生物多样性 ›› 2021, Vol. 29 ›› Issue (1): 32-42. DOI: 10.17520/biods.2020067
余宏昌1(), 毕宝帅1(), 唐文乔1,2,*()(), 张亚1,2(), 郭弘艺1,2()
收稿日期:
2020-03-02
接受日期:
2020-05-23
出版日期:
2021-01-20
发布日期:
2020-09-12
通讯作者:
唐文乔
基金资助:
Hongchang Yu1(), Baoshuai Bi1(), Wenqiao Tang1,2,*()(), Ya Zhang1,2(), Hongyi Guo1,2()
Received:
2020-03-02
Accepted:
2020-05-23
Online:
2021-01-20
Published:
2020-09-12
Contact:
Wenqiao Tang
摘要:
为了评估近20年来上海苏州河环境综合整治过程中鱼类多样性的变化状况, 本文于2019年6月(夏季)和9月(秋季)对苏州河13个断面的鱼类样本进行了采集, 对鱼类多样性和群落结构作了分析。结果显示, 2次采集共获得鱼类样本10,102号, 隶属于8目15科37属45种。夏季和秋季, 上游8个断面的鱼类均为36种, 下游5个断面则为12种和15种。从上游到下游, Shannon-Wiener多样性指数(H')、Margalef种类丰富度指数(D)和Simpson优势度指数(C)总体呈逐渐降低的趋势。相对重要性指数(IRI)显示, 夏秋两季上游断面共同的优势种为似鳊(Pseudobrama simoni), 下游为鲫(Carassius auratus)和泥鳅(Misgurnus anguillicaudatus)。丰度生物量曲线表明, 全河段鱼类群落结构总体上并不稳定, 特别是夏季的下游河段。Cluster聚类和非参数多维标度排序分析可明显将鱼类群落分为上游群组(I)与下游群组(II), 似鳊、泥鳅、鲫、光泽黄颡鱼(Pelteobagrus nitidus)和兴凯鱊(Acheilognathus chankaensis)等是造成群组间差异性的主要分歧种。与2001年的43种、2006年的28种相比, 本次调查的物种数出现了明显回升, 特别是下游河段。这种上游鱼类向下游迁移的趋势, 预示着下游中心城区与上游郊区河段的水质差别正在缩小, 水生态系统恢复迹象明显。本文认为, 上下游之间鱼类群落结构差异的缩小以及翘嘴鲌(Culter alburnus)、红鳍原鲌(Cultrichthys erythropterus)、棒花鱼(Abbottina rivularis)、子陵吻虾虎鱼(Rhinogobius giurinus)等在下游河段的出现, 可作为苏州河综合整治效果的重要生态标志。
余宏昌, 毕宝帅, 唐文乔, 张亚, 郭弘艺 (2021) 上海苏州河治理中鱼类多样性及群落结构变化. 生物多样性, 29, 32-42. DOI: 10.17520/biods.2020067.
Hongchang Yu, Baoshuai Bi, Wenqiao Tang, Ya Zhang, Hongyi Guo (2021) Changes in fish diversity and assemblage during comprehensive restoration of the Suzhou River in Shanghai. Biodiversity Science, 29, 32-42. DOI: 10.17520/biods.2020067.
代号 Codes | 断面名称 Section names | 中心经纬度 Coordinates |
---|---|---|
上游 Upstream | ||
S1 | 赵屯 Zhaotun | 121°04′ E, 31°16′ N |
S2 | 白鹤 Baihe | 121°08′ E, 31°16′ N |
S3 | 油墩港 Youdungang | 121°09′ E, 31°14′ N |
S4 | 蕰藻浜 Wenzaobang | 121°12′E, 31°18′ N |
S5 | 黄渡 Huangdu | 121°12′ E, 31°15′ N |
S6 | 新通波塘 Xintongbotang | 121°12′ E, 31°14′ N |
S7 | 封浜河口 Fengbanghekou | 121°18′ E, 31°13′ N |
S8 | 北新泾 Beixinjing | 121°22′ E, 31°13′ N |
下游 Downstream | ||
S9 | 中山西路桥 Zhongshanxilu Bridge | 121°23′ E, 31°13′ N |
S10 | 武宁路桥 Wuninglu Bridge | 121°25′ E, 31°14′ N |
S11 | 昌化路桥 Changhualu Bridge | 121°26′ E, 31°15′ N |
S12 | 成都路桥 Chengdulu Bridge | 121°27′ E, 31°14′ N |
S13 | 外白渡桥 Waibaidu Bridge | 121°29′ E, 31°14′ N |
表1 上海苏州河各采样断面位置信息表
Table 1 The coordinates of sections of the Suzhou River in Shanghai
代号 Codes | 断面名称 Section names | 中心经纬度 Coordinates |
---|---|---|
上游 Upstream | ||
S1 | 赵屯 Zhaotun | 121°04′ E, 31°16′ N |
S2 | 白鹤 Baihe | 121°08′ E, 31°16′ N |
S3 | 油墩港 Youdungang | 121°09′ E, 31°14′ N |
S4 | 蕰藻浜 Wenzaobang | 121°12′E, 31°18′ N |
S5 | 黄渡 Huangdu | 121°12′ E, 31°15′ N |
S6 | 新通波塘 Xintongbotang | 121°12′ E, 31°14′ N |
S7 | 封浜河口 Fengbanghekou | 121°18′ E, 31°13′ N |
S8 | 北新泾 Beixinjing | 121°22′ E, 31°13′ N |
下游 Downstream | ||
S9 | 中山西路桥 Zhongshanxilu Bridge | 121°23′ E, 31°13′ N |
S10 | 武宁路桥 Wuninglu Bridge | 121°25′ E, 31°14′ N |
S11 | 昌化路桥 Changhualu Bridge | 121°26′ E, 31°15′ N |
S12 | 成都路桥 Chengdulu Bridge | 121°27′ E, 31°14′ N |
S13 | 外白渡桥 Waibaidu Bridge | 121°29′ E, 31°14′ N |
种类 Species | 夏季 Summer | 秋季 Autumn | ||
---|---|---|---|---|
上游 Upstream | 下游 Downstream | 上游 Upstream | 下游 Downstream | |
刀鲚 Coilia nasus | 1,045.89 | 154.59 | ||
翘嘴鲌 Culter alburnus | 130.01 | |||
达氏鲌 Culter dabryi | 920.05 | 827.64 | ||
红鳍原鲌 Cultrichthys erythropterus | 454.52 | 109.75 | ||
贝氏䱗 Hemiculter bleekeri | 1,116.50 | 139.41 | ||
䱗 Hemiculter leucisculus | 2,898.83 | 183.99 | ||
似鳊 Pseudobrama simoni | 10,159.54 | 309.94 | 11,302.52 | 756.94 |
麦穗鱼 Pseudorasbora parva | 391.31 | 244.64 | ||
兴凯鱊 Acheilognathus chankaensis | 1,024.73 | 976.12 | ||
大鳍鱊 Acheilognathus macropterus | 215.51 | |||
高体鳑鲏 Rhodeus ocellatus | 274.22 | |||
鲫 Carassius auratus | 549.44 | 6,752.95 | 1,798.81 | 7,029.52 |
鲤 Cyprinus carpio | 1,666.27 | |||
泥鳅 Misgurnus anguillicaudatus | 167.30 | 5,946.77 | 264.08 | 5,202.53 |
光泽黄颡鱼 Pelteobagrus nitidus | 179.78 | 932.39 | ||
子陵吻虾虎鱼 Rhinogobius giurinus | 182.71 | |||
乌鳢 Channa argus | 1,334.40 | 765.65 |
表2 上海苏州河鱼类优势种(IRI ≥ 1,000)和常见种(100 ≤ IRI < 1,000)的相对重要性指数
Table 2 Index of relative importance (IRI) of the dominant (IRI ≥ 1,000) and common (100 ≤ IRI < 1,000) fish species of the Suzhou River in Shanghai
种类 Species | 夏季 Summer | 秋季 Autumn | ||
---|---|---|---|---|
上游 Upstream | 下游 Downstream | 上游 Upstream | 下游 Downstream | |
刀鲚 Coilia nasus | 1,045.89 | 154.59 | ||
翘嘴鲌 Culter alburnus | 130.01 | |||
达氏鲌 Culter dabryi | 920.05 | 827.64 | ||
红鳍原鲌 Cultrichthys erythropterus | 454.52 | 109.75 | ||
贝氏䱗 Hemiculter bleekeri | 1,116.50 | 139.41 | ||
䱗 Hemiculter leucisculus | 2,898.83 | 183.99 | ||
似鳊 Pseudobrama simoni | 10,159.54 | 309.94 | 11,302.52 | 756.94 |
麦穗鱼 Pseudorasbora parva | 391.31 | 244.64 | ||
兴凯鱊 Acheilognathus chankaensis | 1,024.73 | 976.12 | ||
大鳍鱊 Acheilognathus macropterus | 215.51 | |||
高体鳑鲏 Rhodeus ocellatus | 274.22 | |||
鲫 Carassius auratus | 549.44 | 6,752.95 | 1,798.81 | 7,029.52 |
鲤 Cyprinus carpio | 1,666.27 | |||
泥鳅 Misgurnus anguillicaudatus | 167.30 | 5,946.77 | 264.08 | 5,202.53 |
光泽黄颡鱼 Pelteobagrus nitidus | 179.78 | 932.39 | ||
子陵吻虾虎鱼 Rhinogobius giurinus | 182.71 | |||
乌鳢 Channa argus | 1,334.40 | 765.65 |
种类 Species | 平均相似性贡献率 Average similarity contribution (%) | 平均相异性贡献率 Average dissimilarity contribution (%) | |
---|---|---|---|
群组I Group I | 群组II Group II | 群组I-群组II Group I-Group II | |
似鳊 Pseudobrama simoni | 66.34 | 4.43 | 26.37 |
䱗 Hemiculter leucisculus | 8.61 | 4.65 | |
兴凯鱊 Acheilognathus chankaensis | 7.18 | 5.63 | |
达氏鲌 Culter dabryi | 3.05 | 2.62 | |
鲫 Carassius auratus | 2.58 | 34.68 | 15.62 |
泥鳅 Misgurnus anguillicaudatus | 47.65 | 21.45 | |
光泽黄颡鱼 Pelteobagrus nitidus | 4.36 | 6.19 | |
麦穗鱼 Pseudorasbora parva | 2.67 | ||
乌鳢 Channa argus | 2.43 | ||
贝氏䱗 Hemiculter bleekeri | 2.25 | ||
鲤 Cyprinus carpio | 2.16 | ||
不足1% Less than 1% | 4.23 | ||
总计 Total | 91.99 | 91.12 | 92.04 |
平均值 Average values | 59.73 | 43.90 | 82.93 |
表3 上海苏州河鱼类群组内相似性(或群组间相异性)贡献率之和占90%以上的特征种(或分歧种)
Table 3 Fish characteristic species (or divergent species) with more than 90% of the total contribution rate of similarity within group (or dissimilarity between groups) of the Suzhou River in Shanghai
种类 Species | 平均相似性贡献率 Average similarity contribution (%) | 平均相异性贡献率 Average dissimilarity contribution (%) | |
---|---|---|---|
群组I Group I | 群组II Group II | 群组I-群组II Group I-Group II | |
似鳊 Pseudobrama simoni | 66.34 | 4.43 | 26.37 |
䱗 Hemiculter leucisculus | 8.61 | 4.65 | |
兴凯鱊 Acheilognathus chankaensis | 7.18 | 5.63 | |
达氏鲌 Culter dabryi | 3.05 | 2.62 | |
鲫 Carassius auratus | 2.58 | 34.68 | 15.62 |
泥鳅 Misgurnus anguillicaudatus | 47.65 | 21.45 | |
光泽黄颡鱼 Pelteobagrus nitidus | 4.36 | 6.19 | |
麦穗鱼 Pseudorasbora parva | 2.67 | ||
乌鳢 Channa argus | 2.43 | ||
贝氏䱗 Hemiculter bleekeri | 2.25 | ||
鲤 Cyprinus carpio | 2.16 | ||
不足1% Less than 1% | 4.23 | ||
总计 Total | 91.99 | 91.12 | 92.04 |
平均值 Average values | 59.73 | 43.90 | 82.93 |
图7 上海苏州河各断面鱼类种类的历年变化。2001年数据引自夏建宏等(2009); 2006年数据引自陈小华等(2008)。断面代号见表1。
Fig. 7 Changes of fish species in different sections of Suzhou River in Shanghai over the years. Data for 2011 from Xia et al, 2009; Data for 2006 from Chen et al, 2008. Section codes see Table 1.
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