Ecology and Environment ›› 2023, Vol. 32 ›› Issue (5): 969-979.DOI: 10.16258/j.cnki.1674-5906.2023.05.014
• Research Articles • Previous Articles Next Articles
JIANG Yongwei1,2(), DING Zhenjun1, YUAN Junbin1, ZHANG Zheng1, LI Yang1, WEN Qingchun1, WANG Yeyao2,3,*(
), JIN Xiaowei3
Received:
2023-03-10
Online:
2023-05-18
Published:
2023-08-09
Contact:
WANG Yeyao
姜永伟1,2(), 丁振军1, 袁俊斌1, 张峥1, 李杨1, 问青春1, 王业耀2,3,*(
), 金小伟3
通讯作者:
王业耀
作者简介:
姜永伟(1984年生),男,高级工程师,博士研究生,主要研究方向为水生态监测与评价。E-mail: jyw435@126.com
基金资助:
CLC Number:
JIANG Yongwei, DING Zhenjun, YUAN Junbin, ZHANG Zheng, LI Yang, WEN Qingchun, WANG Yeyao, JIN Xiaowei. Study on Benthic Macroinvertebrates Community Structure and Water Quality Evaluation in Main Rivers of Liaoning Province[J]. Ecology and Environment, 2023, 32(5): 969-979.
姜永伟, 丁振军, 袁俊斌, 张峥, 李杨, 问青春, 王业耀, 金小伟. 辽宁省主要河流底栖动物群落结构及水质评价研究[J]. 生态环境学报, 2023, 32(5): 969-979.
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URL: https://www.jeesci.com/EN/10.16258/j.cnki.1674-5906.2023.05.014
监测区域 | 辽河 | 浑河 | 太子河 | 大辽河 | 大凌河 | 鸭绿江 | 碧流河 |
---|---|---|---|---|---|---|---|
上游点位 | 辽河源、四双大桥、二道河子、福德店、三合屯、通江口、清辽、东大桥、黄河子、珠尔山 | 北杂木、古楼、台沟、阿及堡、戈布桥 | 老关砬子、 兴安、邱家 | 王家窝棚 | 坦甸子 | 茧场 | |
中游点位 | 马虎山、红庙子 | 东陵大桥、七台子、于家房、蒲河沿 | 参窝坝下、汤河桥、下王家、孟柳 | 南大桥、长宝渡口、章吉营 | 蒲石河大桥、 荒沟、爱河大桥 | ||
下游点位 | 盘锦兴安、曙光大桥 | 韭菜台子 | 牛庄、小姐庙 | 辽河公园 | 王家沟、高台子、张家堡 | 文安 |
Table 1 Sampling sites of benthic macroinvertebrates in main rivers of Liaoning province
监测区域 | 辽河 | 浑河 | 太子河 | 大辽河 | 大凌河 | 鸭绿江 | 碧流河 |
---|---|---|---|---|---|---|---|
上游点位 | 辽河源、四双大桥、二道河子、福德店、三合屯、通江口、清辽、东大桥、黄河子、珠尔山 | 北杂木、古楼、台沟、阿及堡、戈布桥 | 老关砬子、 兴安、邱家 | 王家窝棚 | 坦甸子 | 茧场 | |
中游点位 | 马虎山、红庙子 | 东陵大桥、七台子、于家房、蒲河沿 | 参窝坝下、汤河桥、下王家、孟柳 | 南大桥、长宝渡口、章吉营 | 蒲石河大桥、 荒沟、爱河大桥 | ||
下游点位 | 盘锦兴安、曙光大桥 | 韭菜台子 | 牛庄、小姐庙 | 辽河公园 | 王家沟、高台子、张家堡 | 文安 |
类型 | 候选参数 | 对干扰的反应 | 平均值 | 标准差 | 最小值 | 最大值 | 25%分位数 | 中位数 | 75%分位数 |
---|---|---|---|---|---|---|---|---|---|
丰富度参数 | M1 | 减小 | 13.6 | 5.27 | 9.0 | 25.0 | 9.5 | 11.5 | 16.3 |
M2 | 不确定 | 628.8 | 880.5 | 55.0 | 2790 | 108.8 | 283.5 | 521.5 | |
M3 | 减小 | 4.4 | 3.3 | 0.0 | 10.0 | 2.0 | 4.0 | 6.8 | |
M4 | 减小 | 324.6 | 743.3 | 0.0 | 2417.0 | 43.0 | 57.0 | 141.5 | |
M5 | 减小 | 0.4 | 0.5 | 0.0 | 1.0 | 0.0 | 0.0 | 1.0 | |
M6 | 增大 | 8.7 | 16.2 | 0.0 | 44.0 | 0.0 | 0.0 | 7.0 | |
M7 | 减小 | 6.4 | 3.4 | 1.0 | 13.0 | 5.0 | 5.5 | 8.3 | |
M8 | 减小 | 359.9 | 520.6 | 9.0 | 1600.0 | 50.3 | 156.5 | 281.5 | |
M9 | 增大 | 1.8 | 1.1 | 0.0 | 4.0 | 1.0 | 2.0 | 2.0 | |
M10 | 增大 | 44.5 | 94.9 | 0.0 | 310.0 | 1.5 | 7.0 | 40.0 | |
物种组成参数 | M11 | 增大 | 0.4 | 0.1 | 0.2 | 0.6 | 0.3 | 0.4 | 0.5 |
M12 | 减小 | 0.4 | 0.3 | 0.0 | 0.8 | 0.1 | 0.4 | 0.7 | |
M13 | 减小 | 0.5 | 0.2 | 0.1 | 0.7 | 0.4 | 0.5 | 0.6 | |
M14 | 减小 | 0.6 | 0.2 | 0.0 | 0.9 | 0.5 | 0.6 | 0.7 | |
M15 | 增大 | 0.1 | 0.1 | 0.0 | 0.2 | 0.1 | 0.1 | 0.2 | |
M16 | 增大 | 0.1 | 0.1 | 0.0 | 0.2 | 0.0 | 0.0 | 0.1 | |
M17 | 减小 | 2.8 | 0.6 | 2.0 | 3.5 | 2.3 | 2.8 | 3.1 | |
M18 | 减小 | 2.3 | 1.0 | 1.5 | 3.0 | 1.6 | 1.9 | 2.7 | |
耐受性/敏感性参数 | M19 | 增大 | 3.5 | 0.8 | 2.4 | 4.7 | 2.8 | 3.7 | 4.1 |
M20 | 增大 | 0.4 | 0.2 | 0.1 | 0.7 | 0.3 | 0.4 | 0.4 | |
M21 | 减小 | 70.5 | 31.3 | 31.0 | 124.0 | 51.0 | 61.5 | 97.3 |
Table 2 The responses of 21 candidate parameters to disturbance and their distribution ranges at reference sites
类型 | 候选参数 | 对干扰的反应 | 平均值 | 标准差 | 最小值 | 最大值 | 25%分位数 | 中位数 | 75%分位数 |
---|---|---|---|---|---|---|---|---|---|
丰富度参数 | M1 | 减小 | 13.6 | 5.27 | 9.0 | 25.0 | 9.5 | 11.5 | 16.3 |
M2 | 不确定 | 628.8 | 880.5 | 55.0 | 2790 | 108.8 | 283.5 | 521.5 | |
M3 | 减小 | 4.4 | 3.3 | 0.0 | 10.0 | 2.0 | 4.0 | 6.8 | |
M4 | 减小 | 324.6 | 743.3 | 0.0 | 2417.0 | 43.0 | 57.0 | 141.5 | |
M5 | 减小 | 0.4 | 0.5 | 0.0 | 1.0 | 0.0 | 0.0 | 1.0 | |
M6 | 增大 | 8.7 | 16.2 | 0.0 | 44.0 | 0.0 | 0.0 | 7.0 | |
M7 | 减小 | 6.4 | 3.4 | 1.0 | 13.0 | 5.0 | 5.5 | 8.3 | |
M8 | 减小 | 359.9 | 520.6 | 9.0 | 1600.0 | 50.3 | 156.5 | 281.5 | |
M9 | 增大 | 1.8 | 1.1 | 0.0 | 4.0 | 1.0 | 2.0 | 2.0 | |
M10 | 增大 | 44.5 | 94.9 | 0.0 | 310.0 | 1.5 | 7.0 | 40.0 | |
物种组成参数 | M11 | 增大 | 0.4 | 0.1 | 0.2 | 0.6 | 0.3 | 0.4 | 0.5 |
M12 | 减小 | 0.4 | 0.3 | 0.0 | 0.8 | 0.1 | 0.4 | 0.7 | |
M13 | 减小 | 0.5 | 0.2 | 0.1 | 0.7 | 0.4 | 0.5 | 0.6 | |
M14 | 减小 | 0.6 | 0.2 | 0.0 | 0.9 | 0.5 | 0.6 | 0.7 | |
M15 | 增大 | 0.1 | 0.1 | 0.0 | 0.2 | 0.1 | 0.1 | 0.2 | |
M16 | 增大 | 0.1 | 0.1 | 0.0 | 0.2 | 0.0 | 0.0 | 0.1 | |
M17 | 减小 | 2.8 | 0.6 | 2.0 | 3.5 | 2.3 | 2.8 | 3.1 | |
M18 | 减小 | 2.3 | 1.0 | 1.5 | 3.0 | 1.6 | 1.9 | 2.7 | |
耐受性/敏感性参数 | M19 | 增大 | 3.5 | 0.8 | 2.4 | 4.7 | 2.8 | 3.7 | 4.1 |
M20 | 增大 | 0.4 | 0.2 | 0.1 | 0.7 | 0.3 | 0.4 | 0.4 | |
M21 | 减小 | 70.5 | 31.3 | 31.0 | 124.0 | 51.0 | 61.5 | 97.3 |
候选参数 | 平均值 | 标准差 | 最小值 | 最大值 | 25%分位数 | 中位数 | 75%分位数 | IQ值 | 参数取舍 |
---|---|---|---|---|---|---|---|---|---|
M1 | 6.2 | 4.3 | 1.0 | 17.0 | 2.0 | 6.0 | 9.0 | 3 | 保留 |
M3 | 0.7 | 1.1 | 0.0 | 4.0 | 0.0 | 0.0 | 1.0 | 3 | 保留 |
M6 | 3.7 | 9.4 | 0.0 | 45.0 | 0.0 | 0.0 | 0.0 | 0 | 删除 |
M7 | 1.9 | 1.3 | 0.0 | 5.0 | 1.0 | 2.0 | 3.0 | 3 | 保留 |
M9 | 0.5 | 0.8 | 0.0 | 4.0 | 0.0 | 0.0 | 1.0 | 2 | 保留 |
M11 | 0.6 | 0.2 | 0.3 | 1.0 | 0.5 | 0.6 | 0.9 | 2 | 保留 |
M12 | 0.1 | 0.2 | 0.0 | 0.9 | 0.0 | 0.0 | 0.2 | 2 | 保留 |
M13 | 0.4 | 0.2 | 0.0 | 1.0 | 0.3 | 0.3 | 0.5 | 1 | 删除 |
M14 | 0.5 | 0.3 | 0.0 | 1.0 | 0.2 | 0.5 | 0.8 | 1 | 删除 |
M15 | 0.1 | 0.1 | 0.0 | 0.7 | 0.0 | 0.0 | 0.1 | 1 | 删除 |
M16 | 0.1 | 0.2 | 0.0 | 0.9 | 0.0 | 0.0 | 0.1 | 1 | 删除 |
M17 | 1.5 | 0.9 | 0.0 | 2.9 | 1.0 | 1.6 | 2.2 | 3 | 保留 |
M18 | 1.4 | 1.2 | 0.0 | 5.1 | 0.6 | 1.0 | 2.3 | 1 | 删除 |
M19 | 4.2 | 1.3 | 2.5 | 8.0 | 3.3 | 3.8 | 4.8 | 0 | 删除 |
M20 | 0.3 | 0.3 | 0.1 | 1.3 | 0.2 | 0.2 | 0.5 | 1 | 删除 |
M21 | 16.3 | 12.0 | 0.0 | 52.0 | 7.0 | 12.0 | 24.0 | 3 | 保留 |
Table 3 The distribution range, IQ value and choice of 16 parameters at monitoring sites
候选参数 | 平均值 | 标准差 | 最小值 | 最大值 | 25%分位数 | 中位数 | 75%分位数 | IQ值 | 参数取舍 |
---|---|---|---|---|---|---|---|---|---|
M1 | 6.2 | 4.3 | 1.0 | 17.0 | 2.0 | 6.0 | 9.0 | 3 | 保留 |
M3 | 0.7 | 1.1 | 0.0 | 4.0 | 0.0 | 0.0 | 1.0 | 3 | 保留 |
M6 | 3.7 | 9.4 | 0.0 | 45.0 | 0.0 | 0.0 | 0.0 | 0 | 删除 |
M7 | 1.9 | 1.3 | 0.0 | 5.0 | 1.0 | 2.0 | 3.0 | 3 | 保留 |
M9 | 0.5 | 0.8 | 0.0 | 4.0 | 0.0 | 0.0 | 1.0 | 2 | 保留 |
M11 | 0.6 | 0.2 | 0.3 | 1.0 | 0.5 | 0.6 | 0.9 | 2 | 保留 |
M12 | 0.1 | 0.2 | 0.0 | 0.9 | 0.0 | 0.0 | 0.2 | 2 | 保留 |
M13 | 0.4 | 0.2 | 0.0 | 1.0 | 0.3 | 0.3 | 0.5 | 1 | 删除 |
M14 | 0.5 | 0.3 | 0.0 | 1.0 | 0.2 | 0.5 | 0.8 | 1 | 删除 |
M15 | 0.1 | 0.1 | 0.0 | 0.7 | 0.0 | 0.0 | 0.1 | 1 | 删除 |
M16 | 0.1 | 0.2 | 0.0 | 0.9 | 0.0 | 0.0 | 0.1 | 1 | 删除 |
M17 | 1.5 | 0.9 | 0.0 | 2.9 | 1.0 | 1.6 | 2.2 | 3 | 保留 |
M18 | 1.4 | 1.2 | 0.0 | 5.1 | 0.6 | 1.0 | 2.3 | 1 | 删除 |
M19 | 4.2 | 1.3 | 2.5 | 8.0 | 3.3 | 3.8 | 4.8 | 0 | 删除 |
M20 | 0.3 | 0.3 | 0.1 | 1.3 | 0.2 | 0.2 | 0.5 | 1 | 删除 |
M21 | 16.3 | 12.0 | 0.0 | 52.0 | 7.0 | 12.0 | 24.0 | 3 | 保留 |
参数 | M1 | M3 | M7 | M9 | M11 | M12 | M17 | M21 |
---|---|---|---|---|---|---|---|---|
M1 | 1 | |||||||
M3 | 0.68**1) | 1 | ||||||
M7 | 0.73** | 0.88** | 1 | |||||
M9 | 0.69** | 0.43** | 0.49** | 1 | ||||
M11 | 0.63** | -0.51** | 0.59** | -0.53** | 1 | |||
M12 | 0.49** | 0.80** | 0.60** | 0.32* 2) | -0.43** | 1 | ||
M17 | 0.73** | 0.62** | 0.71** | 0.56** | -0.87** | 0.44** | 1 | |
M21 | 0.79** | 0.89** | 0.91** | 0.65** | -0.62** | 0.62** | 0.76** | 1 |
Table 4 Pearson correlation coefficient among 8 parameters
参数 | M1 | M3 | M7 | M9 | M11 | M12 | M17 | M21 |
---|---|---|---|---|---|---|---|---|
M1 | 1 | |||||||
M3 | 0.68**1) | 1 | ||||||
M7 | 0.73** | 0.88** | 1 | |||||
M9 | 0.69** | 0.43** | 0.49** | 1 | ||||
M11 | 0.63** | -0.51** | 0.59** | -0.53** | 1 | |||
M12 | 0.49** | 0.80** | 0.60** | 0.32* 2) | -0.43** | 1 | ||
M17 | 0.73** | 0.62** | 0.71** | 0.56** | -0.87** | 0.44** | 1 | |
M21 | 0.79** | 0.89** | 0.91** | 0.65** | -0.62** | 0.62** | 0.76** | 1 |
B-IBI组成参数 | 分值计算公式 |
---|---|
总分类单元数 | 指数值/17 |
EPT分类单元数 | 指数值/6.7 |
耐污种分类单元数 | (4-指数值)/4 |
香农-维纳多样性指数 | 指数值/3.08 |
Table 5 Score calculation formulas of the four parameters that constitute B-IBI
B-IBI组成参数 | 分值计算公式 |
---|---|
总分类单元数 | 指数值/17 |
EPT分类单元数 | 指数值/6.7 |
耐污种分类单元数 | (4-指数值)/4 |
香农-维纳多样性指数 | 指数值/3.08 |
优秀 | 良好 | 中等 | 较差 | 很差 |
---|---|---|---|---|
>2.36 | 1.77-2.36 | 1.18-1.77 | 0.59-1.18 | 0.00-0.59 |
Table 6 B-IBI evaluation criteria
优秀 | 良好 | 中等 | 较差 | 很差 |
---|---|---|---|---|
>2.36 | 1.77-2.36 | 1.18-1.77 | 0.59-1.18 | 0.00-0.59 |
底栖动物 评价指数 | 计算方法 | 等级标准 | ||||
---|---|---|---|---|---|---|
优秀 | 良好 | 中等 | 较差 | 很差 | ||
B-IBI | (总分类单元数/17)+(EPT分类单元数/6.7)+[(4-耐污种分类单元数)/4]+(Shannon-Wiener多样性指数值/3.08) | >2.36 | (1.77, 2.36] | (1.18, 1.77] | (0.59, 1.18] | (0.00, 0.59] |
BI | <4.2 | (4.2, 5.6] | (5.6, 7.0] | (7.0, 8.4] | >8.4 | |
CMSI | ≥43 | (32, 43] | (22, 31] | (11, 21] | ≤10 | |
ACMSI | CMSI/n:CMSI指底栖动物分值指数,n指参加记分的科数 | ≥6.57 | (4.93, 6.56] | (3.28, 4.92] | (1.64, 3.27] | ≤1.63 |
BPI | <0.1 | (0.1, 0.5] | (0.5, 1.5] | (1.5, 5.0] | ≥5.0 | |
SDI | >3.0 | (2.0, 3.0] | (1.0, 2.0] | (0, 1.0] | 0 |
Table 7 Calculation method and grade standard of the benthic macroinvertebrates evaluation index
底栖动物 评价指数 | 计算方法 | 等级标准 | ||||
---|---|---|---|---|---|---|
优秀 | 良好 | 中等 | 较差 | 很差 | ||
B-IBI | (总分类单元数/17)+(EPT分类单元数/6.7)+[(4-耐污种分类单元数)/4]+(Shannon-Wiener多样性指数值/3.08) | >2.36 | (1.77, 2.36] | (1.18, 1.77] | (0.59, 1.18] | (0.00, 0.59] |
BI | <4.2 | (4.2, 5.6] | (5.6, 7.0] | (7.0, 8.4] | >8.4 | |
CMSI | ≥43 | (32, 43] | (22, 31] | (11, 21] | ≤10 | |
ACMSI | CMSI/n:CMSI指底栖动物分值指数,n指参加记分的科数 | ≥6.57 | (4.93, 6.56] | (3.28, 4.92] | (1.64, 3.27] | ≤1.63 |
BPI | <0.1 | (0.1, 0.5] | (0.5, 1.5] | (1.5, 5.0] | ≥5.0 | |
SDI | >3.0 | (2.0, 3.0] | (1.0, 2.0] | (0, 1.0] | 0 |
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