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模拟生物曝气对受水成膜泡沫影响土壤中多氟和全氟烷基物质释放和转化的影响。

Simulating Impacts of Biosparging on Release and Transformation of Poly- and Perfluorinated Alkyl Substances from Aqueous Film-Forming Foam-Impacted Soil.

机构信息

Department of Civil and Environmental Engineering, Colorado School of Mines, 1500 Illinois St, Golden, Colorado 80401, United States.

Department of Civil and Environmental Engineering, University of California Berkeley, Berkeley, California 94720, United States.

出版信息

Environ Sci Technol. 2021 Dec 7;55(23):15744-15753. doi: 10.1021/acs.est.1c03448. Epub 2021 Nov 8.

DOI:10.1021/acs.est.1c03448
PMID:34748313
Abstract

Poly- and perfluorinated alkyl substances (PFASs) frequently co-occur with fuel-derived contaminants because of the use of aqueous film-forming foam (AFFF). Biosparging is a common remediation technology that injects oxygen into the saturated zone to encourage aerobic biodegradation, thereby altering aquifer redox conditions and potentially facilitating the biotransformation of polyfluorinated substances. Between 136 and 280 pore volumes of nitrogen-sparged or oxygen-sparged artificial groundwater amended with toluene were pumped through four saturated, AFFF-impacted soil columns to assess impacts on PFAS release and transformation. Column effluents and soils were analyzed for PFASs by high-resolution mass spectrometry. Significantly higher concentrations of five PFASs eluted from O-sparged columns compared to N-sparged columns shortly after sparging was initiated. The mass fractions eluted of many zwitterionic, sulfonamide-based PFASs were higher in both sets of columns than unaltered, non-biostimulated columns. Mass balance calculations suggested the transformation of sulfonamide-based precursors to perfluorinated sulfonamides (i.e., perfluorohexanesulfonamide) in oxygen- and nitrogen-sparged columns: recoveries of perfluorinated sulfonamides were 158-235% for C3-C6 homologs but recoveries of several prominent sulfonamide-based zwitterions were low. For example, the recovery of -carboxyethyldimethyl-ammoniopropyl perfluorohexanesulfonamide was 9-13%. These results suggest biosparging can enhance the transformation and release of PFASs in saturated soils, which has important implications for site characterization and remediation.

摘要

多氟和全氟烷基物质(PFAS)经常与源自燃料的污染物共同存在,因为使用了水成膜泡沫(AFFF)。生物曝气是一种常见的修复技术,它向饱和区注入氧气以鼓励好氧生物降解,从而改变含水层的氧化还原条件,并可能促进多氟化物质的生物转化。将含有甲苯的氮曝气或氧曝气人工地下水抽提 136-280 倍孔隙体积通过四个饱和的、受 AFFF 影响的土壤柱,以评估对 PFAS 释放和转化的影响。通过高分辨率质谱法对柱流出物和土壤中的 PFAS 进行分析。在曝气开始后不久,与氮曝气柱相比,氧曝气柱中洗脱的五种 PFAS 浓度显著更高。在两组柱中,许多两性离子、基于磺酰胺的 PFAS 的洗脱质量分数均高于未经改变的、未生物刺激的柱。质量平衡计算表明,在有氧和氮曝气柱中,磺酰胺基前体转化为全氟磺酰胺(即全氟己烷磺酰胺):C3-C6 同系物的全氟磺酰胺回收率为 158-235%,但几种主要的基于磺酰胺的两性离子回收率较低。例如,-羧乙基二甲基-丙基全氟己烷磺酰胺的回收率为 9-13%。这些结果表明,生物曝气可以增强饱和土壤中 PFAS 的转化和释放,这对场地特征描述和修复具有重要意义。

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