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污染地块土壤砷修复目标值确定方法研究

刘虎鹏 杜平 袁贝 张云慧 陈娟 张昊

刘虎鹏,杜平,袁贝,等.污染地块土壤砷修复目标值确定方法研究[J].环境工程技术学报,2024,14(1):130-138 doi: 10.12153/j.issn.1674-991X.20230267
引用本文: 刘虎鹏,杜平,袁贝,等.污染地块土壤砷修复目标值确定方法研究[J].环境工程技术学报,2024,14(1):130-138 doi: 10.12153/j.issn.1674-991X.20230267
LIU H P,DU P,YUAN B,et al.Study on methods for determining the remediation target value of soil arsenic in contaminated sites[J].Journal of Environmental Engineering Technology,2024,14(1):130-138 doi: 10.12153/j.issn.1674-991X.20230267
Citation: LIU H P,DU P,YUAN B,et al.Study on methods for determining the remediation target value of soil arsenic in contaminated sites[J].Journal of Environmental Engineering Technology,2024,14(1):130-138 doi: 10.12153/j.issn.1674-991X.20230267

污染地块土壤砷修复目标值确定方法研究

doi: 10.12153/j.issn.1674-991X.20230267
基金项目: 国家重点研发计划项目(2020YFC1806304)
详细信息
    作者简介:

    刘虎鹏 (1998—),男,硕士研究生,主要从事污染场地调查评价与修复研究,liuhupeng6@163.com

    通讯作者:

    杜平(1980—),女,研究员,主要从事土壤污染防治研究,duping@craes.org.cn

  • 中图分类号: X53

Study on methods for determining the remediation target value of soil arsenic in contaminated sites

  • 摘要:

    修复目标值的确定是污染地块环境监管的重要环节,通常基于风险评估方法计算风险控制值来确定。而对于砷污染地块,采用HJ 25.3—2019《建设用地土壤污染风险评估技术导则》推荐模型和参数推算得到的修复目标值往往低于土壤砷环境背景值,难以满足监管需求。系统梳理了国内外污染地块土壤砷修复目标值确定方法,探讨了基于土壤环境标准值、传统风险评估、层次化风险评估、等效风险评估及土壤砷环境背景值修正方法的实现路径与实践应用。结合我国污染地块监管策略和砷污染地块开发再利用现状,提出了基于土壤环境背景值、层次化风险评估和生物可给性相关参数修正的土壤砷修复目标值确定方法,旨在为我国砷污染地块的修复和再利用提供更加科学合理的方案。

     

  • 图  1  我国污染地块土壤砷修复目标值确定依据及取值

    注:括号中的数字为污染地块数量。

    Figure  1.  Values and sources for determining the target values of arsenic remediation in contaminated sites in China

    图  2  基于层次化风险评估确定污染地块土壤砷修复目标值流程

    Figure  2.  Process for determining target values for arsenic remediation in contaminated site based on tiered risk assessment

    图  3  等效风险参数的获取方法

    注:①、②、③、④推导过程分别对应式(2)、式(4)、式(5)、式(3)。

    Figure  3.  Methods for obtaining equivalent risk parameters

    图  4  基于CLEA模型的传统风险评估及等效风险评估中砷浓度与ID/HCV的浓度-效应关系

    Figure  4.  Concentration-effect relationships between As concentrations and ID/HCV values in conventional and equivalent risk assessments based on CLEA models

    图  5  我国各地区土壤砷环境背景值[37]

    Figure  5.  Background values of soil arsenic by regions in China

    图  6  生物可给性对土壤砷修复目标值的影响

    Figure  6.  Effect of bioaccessibility on target values for soil arsenic remediation

    表  1  不同国家土壤砷环境标准出处、名称及取值

    Table  1.   Sources, names and values of screening values for different countries

    国家 出处 名称 取值/(mg/kg) 数据来源
    中国1) 《土壤环境质量 建设用地土壤污染风险管控标准(试行)》 筛选值 20(一类用地);
    60(二类用地)
    文献[17]
    加拿大1) 《加拿大土壤环境质量指南》
    《保护环境和人体健康土壤质量
    指导值的指南》
    土壤质量指导值
    (soil quality guidelines)
    12(除特定地点外);
    160(黄刀地区居住用地),
    340(黄刀地区工业用地),
    220(黄刀地区公共场所)
    文献[18-19]
    德国1) 《联邦土壤保护与污染场地条例》
    触发值
    (trigger values)
    25(儿童乐园);
    50(住宅区);
    125(公园-休闲设施);
    140(工商业用地)
    文献[20]
    日本1) 《土壤环境质量标准》 土壤环境质量标准
    (environment quality standards for soil)
    150 文献[21]
    美国2) 《区域筛选值表》 区域筛选值
    (regional screening levels)
    0.68(居住用地);
    3(工业用地)
    文献[22]
    英国2) 《土壤中无机砷的指导值》 土壤指导值
    (soil guideline values)
    32(居住用地);
    43(菜地);
    640(商业用地)
    文献[23]
    荷兰2) 《土壤修复通告》 干预值(intervention value) 76 文献[24]
      1)土壤砷环境标准值可作为土壤砷修复目标值;2)土壤砷环境标准值通常不作为土壤砷修复目标值。
    下载: 导出CSV
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  • 收稿日期:  2023-04-04
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