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Hydraulic Containment of TCE Contaminated Groundwater at the DOE Portsmouth Gaseous Diffusion Plant - 8069

机译:DOE朴茨茅斯气体扩散工厂的TCE污染地下水的水力遏制-8069

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This paper will describe the progress of a groundwater remedial action at the Portsmouth Gaseous Diffusion Plant (PORTS), a Department of Energy (DOE) facility that enriched uranium from the early 1950s until 2000. The X-749 southern boundary hydraulic containment system, combining a four-well extraction system with a previously constructed subsurface barrier wall, has been employed at PORTS. The hydraulic containment project has been implemented as part of containment and remediation of the X-749/X-120 area trichloroethylene (TCE) contaminant.The X-749/X-120 groundwater contaminant plume is located in the south central section (Quadrant I) of the PORTS facility. The plume is associated with the former X-120 Goodyear Training Facility and a landfill known as the X-749 Contaminated Materials Disposal Facility. The principal contaminants of concern are chlorinated solvents (primarily TCE) and technetium-99 (Tc-99). A subsurface barrier wall (X-749 South Barrier Wall) was completed in 1994 at the PORTS southern reservation boundary as an interim remedial measure to slow the advancement of the leading edge of the contaminated groundwater plume or to prevent the plume from migrating off DOE property. Remedial measures identified by Ohio Environmental Protection Agency (Ohio EPA) included installation of a barrier wall around the eastern and southern portions of the X-749 landfill to provide source control and installation of a phytoremediation system to help contain groundwater flow and remove volatile organic compounds. Previous remedial measures that were implemented as elements of 'closures' on the X-749 landfill included a multimedia cap, barrier walls, and a groundwater collection system. Despite these measures, the X-749/X-120 groundwater plume has migrated beyond the southern DOE property boundary. Current TCE concentrations in off-site groundwater monitoring wells are below the preliminary remediation goal and drinking water maximum contaminant level for TCE of 5 μg/kg, but continue to increase.Hydraulic containment was selected as the method for controlling the plume at the southern DOE property boundary. Recent borings and pumping tests indicate that approximately a 400-foot section of the existing subsurface barrier wall near the DOE property boundary may been improperly keyed into the Sunbury Shale bedrock which underlies the unconsolidated uppermost Gallia sand and gravel aquifer (Gallia). This gap is reported to be as much as 4 vertical feet. In addition, the X-749 groundwater plume is migrating around the western end of the X-749 South Barrier Wall.Four groundwater extraction wells were installed at the DOE property boundary to provide hydraulic control of the plume currently flowing under and around the existing subsurface barrier wall. Placement of the new extraction wells was based on groundwater modeling and data collected from pumping tests in the area. The extracted groundwater is being sent to the on-site X-622 Groundwater Treatment Facility via subsurface piping.The hydraulic containment system began operation in June 2007. The preliminary water elevations from monitoring wells in the vicinity of two of the four extraction wells demonstrate a significant decrease in groundwater potentiometric head in the southern boundary area. The current extraction rates should be adequate to contain the leading edge of the contaminant plume. Monitoring wells in the area will continue to be sampled on a quarterly basis.
机译:本文将描述朴茨茅斯气体扩散工厂(PORTS)的地下水补救行动的进展,该工厂是美国能源部(DOE)的一个设施,从1950年代初期到2000年,该铀浓缩了铀。X-749南部边界水力围堵系统结合起来PORTS已采用具有先前构造的地下防渗墙的四井抽采系统。液压遏制项目已作为X-749 / X-120区域三氯乙烯(TCE)污染物的遏制和修复工作的一部分而实施.X-749 / X-120地下水污染物羽流位于南部中部(象限I )。羽流与以前的X-120固特异培训设施和一个称为X-749污染材料处置设施的垃圾填埋场有关。关注的主要污染物是氯化溶剂(主要是TCE)和tech 99(Tc-99)。作为临时补救措施,1994年在PORTS南部保留区边界完成了地下屏障墙(X-749南屏障墙),以减缓受污染地下水羽流前缘的前进或防止羽流从DOE属性中迁移出来。 。俄亥俄州环境保护局(Ohio EPA)确定的补救措施包括在X-749垃圾填埋场的东部和南部附近安装隔离墙,以进行源头控制和安装植物修复系统以帮助抑制地下水流和去除挥发性有机化合物。以前作为X-749垃圾填埋场“封闭物”的组成部分采取的补救措施包括多媒体帽,隔离墙和地下水收集系统。尽管采取了这些措施,但X-749 / X-120地下水羽流已迁移到美国能源部南部财产边界之外。当前非现场地下水监测井中的三氯乙烯浓度低于初步补救目标,三氯乙烯的饮用水最大污染物水平为5μg/ kg,但仍在增加。选择液压遏制作为控制能源部南部烟羽的方法属性边界。最近的钻孔和抽水测试表明,在DOE属性边界附近的现有地下屏障墙的大约400英尺部分可能被不正确地锁入了Sunbury页岩基岩,该基岩位于未固结的最上部Gallia砂砾石含水层(Gallia)之下。据报道,该间隙多达4个垂直英尺。此外,X-749地下水羽流正在X-749南屏障墙的西端附近迁移。在DOE属性边界安装了四个地下水抽取井,以对当前在地下下和周围流动的羽流进行水力控制。隔离墙。新抽水井的布置基于地下水模型和该地区抽水试验收集的数据。抽取的地下水将通过地下管道输送到现场的X-622地下水处理设施。液压密封系统于2007年6月开始运行。来自四个抽取井中的两个的监测井的初步水高表明南部边界地区的地下水电位头明显下降。当前的抽气速率应足以容纳污染物羽流的前沿。该地区的监测井将继续按季度抽样。

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