St. Anthony Falls Laboratory, University of Minnesota, Minneapolis, MN 55414, USA.
Division of Environmental Health Sciences, School of Public Health, University of Minnesota, Minneapolis, MN 55455, USA.
Water Res. 2015 Apr 1;72:64-74. doi: 10.1016/j.watres.2014.09.052. Epub 2014 Oct 13.
Perfluorooctane sulfonate (PFOS) and perfluorooctanoate (PFOA) are emerging anthropogenic compounds that have recently become the target of global concern due to their ubiquitous presence in the environment, persistence, and bioaccumulative properties. This study was carried out to investigate the migration of PFOS and PFOA in soils and groundwater in a U.S. metropolitan area. We observed elevated levels in surface soils (median: 12.2 ng PFOS/g dw and 8.0 ng PFOA/g dw), which were much higher than the soil-screening levels for groundwater protection developed in this study. The measured levels in subsurface soils show a general increase with depth, suggesting a downward movement toward the groundwater table and a potential risk of aquifer contamination. Furthermore, concentrations of PFOS and PFOA in monitoring wells in the source zone varied insignificantly over 5 years (2009-2013), suggesting limited or no change in either the source or the magnitude of the source. The analysis also shows that natural processes of dispersion and dilution can significantly attenuate the groundwater contamination; the adsorption on aquifer solids, on the other hand, appears to have limited effects on the transport of PFOS and PFOA in the aquifer. The probabilistic exposure assessment indicates that ingestion of contaminated groundwater constitutes a much more important exposure route than ingestion of contaminated soil. Overall, the results suggest that (i) the transport of PFOS and PFOA is retarded in the vadose zone, but not in the aquifer; (ii) the groundwater contamination of PFOS and PFOA often follows their release to surface soils by years, if not decades; and (iii) the aquifer can be a major source of exposure for communities living near point sources.
全氟辛烷磺酸 (PFOS) 和全氟辛酸 (PFOA) 是新兴的人为化合物,由于它们在环境中的普遍存在、持久性和生物累积性,最近成为全球关注的焦点。本研究旨在调查全氟辛烷磺酸和全氟辛酸在美国大都市地区土壤和地下水中的迁移情况。我们观察到表层土壤中(中位数:12.2ng PFOS/gdw 和 8.0ng PFOA/gdw)的含量升高,远高于本研究中为保护地下水而制定的土壤筛选水平。地下土壤中的测量水平随深度呈普遍增加趋势,表明它们向下移动到地下水面,存在含水层污染的潜在风险。此外,在源区的监测井中,PFOS 和 PFOA 的浓度在 5 年内(2009-2013 年)变化不大,这表明源区或源的强度没有变化或变化很小。分析还表明,自然扩散和稀释过程可以显著减轻地下水的污染;另一方面,含水层固体的吸附对 PFOS 和 PFOA 在含水层中的迁移似乎影响有限。概率暴露评估表明,受污染地下水的摄入比受污染土壤的摄入构成更重要的暴露途径。总体而言,结果表明:(i) PFOS 和 PFOA 的迁移在包气带中受到阻碍,但在含水层中不受阻碍;(ii) 地下水的 PFOS 和 PFOA 污染通常会在其释放到地表土壤多年后(如果不是几十年后)才会发生;以及 (iii) 含水层可能是居住在点源附近的社区的主要暴露源。