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异龙湖大型底栖动物群落结构及其对水环境变化的响应

Macrozoobenthos community structure and its response to water environmental changes in Yilong Lake

  • 摘要: 为了探究异龙湖大型底栖动物群落结构及其对水环境变化的响应,研究于2023年丰水期(7月)和枯水期(11月)对异龙湖大型底栖动物群落进行采样和鉴定,同时测定10项水环境指标,分析水环境指标与大型底栖动物群落的关系。研究结果表明,此次在异龙湖采集到的大型底栖动物共鉴定出64种,隶属于5门16科33属,其中摇蚊幼虫、寡毛类、甲壳类为主要类群,分别有32种(50%)、11种(17.19%)和7种(10.94%),除摇蚊外的其他水生昆虫有9种(14.06%),软体动物有3种(5%),其他动物有2种(3%)。优势度排名前3的物种为霍甫水丝蚓(Limnodrilus hoffmeisteri)、长足摇蚊(Tanypus sp.A)和细螯沼虾(Macrobrachium superbum)。大型底栖动物平均密度和生物量分别为313.72 ind./m2和51.73 g/m2;非参数检验结果显示,丰水期与枯水期各类群大型底栖动物的密度和生物量变化不显著,但是总密度和生物量在丰水期均高于枯水期;在空间分布上,大型底栖动物密度在湖心区远大于湖滨带,生物量为湖心区小于湖滨带。丰水期大型底栖动物群落Shannon-Wiener多样性指数和Margalef丰富度指数显著低于枯水期,Pielou均匀度指数无显著差异。线性模型冗余分析(RDA)和蒙特卡罗置换检验(Monte Carlo)结果表明,水体浊度(f=2.6,p<0.010)是丰水期影响大型底栖动物群落变化的主要因子,其次为水温(f=3.4,p=0.040);pH(f=4.2,p=0.018)是枯水期影响大型底栖动物群落变化的主要因子。

     

    Abstract: To investigate the community structure of macrozoobenthos in Yilong Lake and its response to aquatic environmental changes, sampling and identification of macrozoobenthos were conducted in the wet season (July) and the dry season(November) of 2023, with 10 water quality parameters measured simultaneously to analyze the relationship between water quality indicators and the macrozoobenthic community.The results indicate that a total of 64 macrozoobenthic species were identified from Yilong Lake, belonging to 5 phyla, 16 families, and 33 genera.The dominant groups were chironomid larvae (32 species, 50%), oligochaetes (11 species, 17.19%), and crustaceans (7 species, 10.94%), followed by other aquatic insects (9 species, 14.06%, excluding chironomids), mollusks (3 species, 5%), and others (2 species, 3%). The top three dominant species were Limnodrilus hoffmeisteri, Tanypus sp. A, and Macrobrachium superbum.The average density and biomass of macrozoobenthos were 313.72 ind./m2 and 51.73 g/m2, respectively. Non-parametric tests revealed no significant seasonal differences in density or biomass of various macrozoobenthic groups between the wet and dry seasons, though both total density and biomass were higher in the wet season than in the dry season. Spatially, the density was significantly higher in the central lake area more than in the littoral zone, whereas biomass showed the opposite trend. The Shannon-Wiener diversity index and Margalef richness index of the macrozoobenthic community were significantly lower in the wet season than in the dry season, while no significant difference was observed in the Pielou evenness index. Redundancy analysis (RDA) and Monte Carlo permutation tests revealed that turbidity (f=2.6, p<0.010) was the primary factor influencing macrozoobenthic community variation in the wet season, with water temperature (f=3.4, p=0.040) as a secondary factor. In the dry season, pH (f=4.2, p=0.018) emerged as the dominant influencing factor.

     

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