2020年,宾夕法尼亚州卢塞恩县Valmont TCE超级基金站点的水文地质框架、水位和选定污染物浓度

L. Senior, A. R. Fiore, P. H. Bird
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引用次数: 1

摘要

位于宾夕法尼亚州Luzerne县的Valmont TCE超级基金基地位于Pottsville和Mauch块状地层的断裂和折叠砂岩和页岩之下,形成了一个由降水补充的断裂岩石含水层。该工厂的工业活动导致该工厂及其附近的地下水受到三氯乙烯(TCE)的污染,该污染于1987年被发现,并于1989年被美国环境保护署(EPA)列为超级基金遗址。为了解决附近居民水井中TCE浓度超过饮用水最大污染物水平(MCL) 5微克/升(μg/L)的问题,提供了替代供水。2015年,EPA对最初的特征和随后的补救进行了审查,确定需要对复杂的水文地质和概念场地模型进行更新的理解。现场地下水中存在的其他污染物包括一些其他挥发性有机化合物(VOCs)和perand polyfluoroalkyl物质(PFAS),主要由全氟辛酸(PFOA)和全氟辛烷磺酸(PFOS)组成,其测量浓度超过了EPA健康咨询(HA)的标准,即全氟辛酸和全氟辛烷磺酸的组合浓度为每升5纳克(ng/L)。为了响应美国环保署在2019年的要求,美国地质调查局(USGS)准备了横截面和地图,以提供有关现场及附近水文地质框架的更多信息,并利用美国环保署在2020年收集的水位和污染物数据协助改进概念现场模型。截面显示了2002年至2014年收集的井中可用的地球物理测井资料的岩性相关性;它们显示出自然伽马活动相对升高和降低的交替间隔,与岩性变化相对应,含水带和井筛通常位于岩性接触处,有时靠近薄煤层。含水带通常与岩性接触处或其附近的裂缝有关,但也可能与明显断裂处或其附近的裂缝有关。最近(2020年3月)断面和地图上显示的水位数据表明,东北、西北和西南的横向垂直梯度和明显的径向梯度大致与地形一致。最近(2020年2月至3月)在横断面和地图上显示的地下水TCE浓度数据表明,TCE浓度最高(高于3000 μg/L和高达75000 μg/L)以及PFOA和PFOS的综合浓度(高于1000 ng/L和高达至少2350 ng/L)来自前Chromatex工厂中心附近的浅层(低于地表60英尺)和中深度(60至100英尺)井。三氯乙烯和全氟辛烷磺酸(PFOA和全氟辛烷磺酸的组合)污染存在于更深的地下水中,高达304英尺/英尺,从工厂附近的一口井(重建的前生产井)收集的样本证明,其浓度分别约为240 μg/L和508 ng/L。2020年的数据还表明,在从原Chromatex工厂向东北方向延伸的区域,地下水深度小于200英尺的地方,TCE和PFAS浓度超过饮用水MCL或HA水平,并且明显受到水力梯度、岩性和地质结构的影响。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Hydrogeologic framework, water levels, and selected contaminant concentrations at Valmont TCE Superfund Site, Luzerne County, Pennsylvania, 2020
The Valmont TCE Superfund Site, Luzerne County, Pennsylvania is underlain by fractured and folded sandstones and shales of the Pottsville and Mauch Chunk Formations, which form a fractured-rock aquifer recharged locally by precipitation. Industrial activities at the former Chromatex Plant resulted in trichloroethene (TCE) contamination of groundwater at and near the facility, which was identified in 1987 and led to listing as a Superfund site by the U.S. Environmental Protection Agency (EPA) in 1989. To address the problem of TCE concentrations in nearby residential wells that exceed the maximum contaminant level (MCL) of 5 micrograms per liter (μg/L) for drinking water, alternate water supplies were provided. A 2015 review of initial characterization and subsequent remediation by the EPA identified the need for an updated understanding of the complex hydrogeology and the conceptual site model. Additional contaminants present in groundwater at the site include some other volatile organic compounds (VOCs) and perand polyfluoroalkyl substances (PFAS), predominantly consisting of perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) measured in concentrations that exceeded the EPA Health Advisory (HA) level of 5 nanograms per liter (ng/L) for combined PFOA and PFOS. In response to a request from the EPA in 2019, the U.S. Geological Survey (USGS) prepared cross sections and maps to provide more information about the hydrogeologic framework at and near the site and assist in improving the conceptual site model using water level and contaminant data collected by the EPA in 2020. The cross sections present lithologic correlations from available geophysical logs collected in wells from 2002 to 2014; they show alternating intervals of relatively elevated and reduced natural gamma activity that correspond to changes in lithology, with waterbearing zones and well screens commonly located at lithologic contacts, sometimes near thin coal seams. Water-bearing zones commonly are associated with fractures at or near lithologic contacts but also may be associated with fractures at or near apparent faulting. Recent (March 2020) water-level data shown on cross sections and maps indicate large downward vertical gradients and apparent radial gradients laterally to the northeast, northwest, and southwest that generally following topography. Recent (February to March 2020) data for TCE groundwater concentration shown on cross sections and maps indicate the highest TCE concentrations (greater than 3,000 μg/L and as much as 75,000 μg/L) and combined PFOA and PFOS concentrations (greater than 1,000 ng/L and up to at least 2,350 ng/L) are from shallow (less than 60 feet [ft] below land surface [bls]) and intermediate depth (60 to 100 ft bls) wells near the center of the former Chromatex Plant. TCE and PFAS (as combined PFOA and PFOS) contamination is present in groundwater at greater depths, as much as 304 ft bls, as evidenced by samples collected from one well (a reconstructed former production well) near the plant, that contained concentrations of about 240 μg/L and 508 ng/L, respectively. The 2020 data also indicate that TCE and PFAS concentrations which exceed drinking-water MCL or HA levels are present in groundwater depths of less than 200 ft in an area that extends predominantly in a northeast direction from the former Chromatex Plant, and is apparently influenced by hydraulic gradients, lithology, and geologic structure.
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