Department of Earth Sciences, Uppsala University, P.O. Box 256, SE-751 05 Uppsala, Sweden.
Department of Earth Sciences, Uppsala University, P.O. Box 256, SE-751 05 Uppsala, Sweden.
Ecotoxicol Environ Saf. 2023 Oct 1;264:115408. doi: 10.1016/j.ecoenv.2023.115408. Epub 2023 Sep 2.
Treatment of environmental media contaminated with per- and polyfluoroalkyl substances (PFAS) is crucial to mitigate mounting health risks associated with exposure. Colloidal activated carbon (CAC) has shown promise in treating contaminated soils, but understanding the interaction among PFAS during sorption is necessary for optimal remediation. This study investigated the extent to which PFAS of varying chain lengths and functional groups compete for sorption to CAC. Batch tests were conducted with natural soil and spiked water, using CAC at 0.2% w/w to remove seven PFAS with individual starting concentrations up to 0.05 mmol L. PFAS sorption to CAC was evaluated in three systems: a composite mixture of all studied compounds, a binary-solute system, and a single-solute system. The sorption experiments exhibited strong PFAS affinity to CAC, with removal rates between 41% and 100%, and solid/liquid partition coefficients (K) between 10 and 10 L kg. Differences were noticed among the various spiking mixtures, based on perfluorocarbon chain length, functional group, and the starting PFAS concentrations. Competition effects were detected when PFAS were in a multi-solute system, with an average 10% drop in removal, which can evidently become more relevant at higher concentrations, due to the observed non-linearity of the sorption process. The PFAS most vulnerable to competition effects in multi-solute systems were the short-chain perfluoropentanoic acid (PFPeA) and perfluorobutane sulfonic acid (PFBS), with an up to 25% reduction in removal. In bi-solute systems, perfluorooctane sulfonamide (FOSA) dominated over its ionisable counterparts, i.e. perfluorooctane sulfonic acid (PFOS) and perfluorononanoic acid (PFNA), indicating the importance of hydrophobic effects or layer formation in the sorption process. These results underscore the importance of considering competition in PFAS sorption processes when designing and implementing remediation techniques for PFAS-contaminated media.
处理环境介质中受全氟和多氟烷基物质(PFAS)污染的物质对于减轻与暴露相关的日益严重的健康风险至关重要。胶体活性炭(CAC)在处理受污染土壤方面显示出了很大的前景,但为了实现最佳修复效果,了解 PFAS 在吸附过程中的相互作用是必要的。本研究调查了不同链长和官能团的 PFAS 在竞争吸附到 CAC 方面的程度。使用 0.2%(w/w)的 CAC 进行了天然土壤和加标水的批量测试,以去除七种起始浓度高达 0.05mmol/L 的 PFAS。在三个系统中评估了 PFAS 对 CAC 的吸附:所有研究化合物的复合混合物系统、二元溶质系统和单一溶质系统。吸附实验表明,PFAS 对 CAC 具有很强的亲和力,去除率在 41%至 100%之间,固/液分配系数(K)在 10 至 10 L/kg 之间。基于全氟碳链长度、官能团和起始 PFAS 浓度,各种加标混合物之间存在差异。当 PFAS 处于多溶质系统中时,会检测到竞争效应,去除率平均下降 10%,由于吸附过程的非线性,在较高浓度下,这种效应可能变得更加相关。在多溶质系统中最容易受到竞争效应影响的 PFAS 是短链全氟戊酸(PFPeA)和全氟丁烷磺酸(PFBS),去除率下降高达 25%。在双溶质系统中,全氟辛烷磺酰胺(FOSA)比其可离子化的对应物,即全氟辛烷磺酸(PFOS)和全氟壬酸(PFNA)更占主导地位,这表明在吸附过程中疏水性效应或层形成的重要性。这些结果强调了在设计和实施受 PFAS 污染介质的修复技术时,考虑 PFAS 吸附过程中的竞争作用的重要性。