生物多样性 ›› 2024, Vol. 32 ›› Issue (3): 23303. DOI: 10.17520/biods.2023303 cstr: 32101.14.biods.2023303
倪艳梅1, 陈莉2, 董志远2, 孙德斌2, 李宝泉2,3(), 王绪敏1, 陈琳琳2,3,*()()
收稿日期:
2023-08-29
接受日期:
2024-01-14
出版日期:
2024-03-20
发布日期:
2024-02-27
通讯作者:
*E-mail: llchen@yic.ac.cn
基金资助:
Yanmei Ni1, Li Chen2, Zhiyuan Dong2, Debin Sun2, Baoquan Li2,3(), Xumin Wang1, Linlin Chen2,3,*()()
Received:
2023-08-29
Accepted:
2024-01-14
Online:
2024-03-20
Published:
2024-02-27
Contact:
*E-mail: llchen@yic.ac.cn
摘要:
黄河三角洲国际重要湿地生物多样性保护工程于2019年动工, 本研究基于修复区内大型底栖动物群落组成特点及其与环境因子的相关关系, 分析大型底栖动物群落恢复特征, 了解该地区的生态系统健康状况, 评估保护工程实施三年后修复区湿地生态系统演替阶段及修复效果。结果表明: 2022年春、夏、秋三季共采集到大型底栖动物16种, 隶属于5门6纲15科, 昆虫纲动物在物种组成中占据优势地位; 大型底栖动物密度和生物多样性指数的时空差异均不显著(P > 0.05); 大型底栖动物生物量存在显著的季节差异, 表现为秋季(2.89 g/m2) > 夏季(1.95 g/m2) > 春季(1.90 g/m2), 秋季与春季和夏季间均存在显著差异(P < 0.05), 空间差异不显著(P > 0.05)。与环境因子的相关性分析结果显示, 蠓科一种(Ceratopogonidae sp.)、石缨虫属一种(Laonome sp.)、椭圆萝卜螺(Radix swinhoei)、尖口圆扁螺(Hippeutis cantori)等物种密度与电导率、盐度、总碳、铵盐和亚硝酸盐等指标显著相关(P < 0.01)。快速生物综合评价指数评定修复区为“亚健康”状态。本研究通过对黄河三角洲湿地修复区大型底栖动物群落特征以及生态健康评价的分析, 为修复区底栖动物群落的演替规律研究提供基础数据和科学依据, 为后续湿地修复工程的实施和管理提供指导和参考, 对于黄河三角洲生物多样性的保护具有重要意义。
倪艳梅, 陈莉, 董志远, 孙德斌, 李宝泉, 王绪敏, 陈琳琳 (2024) 黄河三角洲湿地生态修复区大型底栖动物群落结构与生态健康评价. 生物多样性, 32, 23303. DOI: 10.17520/biods.2023303.
Yanmei Ni, Li Chen, Zhiyuan Dong, Debin Sun, Baoquan Li, Xumin Wang, Linlin Chen (2024) Community structure of macrobenthos and ecological health evaluation in the restoration area of the Yellow River Delta wetland. Biodiversity Science, 32, 23303. DOI: 10.17520/biods.2023303.
物种 Species | 优势度 Dominance (Y) | ||
---|---|---|---|
2022.5 | 2022.8 | 2022.10 | |
节肢动物门 Arthropoda | |||
摇蚊幼虫一种 Chironomidae sp. | 0.475* | 0.738* | 0.757* |
蠓科一种 Ceratopogonidae sp. | 0.072* | 0.002 | 0.010 |
龙虱科一种 Dytiscidae sp. | 0.005 | 0.026* | |
软体动物门 Mollusca | |||
椭圆萝卜螺 Radix swinhoei | 0.220* | 0.043* | 0.084* |
尖口圆扁螺 Hippeutis cantori | 0.011 | 0.178* | 0.071* |
线虫动物门 Nematoda | |||
线虫动物一种 Nematoda sp. | 0.111* | 0.009 |
表1 黄河三角洲湿地修复区大型底栖动物群落优势种组成
Table 1 The dominant species composition of macrobenthic communities in the Yellow River Delta wetland restoration area
物种 Species | 优势度 Dominance (Y) | ||
---|---|---|---|
2022.5 | 2022.8 | 2022.10 | |
节肢动物门 Arthropoda | |||
摇蚊幼虫一种 Chironomidae sp. | 0.475* | 0.738* | 0.757* |
蠓科一种 Ceratopogonidae sp. | 0.072* | 0.002 | 0.010 |
龙虱科一种 Dytiscidae sp. | 0.005 | 0.026* | |
软体动物门 Mollusca | |||
椭圆萝卜螺 Radix swinhoei | 0.220* | 0.043* | 0.084* |
尖口圆扁螺 Hippeutis cantori | 0.011 | 0.178* | 0.071* |
线虫动物门 Nematoda | |||
线虫动物一种 Nematoda sp. | 0.111* | 0.009 |
图4 2022年黄河三角洲修复区大型底栖动物群落多样性指数的季节(a)和空间(b)差异
Fig. 4 Seasonal (a) and spatial (b) change of biodiversity index of macrobenthic communities in the restoration area of the Yellow River Delta in 2022
图5 黄河三角洲修复区大型底栖动物群落的聚类分析(a)和多维尺度排序(b)。5-S1: 春季S1站位; 5-S2: 春季S2站位; 5-S3: 春季S3站位; 5-S4: 春季S4站位; 8-S1: 夏季S1站位; 8-S2: 夏季S2站位; 8-S3: 夏季S3站位; 8-S4: 夏季S4站位; 10-S1: 秋季S1站位; 10-S2: 秋季S2站位; 10-S3: 秋季S3站位; 10-S4: 秋季S4站位。
Fig. 5 Cluster analysis (a) and multi-dimensional scaling (b) of macrobenthic communities in the Yellow River Delta restoration area. 5-S1, S1 station in spring; 5-S2, S2 station in spring; 5-S3, S3 station in spring; 5-S4, S4 station in spring; 8-S1, S1 station in summer; 8-S2, S2 station in summer; 8-S3, S3 station in summer; 8-S4, S4 station in summer; 10-S1, S1 station in autumn; 10-S2, S2 station in autumn; 10-S3, S3 station in autumn; 10-S4, S4 station in autumn.
物种 Species | 平均相似度 Average similarity (%) | 贡献率 Contribution rate (%) | 累计贡献率 Cumulative contribution rate (%) |
---|---|---|---|
II组 Group II (组内相似性69.9% Within-group similarity 69.9%) | |||
摇蚊幼虫一种 Chironomidae sp. | 31.90 | 45.64 | 45.64 |
椭圆萝卜螺 Radix swinhoei | 18.78 | 26.87 | 72.51 |
蠓科一种 Ceratopogonidae sp. | 11.95 | 17.10 | 89.61 |
线虫动物一种 Nematoda sp. | 5.09 | 7.28 | 96.89 |
IV组 Group IV (组内相似性68.81% Within-group similarity 68.81%) | |||
摇蚊幼虫一种 Chironomidae sp. | 36.91 | 53.65 | 53.65 |
椭圆萝卜螺 Radix swinhoei | 11.73 | 17.05 | 70.69 |
尖口圆扁螺 Hippeutis cantori | 10.76 | 15.63 | 86.32 |
龙虱科一种 Dytiscidae sp. | 3.64 | 5.29 | 91.62 |
II组和IV组 Group II and Group IV (组间差异性47.22% 47.22% difference between groups) | |||
摇蚊幼虫一种 Chironomidae sp. | 13.03 | 27.59 | 27.59 |
尖口圆扁螺 Hippeutis cantori | 8.24 | 17.46 | 45.05 |
线虫动物一种 Nematoda sp. | 6.00 | 12.69 | 57.74 |
龙虱科一种 Dytiscidae sp. | 3.88 | 8.21 | 65.95 |
蠓科一种 Ceratopogonidae sp. | 3.82 | 8.09 | 74.04 |
椭圆萝卜螺 Radix swinhoei | 2.63 | 5.56 | 79.60 |
表2 研究区域大型底栖动物群落相似性分析
Table 2 Similarity analysis of macrobenthic communities in the study area
物种 Species | 平均相似度 Average similarity (%) | 贡献率 Contribution rate (%) | 累计贡献率 Cumulative contribution rate (%) |
---|---|---|---|
II组 Group II (组内相似性69.9% Within-group similarity 69.9%) | |||
摇蚊幼虫一种 Chironomidae sp. | 31.90 | 45.64 | 45.64 |
椭圆萝卜螺 Radix swinhoei | 18.78 | 26.87 | 72.51 |
蠓科一种 Ceratopogonidae sp. | 11.95 | 17.10 | 89.61 |
线虫动物一种 Nematoda sp. | 5.09 | 7.28 | 96.89 |
IV组 Group IV (组内相似性68.81% Within-group similarity 68.81%) | |||
摇蚊幼虫一种 Chironomidae sp. | 36.91 | 53.65 | 53.65 |
椭圆萝卜螺 Radix swinhoei | 11.73 | 17.05 | 70.69 |
尖口圆扁螺 Hippeutis cantori | 10.76 | 15.63 | 86.32 |
龙虱科一种 Dytiscidae sp. | 3.64 | 5.29 | 91.62 |
II组和IV组 Group II and Group IV (组间差异性47.22% 47.22% difference between groups) | |||
摇蚊幼虫一种 Chironomidae sp. | 13.03 | 27.59 | 27.59 |
尖口圆扁螺 Hippeutis cantori | 8.24 | 17.46 | 45.05 |
线虫动物一种 Nematoda sp. | 6.00 | 12.69 | 57.74 |
龙虱科一种 Dytiscidae sp. | 3.88 | 8.21 | 65.95 |
蠓科一种 Ceratopogonidae sp. | 3.82 | 8.09 | 74.04 |
椭圆萝卜螺 Radix swinhoei | 2.63 | 5.56 | 79.60 |
图6 黄河三角洲修复区大型底栖动物类群与环境因子的相关关系。T: 温度; DO: 溶解氧; SPC: 电导率; SAL: 盐度; pH: 酸碱度; NO2--N: 亚硝酸盐; NH4+-N: 铵盐; NO3--N: 硝酸盐; PO43--P: 磷酸盐; SiO32--Si: 硅酸盐; TN: 总氮; TOC: 总有机碳; TC: 总碳。**P < 0.01。
Fig. 6 Correlation between major macrobenthic groups and environmental factors in the Yellow River Delta restoration area. T, Temperature; DO, Dissolved oxygen; SPC, Specific conductance; SAL, Salinity; NO2--N, Nitrite nitrogen; NH4+-N, Ammonium nitrogen; NO3--N, Nitrate; PO43--P, Phosphate; SiO32--Si, Silicate; TN, Total nitrogen; TOC, Total organic carbon; TC, Total carbon. **P < 0.01.
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