生物多样性 ›› 2024, Vol. 32 ›› Issue (7): 23499. DOI: 10.17520/biods.2023499 cstr: 32101.14.biods.2023499
白雪1,6(), 李正飞1,*()(), 刘洋1,6, 张君倩1(), 张多鹏1(), 罗鑫2, 杨佳莉1,6, 杜丽娜3, 蒋玄空4(), 武瑞文5(), 谢志才1,*()()
收稿日期:
2023-12-28
接受日期:
2024-06-01
出版日期:
2024-07-20
发布日期:
2024-06-24
通讯作者:
*E-mail: lizhengfei@ihb.ac.cn; zhcxie@ihb.ac.cn
基金资助:
Xue Bai1,6(), Zhengfei Li1,*()(), Yang Liu1,6, Junqian Zhang1(), Duopeng Zhang1(), Xin Luo2, Jiali Yang1,6, Lina Du3, Xuankong Jiang4(), Ruiwen Wu5(), Zhicai Xie1,*()()
Received:
2023-12-28
Accepted:
2024-06-01
Online:
2024-07-20
Published:
2024-06-24
Contact:
*E-mail: lizhengfei@ihb.ac.cn; zhcxie@ihb.ac.cn
Supported by:
摘要:
作为我国第三大河流珠江的主支, 西江孕育了丰富且独特的生物多样性。受多重人为压力影响, 流域内生物多样性日渐降低。然而, 人们对西江底栖动物物种多样性格局及维持机制的认识明显不足。本研究基于历史文献调研和2021-2023年现场调查, 系统评估了西江主要水体底栖动物物种多样性, 厘定和编撰物种名录, 甄别驱动群落结构变化的关键因子及受胁因素, 并提出保护对策。结合历史文献和实地调查, 共记录大型底栖无脊椎动物5门10纲33目150科437属704种(历史记录506种, 2021-2023年调查记录352种), 中国特有种占比高达26%。现场调查结果显示, 全流域底栖动物的平均密度和平均生物量分别为437.53 ind./m²和38.65 g/m²。全流域的优势种为长足摇蚊属一种(Tanypus sp.)、雕翅摇蚊属一种(Glyptotendipes sp.)、纹沼螺(Parafossarulus striatulus)和河蚬(Corbicula fluminea)。支流、干流和湖泊的底栖动物群落结构差异显著, 支流的物种丰富度、Simpson优势度指数和Shannon-Wiener多样性指数均高于干流和湖泊。典范对应分析显示, 海拔、电导率、高锰酸盐指数等环境因子和空间因子是影响群落结构的重要因素。方差分解表明, 支流和湖泊的群落主要受环境过滤驱动, 而干流的群落主要受空间过程(质量效应)的影响。流域内的多重人类活动(航运业、大型水利设施、挖沙业、水体污染、土地无序开发利用和外来种入侵等)严重威胁底栖动物多样性。建议采取相应对策, 包括打击过度捕捞、管控挖沙业、恢复湖滨带以维持水文自然节律、控制污染物排放以及科学防控外来入侵种等。
白雪, 李正飞, 刘洋, 张君倩, 张多鹏, 罗鑫, 杨佳莉, 杜丽娜, 蒋玄空, 武瑞文, 谢志才 (2024) 西江流域大型底栖无脊椎动物物种多样性及维持机制. 生物多样性, 32, 23499. DOI: 10.17520/biods.2023499.
Xue Bai, Zhengfei Li, Yang Liu, Junqian Zhang, Duopeng Zhang, Xin Luo, Jiali Yang, Lina Du, Xuankong Jiang, Ruiwen Wu, Zhicai Xie (2024) Species diversity and maintenance mechanisms of benthic macroinvertebrate assemblages in the Xijiang River. Biodiversity Science, 32, 23499. DOI: 10.17520/biods.2023499.
干流 Main stream | 支流 Tributary | 湖泊 Lake | F | P | |
---|---|---|---|---|---|
海拔 Altitude (m) | 553.781 ± 670.88c | 274.31 ± 357.87b | 1,639.46 ± 160.75a | 35.95 | < 0.001 |
水温 Water temperature (℃) | 21.13 ± 2.50b | 20.70 ± 2.74a | 23.49 ± 3.28a | 5.93 | < 0.001 |
电导率 Electric conductivity (μS/cm) | 364.60 ± 118.04b | 189.71 ± 154.16c | 630.38 ± 115.04a | 59.67 | < 0.001 |
溶解氧 Dissolved oxygen (mg/L) | 7.90 ± 0.95 | 7.36 ± 1.43 | 7.94 ± 1.37 | 2.12 | 0.130 |
水深 Water depth (m) | 3.88 ± 5.47 | 3.04 ± 3.86 | 5.94 ± 7.72 | 1.45 | 0.239 |
pH | 7.89 ± 0.16b | 7.41 ± 0.44c | 8.61 ± 0.26a | 86.95 | < 0.001 |
高锰酸盐指数 CODMn (mg/L) | 1.59 ± 1.20b | 1.53 ± 0.47b | 16.26 ± 16.68a | 30.73 | < 0.001 |
总氮 Total nitrogen (mg/L) | 1.49 ± 0.68 | 1.63 ± 0.50 | 2.13 ± 2.29 | 2.03 | 0.138 |
硝态氮 Nitric nitrogen (mg/L) | 2.44 ± 1.34a | 1.54 ± 0.56b | 0.77 ± 0.73c | 16.91 | < 0.001 |
铵氮 Ammonium nitrogen (mg/L) | 0.44 ± 1.32 | 0.24 ± 0.03 | 0.41 ± 0.43 | 0.38 | 0.680 |
盐度 Salinity (‰) | 0.10 ± 0.05b | 0.05 ± 0.03c | 0.25 ± 0.10a | 67.41 | < 0.001 |
总磷 Total phosphorus (mg/L) | 0.18 ± 0.35 | 0.08 ± 0.04 | 0.10 ± 0.10 | 1.58 | 0.210 |
表1 西江主要水体环境因子的均值和标准差
Table 1 Mean value and standard deviation of environmental variables among the main water bodies in the Xijiang River
干流 Main stream | 支流 Tributary | 湖泊 Lake | F | P | |
---|---|---|---|---|---|
海拔 Altitude (m) | 553.781 ± 670.88c | 274.31 ± 357.87b | 1,639.46 ± 160.75a | 35.95 | < 0.001 |
水温 Water temperature (℃) | 21.13 ± 2.50b | 20.70 ± 2.74a | 23.49 ± 3.28a | 5.93 | < 0.001 |
电导率 Electric conductivity (μS/cm) | 364.60 ± 118.04b | 189.71 ± 154.16c | 630.38 ± 115.04a | 59.67 | < 0.001 |
溶解氧 Dissolved oxygen (mg/L) | 7.90 ± 0.95 | 7.36 ± 1.43 | 7.94 ± 1.37 | 2.12 | 0.130 |
水深 Water depth (m) | 3.88 ± 5.47 | 3.04 ± 3.86 | 5.94 ± 7.72 | 1.45 | 0.239 |
pH | 7.89 ± 0.16b | 7.41 ± 0.44c | 8.61 ± 0.26a | 86.95 | < 0.001 |
高锰酸盐指数 CODMn (mg/L) | 1.59 ± 1.20b | 1.53 ± 0.47b | 16.26 ± 16.68a | 30.73 | < 0.001 |
总氮 Total nitrogen (mg/L) | 1.49 ± 0.68 | 1.63 ± 0.50 | 2.13 ± 2.29 | 2.03 | 0.138 |
硝态氮 Nitric nitrogen (mg/L) | 2.44 ± 1.34a | 1.54 ± 0.56b | 0.77 ± 0.73c | 16.91 | < 0.001 |
铵氮 Ammonium nitrogen (mg/L) | 0.44 ± 1.32 | 0.24 ± 0.03 | 0.41 ± 0.43 | 0.38 | 0.680 |
盐度 Salinity (‰) | 0.10 ± 0.05b | 0.05 ± 0.03c | 0.25 ± 0.10a | 67.41 | < 0.001 |
总磷 Total phosphorus (mg/L) | 0.18 ± 0.35 | 0.08 ± 0.04 | 0.10 ± 0.10 | 1.58 | 0.210 |
图4 西江主要水体大型底栖无脊椎动物群落密度、生物量及多样性指数的差异。* P < 0.05; ** P < 0.01; NS: P > 0.05。
Fig. 4 Comparation of density, biomass and diversity indices of benthic macroinvertebrate communities in main water bodies in the Xijiang River. * P < 0.05; ** P < 0.01; NS, P > 0.05.
物种 Species | 西江 Xijiang River (%) | 干流 Main stream (%) | 支流 Tributary (%) | 湖泊 Lake (%) |
---|---|---|---|---|
苏氏尾鳃蚓 Branchiura sowerbyi | - | 6.4 | - | - |
水丝蚓属一种 Limnodrilus sp. | - | - | - | 6.2 |
蜾蠃蜚属一种 Corophium sp. | - | 6.3 | - | - |
米虾属一种 Caridina sp. | - | 7.2 | - | - |
摇蚊属一种 Chironomus sp. | - | - | 7.8 | - |
长足摇蚊属一种 Tanypus sp. | 17.2 | - | - | 42.9 |
多足摇蚊属一种 Polypedilum sp. | - | 7.9 | - | - |
雕翅摇蚊属一种 Glyptotendipes sp. | 5.2 | - | - | 12.9 |
石田螺属一种 Sinotaia sp. | - | 5.8 | - | - |
膀胱螺属一种 Physa sp. | - | 5.0 | - | - |
纹沼螺 Parafossarulus striatulus | 7.2 | - | - | 17.3 |
越南沟蜷 Sulcospira tonkiniana | - | - | 5.7 | - |
河蚬 Corbicula fluminea | 6.2 | - | 14.4 | - |
湖沼股蛤 Limnoperna lacustris | - | - | 7.1 | - |
表2 西江主要水体大型底栖无脊椎动物优势种百分比
Table 2 The relative density percentage of dominant species of benthic macroinvertebrates in main water bodies in the Xijiang River
物种 Species | 西江 Xijiang River (%) | 干流 Main stream (%) | 支流 Tributary (%) | 湖泊 Lake (%) |
---|---|---|---|---|
苏氏尾鳃蚓 Branchiura sowerbyi | - | 6.4 | - | - |
水丝蚓属一种 Limnodrilus sp. | - | - | - | 6.2 |
蜾蠃蜚属一种 Corophium sp. | - | 6.3 | - | - |
米虾属一种 Caridina sp. | - | 7.2 | - | - |
摇蚊属一种 Chironomus sp. | - | - | 7.8 | - |
长足摇蚊属一种 Tanypus sp. | 17.2 | - | - | 42.9 |
多足摇蚊属一种 Polypedilum sp. | - | 7.9 | - | - |
雕翅摇蚊属一种 Glyptotendipes sp. | 5.2 | - | - | 12.9 |
石田螺属一种 Sinotaia sp. | - | 5.8 | - | - |
膀胱螺属一种 Physa sp. | - | 5.0 | - | - |
纹沼螺 Parafossarulus striatulus | 7.2 | - | - | 17.3 |
越南沟蜷 Sulcospira tonkiniana | - | - | 5.7 | - |
河蚬 Corbicula fluminea | 6.2 | - | 14.4 | - |
湖沼股蛤 Limnoperna lacustris | - | - | 7.1 | - |
图6 西江主要水体大型底栖无脊椎动物群落结构与环境和空间因子的典范对应分析(CCA)排序图。PCNM1、PCNM2、PCNM3、PCNM4、PCNM6、PCNM7代表大尺度空间因子, PCNM12、PCNM18、PCNM21、PCNM35代表小尺度空间因子。
Fig. 6 Canonical correspondence analysis (CCA) ordination plots presenting the relationship between benthic macroinvertebrate communities and significant environmental and spatial factors in main water bodies in the Xijiang River. PCNM1, PCNM2, PCNM3, PCNM4, PCNM6, and PCNM7 are large-scale spatial factors; PCNM12, PCNM18, PCNM21, and PCNM35 are small-scale spatial factors.
图7 环境因子和空间因子对西江主要水体底栖动物群落结构的相对影响。* P < 0.05。
Fig. 7 Relative contribution of environmental and spatial factors on the macroinvertebrate communities structure in main water bodies across the Xijiang River. * P < 0.05.
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