%~10.17%)。在属分类水平上,渭河右岸河源溪流中以高原鳅属和大吻鱥属的相对丰度最高,均为5.06%;汉江河源溪流中以大吻鱥属的相对丰度最高(4.93%);嘉陵江河源溪流中以䱻属的相对丰度最高(5.00%);丹江河源溪流中以鳈属和鲫属的相对丰度最高,均为4.62%。在具有单一拦河坝的16条溪流中,除了石门子河与旬河外,其余14条溪流的坝上河段鱼类物种的Shannon指数和Pielou指数均低于坝下河段。【结论】与秦岭北麓河源溪流相比,秦岭南麓河源溪流的鱼类物种更丰富,特有物种更多。秦岭地区河源溪流中外来鱼类物种数量呈明显增加趋势,且河源溪流上建坝破坏了上下游河段的连通性,导致鱼类多样性降低。

     

    Abstract:Objective】This study aimed to investigate the population structure and diversity differences of fish in the headwater streams of northern and southern foothills of Qinling Mountains, to explore effects of barrages on ecology of fish in upstream and downstream in the headwater streams of northern and southern foothills of Qinling Mountains, so as to provide basic materials for conserving diversity of fish in northern and southern foothills of Qinling Mountains.【Method】Environmental DNA (eDNA) was extracted from water samples of headwater streams of northern and southern foothills of Qinling Mountains. 2×250 bp double-ended sequencing was performed on the Illumina MiSeq 6000 sequen-cing platform. Then the fish diversity was analyzed based on the self-built localized nt database and historical survey data of traditional fish resources.【Result】A total of 94 species of fish, including 11 alien species were detected at 137 sampling sites in the headwater streams of northern and southern foothills of Qinling Mountains belonging to 8 orders, 17 families, and 64 genera. Among them, a total of 91 species belonging to 8 orders, 17 families, and 63 genera were detected in the headwater streams of southern foothill of Qinling Mountains. A total of 79 species belonging to 8 orders, 17 families, and 57 genera were detected in the headwater streams at northern foothill. There were 12 endemic fish species in the headwater streams of southern foothill of Qinling Mountains, including 8 endemic fish species in the headwater streams of Hanjiang River, 3 endemic fish species in the headwater streams of Danjiang River, and Onychostoma fangi endemic to the headwater streams of Jialing River. Only three endemic fish species to the headwater streams of northern foothill. At the level of order, the relative abundance of Cypriniformes was the highest in different headwater streams of the northern and southern foothills, ranging from 74.58% to 78.79%, followed by Siluriformes (7.41%-10.17%). At the level of genus, the relative abundances of Triplophysa and Rhynchocypris were the highest in the headwater streams of right bank tributaries of Wei River, both accounting for 5.06%. The relative abundance of Rhynchocypris was the highest in the headwater streams of Hanjiang River, accounting for 4.93%. In the headwater streams of Jialing River, the relative abundance of Hemibarbus was the highest, accounting for 5.00%. In the streams of Danjiang River, the relative abundance of Sarcocheilichthys and Carassius were the highest, both accounting for 4.62%. In the 16 streams blocked by a single barrage, the Shannon index and Pielou index of fish species in the upper barrage sections of 14 streams (Shimenzi River and Xun River not included) were lower than those in the lower barrage sections.【Conclusion】Compared with the headwater streams of the northern foothill of Qinling Mountains, the headwater streams of the southern foothill show richer varieties of fish species and more endemic species. The number of alien fish species in the headwater streams of Qinling Mountains exhibits a significant increasing trend, and constructing barrages on the headwater streams disrupts the connectivity of the upstream and downstream river sections, resulting in a decrease in fish diversity.

     

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