万宁潟湖红树林区域海水重金属污染状况评估

陈靓, 黄赞慧, 王照翻, 邢子浩, 李平汝, 符钉辉, 韦秀. 万宁潟湖红树林区域海水重金属污染状况评估[J]. 海洋地质前沿, 2025, 41(6): 93-102. doi: 10.16028/j.1009-2722.2024.071
引用本文: 陈靓, 黄赞慧, 王照翻, 邢子浩, 李平汝, 符钉辉, 韦秀. 万宁潟湖红树林区域海水重金属污染状况评估[J]. 海洋地质前沿, 2025, 41(6): 93-102. doi: 10.16028/j.1009-2722.2024.071
CHEN Liang, HUANG Zanhui, WANG Zhaofan, XING Zihao, LI Pingru, FU Dinghui, WEI Xiu. Assessment on heavy metal pollution in mangrove seawater of Wanning Lagoon[J]. Marine Geology Frontiers, 2025, 41(6): 93-102. doi: 10.16028/j.1009-2722.2024.071
Citation: CHEN Liang, HUANG Zanhui, WANG Zhaofan, XING Zihao, LI Pingru, FU Dinghui, WEI Xiu. Assessment on heavy metal pollution in mangrove seawater of Wanning Lagoon[J]. Marine Geology Frontiers, 2025, 41(6): 93-102. doi: 10.16028/j.1009-2722.2024.071

万宁潟湖红树林区域海水重金属污染状况评估

  • 基金项目: 中国地质调查局项目“海南岛东南海域自然资源调查试点”(DD20220993),“福建兴化湾-鉴江湾海岛(礁)综合地质调查评价”(DD20251040);海南省科技专项资助(ZDYF2023GXJS011)
详细信息
    作者简介: 陈靓(1992—),女,硕士,工程师,主要从事海洋地质及海洋自然资源调查方面的研究工作. E-mail:clcugb@163.com
    通讯作者: 邢子浩(1990—),男,硕士,工程师,主要从事海洋区域地质调查方面的研究工作. E-mail:331934024@qq.com
  • 中图分类号: P736

Assessment on heavy metal pollution in mangrove seawater of Wanning Lagoon

More Information
  • 重金属污染是海洋环境评价的重要内容,为了解万宁潟湖红树林区域海水重金属含量分布及质量现状,于2022年10月采集了调查区红树林区域20个表层海水样品,对7种常见重金属元素(Hg、Cr、Cu、Zn、Pb、Cd、As)进行分析。采用综合污染指数法、Hakanson指数法以及风险商评价法等评估了红树林区域海水重金属分布及污染情况,并基于相关性分析及双向分层聚类分析方法分析了重金属来源。结果表明,研究区Hg、Cu、Pb、Cd元素的平均含量分别为0.044、14.975、0.695、0.628 μg/L,Cr、Zn、As元素在各站位均未达检出限;海水重金属元素分布及污染情况整体呈现出:老爷海潟湖红树林区域优于小海潟湖红树林区域、连片自然林区域优于其他区域、河口区域劣于其他区域的特征;所有重金属元素中以Cu元素超标程度及生物风险程度相对较高;重金属主要来源于渔业养殖和农业生产等陆源人为活动以及港口运输及船舶尾气等的大气沉降,部分区域受到点源状人为活动的影响。相关评价结果可为万宁潟湖周边红树林生态系统保护提供参考。

  • 加载中
  • 图 1  海南万宁区域采样站位分布

    Figure 1. 

    图 2  万宁潟湖红树林区域各站位重金属元素含量分布

    Figure 2. 

    图 3  单因子污染指数(Pi)和综合污染指数(WQI)评价

    Figure 3. 

    图 4  各站位表层海水中重金属的Ei$ \mathrm{R}\mathrm{I} $

    Figure 4. 

    图 5  各重金属元素风险商评价

    Figure 5. 

    图 6  各重金属浓度及采样站位双向分层聚类分析图

    Figure 6. 

    表 1  水质综合污染指数评价标准[22-23]

    Table 1.  Assessment criterion of water pollution using WQI (water quality index)[22-23]

    WQI≤11<WQI≤22<WQI≤3WQI>3
    清洁轻微污染中度污染严重污染
    下载: 导出CSV

    表 2  重金属元素毒性响应系数及评价标准值[23-25]

    Table 2.  The metal toxicity coefficient and evaluation standard value[23-25]

    元素 Cu Zn Pb Cd As Cr Hg
    毒性响应系数 5 1 5 30 10 2 40
    评价标准值(μg/L) 5 20 1 1 20 50 0.05
    下载: 导出CSV

    表 3  潜在生态危害系数和指数评价标准[23,25-26]

    Table 3.  Assessment criterion on potential ecological harm using indices Ei and RI [23,25-26]

    潜在生态危害系数
    Ei
    Ei<40 40≤
    Ei<80
    80≤
    Ei<160
    160≤
    Ei<320
    Ei≥80
    轻微 中等 很强 极强
    潜在生态危害指数RI RI<150 150≤RI<300 300≤RI<600 RI≥300
    轻微 中等 很强
    下载: 导出CSV

    表 4  HC5取值及风险商评价标准[8]

    Table 4.  Evaluation criteria on HC5 value and risk quotient[8]

    元素 Cu Zn Pb Cd As Cr Hg
    /(μg/L) 3.46 25.54 234.06 1.07 0.5 25.43 2.84
    风险商RQ RQ≤0.1 0.1<RQ≤1 RQ>1
    低生态风险 中等生态风险 高生态风险
    下载: 导出CSV

    表 5  万宁潟湖红树林区域重金属含量

    Table 5.  Heavy metal contents in the mangrove area of Wanning Lagoon

    元素 Hg Cr Cu Zn Pb Cd As
    检出限/(μg/L) 0.007 0.400 0.200 3.100 0.030 0.010 0.500
    检出率/% 80 0 60 0 20 80 0
    范围/(μg/L) 0.0 035~0.124 0.1~48.2 0.015~4.00 0.005~1.17
    算术平均值/(μg/L) 0.044 14.975 0.695 0.628
    标准偏差/(μg/L) 0.041 16.754 1.415 0.407
    变异系数 0.914 1.119 2.036 0.649
    海水水质标准/(μg/L) 0.05 50 5 20 1 1 20
    0.2 100 10 20 5 5 30
    0.5 200 50 100 10 10 50
    500 500 50
    注:“—”表示未达检出限。
    下载: 导出CSV

    表 6  重金属质量浓度与海水环境因子的相关性分析

    Table 6.  Correlation analysis of mass concentration of heavy metals and environmental factors in seawater

      pH T SAL DO COD Hg Cu Pb Cd
    pH 1
    T 0.651** 1
    SAL −0.529* −0.094 1
    DO −0.299 −0.154 0.256 1
    COD 0.027 0.250 0.297 −0.246 1
    Hg −0.043 −0.095 −0.473* 0.128 −0.175 1
    Cu 0.524* 0.338 −0.107 −0.137 0.065 −0.242 1
    Pb 0.223 0.410 −0.102 −0.088 −0.150 0.052 0.443* 1
    Cd 0.159 −0.306 −0.475* −0.029 −0.312 0.152 −0.092 −0.044 1
    注:**表示在0.01水平下(双侧检验)相关性显著;*表示在0.05水平下(双侧检验)相关性显著。
    下载: 导出CSV
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出版历程
收稿日期:  2024-03-25
刊出日期:  2025-06-28

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