QAEHS, Queensland Alliance for Environmental Health Sciences, The University of Queensland, Brisbane, Queensland 4102, Australia.
School of Agriculture, Food and Wine, The University of Adelaide, Waite Campus, PMB1, Glen Osmond, South Australia 5064, Australia.
Environ Sci Technol. 2020 Dec 15;54(24):15883-15892. doi: 10.1021/acs.est.0c05705. Epub 2020 Nov 28.
The aim of this study was to assess the soil-water partitioning behavior of a wider range of per- and polyfluoroalkyl substances (PFASs) onto soils covering diverse soil properties. The PFASs studied include perfluoroalkyl carboxylates (PFCAs), perfluoroalkane sulfonates (PFSAs), fluorotelomer sulfonates (FTSs), nonionic perfluoroalkane sulfonamides (FASAs), cyclic PFAS (PFEtCHxS), per- and polyfluoroalkyl ether acids (GenX, ADONA, 9Cl-PF3ONS), and three aqueous film-forming foam (AFFF)-related zwitterionic PFASs (AmPr-FHxSA, TAmPr-FHxSA, 6:2 FTSA-PrB). Soil-water partitioning coefficients (log values) of the PFASs ranged from less than zero to approximately three, were chain-length-dependent, and were significantly linearly related to molecular weight (MW) for PFASs with MW > 350 g/mol ( = 0.94, < 0.0001). Across all soils, the values of all short-chain PFASs (≤5 -CF2- moieties) were similar and varied less (<0.5 log units) compared to long-chain PFASs (>0.5 to 1.5 log units) and zwitterions AmPr- and TAmPr-FHxSA (∼1.5 to 2 log units). Multiple soil properties described sorption of PFASs better than any single property. The effects of soil properties on sorption were different for anionic, nonionic, and zwitterionic PFASs. Solution pH could change both PFAS speciation and soil chemistry affecting surface complexation and electrostatic processes. The values of all PFASs increased when solution pH decreased from approximately eight to three. Short-chain PFASs were less sensitive to solution pH than long-chain PFASs. The results indicate the complex interactions of PFASs with soil surfaces and the need to consider both PFAS type and soil properties to describe mobility in the environment.
本研究旨在评估更广泛范围的全氟和多氟烷基物质(PFAS)在覆盖各种土壤特性的土壤中的土壤-水分配行为。所研究的 PFAS 包括全氟烷基羧酸(PFCAs)、全氟烷磺酸(PFSAs)、氟代烷烃磺酸盐(FTSs)、非离子全氟烷磺酸酰胺(FASAs)、环状 PFAS(PFEtCHxS)、全氟和多氟烷基醚酸(GenX、ADONA、9Cl-PF3ONS)以及三种水性成膜泡沫(AFFF)相关的两性离子 PFAS(AmPr-FHxSA、TAmPr-FHxSA、6:2 FTSA-PrB)。PFAS 的土壤-水分配系数(log 值)范围从小于零到大约三,与链长有关,并且与 MW>350 g/mol 的 PFAS 的分子量(MW)呈显著线性关系( = 0.94, < 0.0001)。在所有土壤中,所有短链 PFAS(≤5-CF2- 部分)的 值相似,与长链 PFAS(>0.5 至 1.5 log 单位)和两性离子 AmPr-和 TAmPr-FHxSA(∼1.5 至 2 log 单位)相比变化较小(<0.5 log 单位)。多种土壤特性比任何单一特性更能描述 PFAS 的吸附。阴离子、非离子和两性离子 PFAS 的吸附受土壤特性的影响不同。溶液 pH 既可以改变 PFAS 的形态,也可以改变土壤化学性质,从而影响表面络合和静电过程。当溶液 pH 从大约 8 降至 3 时,所有 PFAS 的 值均增加。短链 PFAS 对溶液 pH 的敏感性低于长链 PFAS。结果表明 PFAS 与土壤表面的复杂相互作用,需要考虑 PFAS 类型和土壤特性来描述环境中的迁移性。