生物多样性 ›› 2021, Vol. 29 ›› Issue (3): 361-372. DOI: 10.17520/biods.2020158
所属专题: 生物入侵
赵阳1,2,3(), 牛诚祎2, 李雪健2,4, 刘海波2, 孙光3, 罗遵兰3,*(), 赵亚辉2,*()
收稿日期:
2020-04-20
接受日期:
2020-07-04
出版日期:
2021-03-20
发布日期:
2020-09-12
通讯作者:
罗遵兰,赵亚辉
作者简介:
E-mail: zhaoyh@ioz.ac.cn;基金资助:
Yang Zhao1,2,3(), Chengyi Niu2, Xuejian Li2,4, Haibo Liu2, Guang Sun3, Zunlan Luo3,*(), Yahui Zhao2,*()
Received:
2020-04-20
Accepted:
2020-07-04
Online:
2021-03-20
Published:
2020-09-12
Contact:
Zunlan Luo,Yahui Zhao
About author:
luozunlan@163.com摘要:
汉江是南水北调中线工程和引汉济渭等跨流域调水工程重要的水源区, 了解其鱼类多样性的现状及变化对于水生态保护尤为重要。作者于2016-2017年间对汉江洋县段干流与6条主要支流的鱼类多样性组成进行了两次调查, 以Margalef丰富度指数、Shannon-Wiener多样性指数、Pielou均匀度指数和Jaccard相似性系数对洋县境内7条河流进行评估, 同时通过相对重要性指数(index of relative importance,IRI)判定优势种, 利用鱼类丰度生物量(abundance biomass comparison, ABC)曲线分析鱼类受干扰情况。结合历史记录, 调查区域内共分布有土著鱼类76种, 隶属于6目14科57属, 以鲤形目鲤科和鲇形目鲿科鱼类为主, 分别占土著鱼类总数的57.89%和11.84%; 珍稀濒危鱼类共计5种, 包括3种国家级保护水生野生动物。鱼类多样性分析结果显示汉江干流的丰富度指数和多样性指数显著高于6条支流。7条河流的IRI指数显示优势种为宽鳍鱲(Zacco platypus)。ABC曲线显示目前调查区域内鱼类小型化现象明显、鱼类受到较严重干扰。水利水电工程建设对于调查区域鱼类多样性影响最大, 干流大型水库(大坝)通过改变原有流水生境、阻断河流纵向连通性、淹没重要鱼类产卵场等对鱼类多样性和群落组成产生不利影响; 支流引水式的中小型电站造成下游河段减、脱水而使河道发生断流以及生境破碎化, 从而威胁土著鱼类的生存。在跨流域调水过程中, 应重视不同水系鱼类引入的潜在生态风险。对引汉济渭工程的水源区鱼类多样性现状的调查, 有助于未来跨流域调水过程中鱼类变化的动态监测和外来物种的预警。
赵阳, 牛诚祎, 李雪健, 刘海波, 孙光, 罗遵兰, 赵亚辉 (2021) 跨流域调水背景下汉江流域洋县段的鱼类多样性及资源现状. 生物多样性, 29, 361-372. DOI: 10.17520/biods.2020158.
Yang Zhao, Chengyi Niu, Xuejian Li, Haibo Liu, Guang Sun, Zunlan Luo, Yahui Zhao (2021) Fish diversity and resource status in the Yangxian Section of the Hanjiang River under the context of inter-basin water transfer. Biodiversity Science, 29, 361-372. DOI: 10.17520/biods.2020158.
图2 汉江洋县段各河流鱼类群落多样性(a)及鱼类群落多样性的季节变化(b)
Fig. 2 Fish diversity of different rivers (a) and seasonal variation of fish diversity of different rivers (b) in the Yangxian section of the Hanjiang River basin
酉水河 Youshui River | 溢水河 Yishui River | 傥水河 Tangshui River | 湑水河 Xushui River | 坪堵河 Pingdu River | 汉江 Hanjiang River | |
---|---|---|---|---|---|---|
金水河 Jinshui River | 0.48 | 0.26 | 0.33 | 0.33 | 0.25 | 0.41 |
酉水河 Youshui River | 0.39 | 0.50 | 0.32 | 0.35 | 0.32 | |
溢水河 Yishui River | 0.71 | 0.33 | 0.29 | 0.19 | ||
傥水河 Tangshui River | 0.47 | 0.43 | 0.26 | |||
湑水河 Xushui River | 0.60 | 0.15 | ||||
坪堵河 Pingdu River | 0.10 |
表1 汉江洋县段各河流鱼类的Jaccard相似性系数
Table 1 The Jaccard similarity coefficient in different rivers in the Yangxian section of the Hanjiang River
酉水河 Youshui River | 溢水河 Yishui River | 傥水河 Tangshui River | 湑水河 Xushui River | 坪堵河 Pingdu River | 汉江 Hanjiang River | |
---|---|---|---|---|---|---|
金水河 Jinshui River | 0.48 | 0.26 | 0.33 | 0.33 | 0.25 | 0.41 |
酉水河 Youshui River | 0.39 | 0.50 | 0.32 | 0.35 | 0.32 | |
溢水河 Yishui River | 0.71 | 0.33 | 0.29 | 0.19 | ||
傥水河 Tangshui River | 0.47 | 0.43 | 0.26 | |||
湑水河 Xushui River | 0.60 | 0.15 | ||||
坪堵河 Pingdu River | 0.10 |
物种 Species | 相对重要性指数 Index of relative importance (IRI) | ||
---|---|---|---|
总计 Total | 秋季 Autumn | 春季 Spring | |
宽鳍鱲 Zacco platypus | 1,031.97 | 1,952.15 | - |
短须颌须鮈 Gnathopogon imberbis | 918.31 | 1,279.67 | 383.99 |
马口鱼 Opsariicjthys bidens | 761.68 | 632.14 | 1,151.37 |
似鮈 Pseudogobio vaillanti vaillant | 588.57 | 968.44 | - |
拉氏鱥 Phoxinus lagowskii | 263.62 | 459.69 | - |
乐山小鳔鮈 Microphysogobio kiatingensis | 234.78 | 389.86 | - |
银鮈 Squalidus argentatus | 148.60 | 340.77 | - |
大斑花鳅 Cobitis macrostigma | 239.22 | 236.36 | 270.79 |
花? Hemibarbus maculatus | - | 144.64 | - |
麦穗鱼 Pseudorasbora parva | - | 122.10 | - |
圆吻鲴 Distoechodon tumirostris | - | 117.47 | - |
鲫 Carassius auratus | - | 113.58 | - |
尖头鲌 Culter oxycephalus | - | - | 172.79 |
多鳞白甲鱼 Onychostoma macrolepis | - | - | 169.57 |
神农吻虾虎鱼 Rhinogobius shennongensis | - | - | 163.97 |
鲇 Silurus asotus | - | - | 103.77 |
表2 汉江洋县段鱼类优势种和重要种的季节变化
Table 2 Seasonal variation of fish dominant species and important species in the Yangxian section of the Hanjiang River basin
物种 Species | 相对重要性指数 Index of relative importance (IRI) | ||
---|---|---|---|
总计 Total | 秋季 Autumn | 春季 Spring | |
宽鳍鱲 Zacco platypus | 1,031.97 | 1,952.15 | - |
短须颌须鮈 Gnathopogon imberbis | 918.31 | 1,279.67 | 383.99 |
马口鱼 Opsariicjthys bidens | 761.68 | 632.14 | 1,151.37 |
似鮈 Pseudogobio vaillanti vaillant | 588.57 | 968.44 | - |
拉氏鱥 Phoxinus lagowskii | 263.62 | 459.69 | - |
乐山小鳔鮈 Microphysogobio kiatingensis | 234.78 | 389.86 | - |
银鮈 Squalidus argentatus | 148.60 | 340.77 | - |
大斑花鳅 Cobitis macrostigma | 239.22 | 236.36 | 270.79 |
花? Hemibarbus maculatus | - | 144.64 | - |
麦穗鱼 Pseudorasbora parva | - | 122.10 | - |
圆吻鲴 Distoechodon tumirostris | - | 117.47 | - |
鲫 Carassius auratus | - | 113.58 | - |
尖头鲌 Culter oxycephalus | - | - | 172.79 |
多鳞白甲鱼 Onychostoma macrolepis | - | - | 169.57 |
神农吻虾虎鱼 Rhinogobius shennongensis | - | - | 163.97 |
鲇 Silurus asotus | - | - | 103.77 |
物种 Species | 相对重要性指数 Index of relative importance (IRI) | ||||||
---|---|---|---|---|---|---|---|
汉江 Hanjiang River | 金水河 Jinshui River | 溢水河 Yishui River | 傥水河 Tangshui River | 酉水河 Youshui River | 湑水河 Xushui River | 坪堵河 Pingdu River | |
宽鳍鱲 Zacco platypus | - | 1,775.83 | - | 1,904.29 | 1,312.76 | 7,872.73 | 4,161.01 |
马口鱼 Opsariicjthys bidens | - | 1,013.00 | - | 1,237.04 | 5,750.20 | - | - |
拉氏鱥 Phoxinus lagowskii | - | - | - | 1,806.22 | - | - | 6,876.49 |
银鮈 Squalidus argentatus | 859.67 | - | - | - | - | - | - |
似鮈 Pseudogobio vaillanti vaillant | - | 2,039.71 | - | 1,478.20 | 1,895.42 | - | 5,129.72 |
短须颌须鮈 Gnathopogon imberbis | - | - | 1,172.40 | 3,290.10 | 1,303.19 | 6,877.97 | 1,148.46 |
红尾荷马条鳅 Homatula variegata | - | - | - | - | - | 1,995.12 | - |
大斑花鳅 Cobitis macrostigma | - | - | 6,300.01 | - | - | - | - |
稀有花鳅 Cobitis rarus | - | - | 1,488.03 | - | - | - | - |
泥鳅 Misgurnus anguillicaudatus | - | - | 1,571.80 | - | - | - | - |
表3 汉江洋县段鱼类优势种的空间变化
Table 3 Spatial variation of dominant fish species in the Yangxian section of the Hanjiang River basin
物种 Species | 相对重要性指数 Index of relative importance (IRI) | ||||||
---|---|---|---|---|---|---|---|
汉江 Hanjiang River | 金水河 Jinshui River | 溢水河 Yishui River | 傥水河 Tangshui River | 酉水河 Youshui River | 湑水河 Xushui River | 坪堵河 Pingdu River | |
宽鳍鱲 Zacco platypus | - | 1,775.83 | - | 1,904.29 | 1,312.76 | 7,872.73 | 4,161.01 |
马口鱼 Opsariicjthys bidens | - | 1,013.00 | - | 1,237.04 | 5,750.20 | - | - |
拉氏鱥 Phoxinus lagowskii | - | - | - | 1,806.22 | - | - | 6,876.49 |
银鮈 Squalidus argentatus | 859.67 | - | - | - | - | - | - |
似鮈 Pseudogobio vaillanti vaillant | - | 2,039.71 | - | 1,478.20 | 1,895.42 | - | 5,129.72 |
短须颌须鮈 Gnathopogon imberbis | - | - | 1,172.40 | 3,290.10 | 1,303.19 | 6,877.97 | 1,148.46 |
红尾荷马条鳅 Homatula variegata | - | - | - | - | - | 1,995.12 | - |
大斑花鳅 Cobitis macrostigma | - | - | 6,300.01 | - | - | - | - |
稀有花鳅 Cobitis rarus | - | - | 1,488.03 | - | - | - | - |
泥鳅 Misgurnus anguillicaudatus | - | - | 1,571.80 | - | - | - | - |
图3 汉江洋县段不同体重范围鱼类的数量和重量占总数量和总体重的比例
Fig. 3 The proportion of fish quantity and weight to total quantity and weight in different weight ranges in the Yangxian section of the Hanjiang River basin
图4 汉江洋县段各河流鱼类按栖息空间以及食性划分的生态习性
Fig. 4 Ecological habits of fish in the Yangxian section of the Hanjiang River basin by habitation space and food preference
图5 汉江洋县段鱼类丰度生物量曲线。a: 鱼类总体; b: 秋季鱼类; c: 春季鱼类。
Fig. 5 Plot abundance biomass comparison of fish in the Yangxian section of the Hanjiang River basin. A, Fish population; B, Fish in autumn; C, Fish in spring.
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