生物多样性 ›› 2020, Vol. 28 ›› Issue (10): 1202-1212. DOI: 10.17520/biods.2020009
所属专题: 生物入侵
白敬沛1, 黄耿1,*(), 蒋长军1, 章伟成1, 王齐东2, 姚伦广1,*(
)
收稿日期:
2020-01-08
接受日期:
2020-05-19
出版日期:
2020-10-20
发布日期:
2020-10-20
通讯作者:
黄耿,姚伦广
作者简介:
E-mail: wangyoukl@126.com;基金资助:
Jingpei Bai1, Geng Huang1,*(), Changjun Jiang1, Weicheng Zhang1, Qidong Wang2, Lunguang Yao1,*(
)
Received:
2020-01-08
Accepted:
2020-05-19
Online:
2020-10-20
Published:
2020-10-20
Contact:
Geng Huang,Lunguang Yao
摘要:
为了解丹江口水库鱼类群落现状及历史变化, 作者于2018-2019年采用多网目复合刺网采样和渔民渔获物调查的方式对丹江口水库进行了鱼类群落调查。本次调查共采集鱼类33种, 隶属5目11科29属, 以鲤科鱼类为主, 占总数的63.6%。基于多网目复合刺网采样的鱼类群落多样性指数和单位努力捕捞量(catch per unit effort, CPUE, g·day -1·m -2)在各采样点间具有一定的差异。目前丹江口水库以定居性、喜静缓流、杂食性和肉食性鱼类为主。与20世纪50年代和80年代的历史资料相比, 丹江口水库鱼类物种丰富度先升高后下降; 而生态类型则呈现杂食性鱼类、喜流水性鱼类和洄游性鱼类比例持续下降的趋势。2018-2019年丹江口水库鱼类组成与20世纪80年代的相似性指数为0.35 (中等不相似), 与20世纪50年代的相似性指数为0.29 (中等不相似)。调查结果表明半个世纪以来丹江口水库鱼类群落结构发生了较大变化, 目前趋于小型化和简单化。这些变化可能是由大坝建设、渔业放养、不合理捕捞、外来鱼类引入等人类活动所致。
白敬沛, 黄耿, 蒋长军, 章伟成, 王齐东, 姚伦广 (2020) 丹江口水库鱼类群落特征及其历史变化. 生物多样性, 28, 1202-1212. DOI: 10.17520/biods.2020009.
Jingpei Bai, Geng Huang, Changjun Jiang, Weicheng Zhang, Qidong Wang, Lunguang Yao (2020) Characteristics and historical changes of the fish assemblage in the Danjiangkou Reservoir. Biodiversity Science, 28, 1202-1212. DOI: 10.17520/biods.2020009.
地点 Sampling site | 马蹬镇 Madeng Town | 丹江口市 Danjiangkou City | 凉水河镇 Liangshuihe Town | 渠首 Headwork | 均县镇 Junxian Town |
---|---|---|---|---|---|
物种丰富度 Species richness (D) | 7.000 ± 0.892a | 8.000± 1.033a | 8.000 ± 0.813a | 10.000 ± 0.433a | 12.000 ± 1.031b |
Shannon-Wiener多样性指数 Shannon-Wiener diversity index (H') | 1.374 ± 0.173a | 1.408 ± 0.169a | 1.424 ± 0.182a | 1.436 ± 0.076a | 1.574 ± 0.226a |
Pielou均匀度指数 Pielou evenness index (J) | 0.769 ± 0.067a | 0.636 ± 0.083a | 0.641 ± 0.069a | 0.614 ± 0.037a | 0.644 ± 0.070a |
单位努力捕捞量 CPUE (g·day-1·m-2) | 2.568 ± 0.977a | 3.735 ± 1.108ab | 3.846 ± 1.112ab | 4.298 ± 1.096ab | 4.841 ± 0.586b |
表1 基于多网目复合刺网采样的2018-2019年丹江口水库鱼类群落多样性指数及单位努力捕捞量的空间差异(不同小写字母表示各地点间具有显著性差异)
Table 1 Spatial variations of biodiversity indexes and catch per unit effort (CPUE) of fish in the Danjiangkou Reservoir in 2018-2019 based on multi-mesh gillnet samplings. Different lowercase letters indicate the significant differences among sites.
地点 Sampling site | 马蹬镇 Madeng Town | 丹江口市 Danjiangkou City | 凉水河镇 Liangshuihe Town | 渠首 Headwork | 均县镇 Junxian Town |
---|---|---|---|---|---|
物种丰富度 Species richness (D) | 7.000 ± 0.892a | 8.000± 1.033a | 8.000 ± 0.813a | 10.000 ± 0.433a | 12.000 ± 1.031b |
Shannon-Wiener多样性指数 Shannon-Wiener diversity index (H') | 1.374 ± 0.173a | 1.408 ± 0.169a | 1.424 ± 0.182a | 1.436 ± 0.076a | 1.574 ± 0.226a |
Pielou均匀度指数 Pielou evenness index (J) | 0.769 ± 0.067a | 0.636 ± 0.083a | 0.641 ± 0.069a | 0.614 ± 0.037a | 0.644 ± 0.070a |
单位努力捕捞量 CPUE (g·day-1·m-2) | 2.568 ± 0.977a | 3.735 ± 1.108ab | 3.846 ± 1.112ab | 4.298 ± 1.096ab | 4.841 ± 0.586b |
科 Family | 种类数 Species number | 三个时期共有种数 | 相似性指数 Jaccard similarity index | ||||
---|---|---|---|---|---|---|---|
1950s | 1980s | 2018-2019 | Number of mutual species | 1950s vs. 1980s | 1950s vs. 2018-2019 | 1980s vs. 2018-2019 | |
鲤科 Cyprinidae | 28 | 42 | 21 | 12 | 0.46 | 0.36 | 0.43 |
鲟科 Acipenseridae | 1 | 0 | 0 | 0 | 0.00 | 0.00 | 0.00 |
银鱼科 Salangidae | 0 | 0 | 1 | 0 | 0.00 | 0.00 | 0.00 |
鳀科 Engraulidae | 1 | 0 | 0 | 0 | 0.00 | 0.00 | 0.00 |
鳗鲡科 Anguillidae | 1 | 0 | 0 | 0 | 0.00 | 0.00 | 0.00 |
鳅科 Cobitidae | 0 | 3 | 1 | 0 | 0.00 | 0.00 | 0.33 |
平鳍鳅科 Balitoridae | 2 | 2 | 0 | 0 | 1.00 | 0.00 | 0.00 |
鮰科 Ictaluridae | 0 | 0 | 1 | 0 | 0.00 | 0.00 | 0.00 |
鲿科 Bagridae | 3 | 9 | 3 | 3 | 0.33 | 0.20 | 0.33 |
鲇科 Siluridae | 1 | 2 | 1 | 1 | 0.50 | 1.00 | 0.00 |
鮡科 Sisoridae | 0 | 1 | 0 | 0 | 0.00 | 0.00 | 0.00 |
合鳃鱼科 Synbranchidae | 1 | 1 | 0 | 0 | 1.00 | 0.00 | 0.00 |
刺鳅科 Mastacembelidae | 0 | 1 | 0 | 0 | 0.00 | 0.00 | 0.00 |
鮨科 Serranidae | 3 | 3 | 1 | 1 | 1.00 | 0.33 | 0.33 |
虾虎鱼科 Gobiidae | 1 | 1 | 1 | 1 | 1.00 | 1.00 | 0.00 |
鳢科 Channidae | 0 | 1 | 1 | 0 | 0.00 | 0.00 | 1.00 |
塘鳢科 Eleotridae | 1 | 1 | 0 | 0 | 1.00 | 0.00 | 0.00 |
太阳鱼科 Centrachidae | 0 | 0 | 1 | 0 | 0.00 | 0.00 | 0.00 |
鱵科 Hemiramphidae | 0 | 0 | 1 | 0 | 0.00 | 0.00 | 0.00 |
合计 Total | 43 | 67 | 33 | 18 | 0.45 | 0.29 | 0.35 |
表2 丹江口水库不同时期鱼类组成相似性指数
Table 2 Variations of fish similarity index in different time periods in the Danjiangkou Reservoir
科 Family | 种类数 Species number | 三个时期共有种数 | 相似性指数 Jaccard similarity index | ||||
---|---|---|---|---|---|---|---|
1950s | 1980s | 2018-2019 | Number of mutual species | 1950s vs. 1980s | 1950s vs. 2018-2019 | 1980s vs. 2018-2019 | |
鲤科 Cyprinidae | 28 | 42 | 21 | 12 | 0.46 | 0.36 | 0.43 |
鲟科 Acipenseridae | 1 | 0 | 0 | 0 | 0.00 | 0.00 | 0.00 |
银鱼科 Salangidae | 0 | 0 | 1 | 0 | 0.00 | 0.00 | 0.00 |
鳀科 Engraulidae | 1 | 0 | 0 | 0 | 0.00 | 0.00 | 0.00 |
鳗鲡科 Anguillidae | 1 | 0 | 0 | 0 | 0.00 | 0.00 | 0.00 |
鳅科 Cobitidae | 0 | 3 | 1 | 0 | 0.00 | 0.00 | 0.33 |
平鳍鳅科 Balitoridae | 2 | 2 | 0 | 0 | 1.00 | 0.00 | 0.00 |
鮰科 Ictaluridae | 0 | 0 | 1 | 0 | 0.00 | 0.00 | 0.00 |
鲿科 Bagridae | 3 | 9 | 3 | 3 | 0.33 | 0.20 | 0.33 |
鲇科 Siluridae | 1 | 2 | 1 | 1 | 0.50 | 1.00 | 0.00 |
鮡科 Sisoridae | 0 | 1 | 0 | 0 | 0.00 | 0.00 | 0.00 |
合鳃鱼科 Synbranchidae | 1 | 1 | 0 | 0 | 1.00 | 0.00 | 0.00 |
刺鳅科 Mastacembelidae | 0 | 1 | 0 | 0 | 0.00 | 0.00 | 0.00 |
鮨科 Serranidae | 3 | 3 | 1 | 1 | 1.00 | 0.33 | 0.33 |
虾虎鱼科 Gobiidae | 1 | 1 | 1 | 1 | 1.00 | 1.00 | 0.00 |
鳢科 Channidae | 0 | 1 | 1 | 0 | 0.00 | 0.00 | 1.00 |
塘鳢科 Eleotridae | 1 | 1 | 0 | 0 | 1.00 | 0.00 | 0.00 |
太阳鱼科 Centrachidae | 0 | 0 | 1 | 0 | 0.00 | 0.00 | 0.00 |
鱵科 Hemiramphidae | 0 | 0 | 1 | 0 | 0.00 | 0.00 | 0.00 |
合计 Total | 43 | 67 | 33 | 18 | 0.45 | 0.29 | 0.35 |
图3 丹江口水库不同生态类型鱼类组成比例的时间变化
Fig. 3 Temporal variations of fish species proportional composition for different ecological types in the Danjiangkou Reservoir
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