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Contaminated Sediment TMDLs: An Oxymoron?

机译:污染的沉积物TMDL:一种矛盾体?

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Background/Objectives. Sediment contaminated with legacy pollutants such as pesticides,polychlorinated biphenyls (PCBs), and other chemicals banned from use years agorepresent a significant challenge to states’ total maximum daily load (TMDL) programs.These challenges manifest themselves in: (1) overlapping regulatory programs; (2) lackof existing point source discharges and site data; (3) atmospheric contaminant cycling;and (4) water quality standards established well below existing analytical capabilities.Approach/Activities. Many legacy pollutant sites are regulated under one or morefederal programs-including the Resource Conservation and Recovery Act (RCRA) andComprehensive Environmental Response, Compensation, and Liability Act (CERCLA)-that consider water quality standards as part of the process and as applicable or relevantand appropriate requirements. Consequently, legacy pollutant TMDLs oftenrepresent a form of regulatory double jeopardy. That is, successful execution of aCERCLA or RCRA cleanup does not preclude responsible parties from the TMDLprovisions of the Clean Water Act. Moreover, execution of legacy pollutant TMDLsoften invokes a double standard. Consider that the primary objective of the TMDLprogram is to restore our nation’s waters to their designated use (drinking water, recreation,support for aquatic life, or fishing). For legacy pollutants, this often translates intothe reduction of fish body burdens to levels acceptable for human consumption and theremoval of fish consumption advisories. However, once a legacy pollutant site makes itto a state’s 303(d) list based on consumption advisories, the TMDL process often involvesestablishing a water concentration target. In many instances, these concentrations,which are derived using bioaccumulation factors that relate human health risk-derivedfish body burdens with water column concentrations, are far below the analytical detectionlimit, exceed background pollutant concentrations, and are not supported by sitespecificdata.Results/Lessons Learned. One potential option is to apply to legacy pollutants thestrategy developed for mercury. That is, allow an “off ramp” in the form of a Category4(b) listing. This designation would require that controls implemented through existingregulatory programs (CERCLA, RCRA) are stringent enough to return the designateduses in a reasonable time period, as well as identify loading controls (e.g., best managementpractices, sediment remediation, and natural recovery). Moreover, establishingrecovery targets based on fish body burdens, rather than unmeasurable water qualitystandards, would simplify monitoring requirements and directly focus monitoring effortson the impaired use.
机译:背景/目标。沉积物被农药等传统污染物污染, 多年前禁止使用多氯联苯(PCB)和其他化学品 对各州的总最大每日负荷(TMDL)计划构成了重大挑战。 这些挑战体现在:(1)重叠的监管计划; (2)缺乏 现有的点源排放量和现场数据; (3)大气污染物循环; (4)建立的水质标准大大低于现有的分析能力。 方法/活动。许多遗留污染物场所受到一个或多个法规的监管 联邦计划-包括《资源保护和恢复法》(RCRA)和 综合环境响应,赔偿和责任法(CERCLA) -将水质标准视为过程的一部分,并视其为可适用或相关的 和适当的要求。因此,传统污染物TMDL通常 代表监管双重危险的一种形式。也就是说,成功执行 CERCLA或RCRA清理并不排除责任方参加TMDL 《清洁水法》的规定。此外,执行遗留污染物TMDL 通常会引用双重标准。考虑到TMDL的主要目标 计划是将我们国家的水恢复为指定用途(饮用水,娱乐活动, 支持水生生物或捕鱼)。对于遗留污染物,这通常会转化为 将鱼体负担减少到人类食用可接受的水平,并 取消鱼类消费咨询。但是,一旦遗留污染物位点 到根据消费咨询意见的州303(d)列表,TMDL流程通常涉及 建立水浓度目标。在许多情况下,这些浓度 使用与人类健康风险相关的生物蓄积因子得出 鱼体内水柱浓度的负担,远低于分析检测 限制,超过背景污染物浓度,并且不受特定地点的支持 数据。 结果/经验教训。一种潜在的选择是将遗留污染物应用于 制定汞战略。也就是说,以类别的形式允许“偏离斜坡” 4(b)清单。此名称将要求通过现有的控制措施来实施 监管计划(CERCLA,RCRA)的严格程度足以退还指定的 在合理的时间段内使用,以及确定加载控件(例如,最佳管理 实践,沉积物修复和自然恢复)。此外,建立 根据鱼体负担而不是不可衡量的水质确定恢复目标 标准,将简化监视要求并直接集中监视工作 禁止使用。

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