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Integrating Federal and State Requirements for Managing PCB Remediation Wastes - A Case Study at a Former MGP Site

机译:整合联邦和国家要求管理PCB补救废物的要求 - 以前MGP网站为例

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Baltimore Gas and Electric Company's (BGE) Spring Gardens site is undergoing remediation for a historic release of PCB-contaminated oil that originally contained between 50 and 250 ppm PCBs. Extensive treatment of the co-recovered groundwater is required prior to its discharge via an NPDES-permitted outfall, because the site retains the legacy from over 100 years of manufactured (coal) gas production. The groundwater treatment system produces separated oil and several process treatment residuals. Prior to the U.S. EPA's June 1998 PCB MEGA Rule, all process residuals had to be managed based upon the PCB concentration of the original PCB source (oils). In addition, Maryland's hazardous waste regulations required that the oils and process residuals that were mixed with, or derived from, the PCB-contaminated oils had to be managed as a state hazardous waste. BGE observed, during early stages of the recovery system trials, that PCBs were not present in the process residuals, but were being segregated in the recovered oils. We realized that managing some or all of the process treatment residuals as non-PCB, non-hazardous waste could significantly reduce disposal costs. Therefore, we initiated a program in mid-1997 to obtain variances for the process residuals from TSCA and State hazardous waste regulation, realizing that separate approvals were required from both U.S. EPA's Region III and Maryland's Department of the Environment. An extensive sampling and analysis program performed at key points throughout the treatment process documented and confirmed our hypothesis that PCBs exited the system in the recovered oil and that no dilution or degradation of the PCBs was occurring. The new definition and disposal requirements for "PCB remediation waste" in EPA's MEGA Rule enabled BGE to obtain a clarification from EPA Region III, that the process residuals and recovered oil could be managed based upon their "as generated" PCB concentration, rather than based upon the PCBs in the originally-released oils. Subsequently, we were able to use the same data to obtain a similar clarification from Maryland's Department of the Environment regarding the non-hazardous status of the process residuals.
机译:巴尔的摩天然气和电气公司(BGE)春季花园遗址正在进行修复历史遗传释放的PCB污染的油,最初包含在50至250ppm PCB之间。在通过NPDES允许的出口放电之前需要进行共回地下水的广泛处理,因为该部位从100多年的制造(煤)天然气生产中保留了遗产。地下水处理系统产生分离的油和几种过程处理残留物。在美国EPA的1998年6月之前,必须基于原始PCB源(油)的PCB浓度来管理所有过程残差。此外,马里兰州的危险废物规定要求与污染的PCB污染的油混合或衍生的油和工艺残留物必须作为国家危险废物管理。在恢复系统试验的早期阶段观察到BGE,PCB不存在于过程残留中,但在回收的油中被隔离。我们意识到,管理部分或全部过程处理残余物作为非PCB,无危险废物可以显着降低处置成本。因此,我们在1997年年中启动了一项计划,以获得来自TSCA和国家危险废物监管的过程残留的差异,从而实现了美国EPA地区和马里兰州的环境部门所需的单独批准。在整个治疗过程中进行的广泛采样和分析程序记录并确认了我们的假设,即PCB在回收的油中离开了系统,并且没有稀释或氯化单的降解发生。 EPA的Mega规则的“PCB修复废物”的新定义和处置要求使BGE能够从EPA区域III获得澄清,即工艺残留和回收的油可以根据其“作为生成的”PCB浓度,而不是基于基于在最初释放的油中的PCB上。随后,我们能够使用相同的数据来获得Maryland的环境部门的类似澄清,了解过程残留的非危险状态。

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