Umeh Anthony C, Hassan Masud, Egbuatu Maureen, Zeng Zijun, Al Amin Md, Samarasinghe Chamila, Naidu Ravi
Global Centre for Environmental Remediation (GCER), The University of Newcastle, Callaghan, NSW 2308, Australia; crcCARE, The University of Newcastle, Callaghan, NSW 2308, Australia.
Global Centre for Environmental Remediation (GCER), The University of Newcastle, Callaghan, NSW 2308, Australia.
Sci Total Environ. 2023 Dec 15;904:166568. doi: 10.1016/j.scitotenv.2023.166568. Epub 2023 Aug 24.
The adsorption and desorption of 9 PFAS, including 3 perfluoroalkyl sulphonic and 6 perfluoroalkyl carboxylic acids, in artificial groundwater was investigated using 3 commercial adsorbents that comprised a powdered activated carbon (PAC), a surface-modified organoclay (NMC+), and a carbonaceous organic amendment (ROAC). Sorption kinetics and isotherms of PFAS, as well as the effects of adsorbent dose, pH, index ion and ionic strength on PFAS adsorption and desorption were investigated. Sorption of multicomponent PFAS in the adsorbents was rapid, especially for NMC+ and ROAC, regardless of PFAS chain length. The sorption and (and especially) desorption of PFAS in the adsorbents was impacted by the pH, index ion, and ionic strength of simulated groundwater, especially for the short chain PFAS, with only minimal impacts on NMC+ and PAC compared to ROAC. Although the potential mineral and charged constituents of the adsorbents contributed to the adsorption of short chain PFAS through electrostatic interactions, these interactions were susceptible to variable groundwater chemistry. Hydrophobic interactions also played a major role in facilitating and increasing PFAS sorption, especially in adsorbents with aliphatic functional groups. The desorption of PFAS from the adsorbents was below 8 % when the aqueous phase was deionised water, with no measurable desorption for NMC+. In contrast, the desorption of short chain PFAS in simulated groundwater increased substantially (30-100 %) in the adsorbents, especially in ROAC and NMC+, but more so with ROAC. In general, the three adsorbents exhibited strong stability for the long chain PFAS, especially the perfluoroalkyl sulphonic acids, with minimal to no sorption reversibility under different pH and ionic composition of simulated groundwater. This study highlights the importance of understanding not only the sorption of PFAS in groundwater using adsorbents, but also the desorption of PFAS, which may be useful for decision making during the ex-situ and in-situ treatment of PFAS-contaminated groundwater.
使用三种商业吸附剂(包括粉末活性炭(PAC)、表面改性有机粘土(NMC+)和碳质有机改良剂(ROAC))研究了9种全氟辛烷磺酸(PFAS)(包括3种全氟烷基磺酸和6种全氟烷基羧酸)在人工地下水中的吸附和解吸情况。研究了PFAS的吸附动力学和等温线,以及吸附剂剂量、pH值、指示离子和离子强度对PFAS吸附和解吸的影响。无论PFAS链长如何,吸附剂中多组分PFAS的吸附都很快,尤其是对于NMC+和ROAC。吸附剂中PFAS的吸附和解吸(尤其是解吸)受到模拟地下水的pH值、指示离子和离子强度的影响,特别是对于短链PFAS,与ROAC相比,对NMC+和PAC的影响最小。尽管吸附剂中的潜在矿物质和带电成分通过静电相互作用促进了短链PFAS的吸附,但这些相互作用易受地下水化学变化的影响。疏水相互作用在促进和增加PFAS吸附方面也起主要作用,尤其是在具有脂肪族官能团的吸附剂中。当水相为去离子水时,PFAS从吸附剂中的解吸率低于8%,NMC+没有可测量的解吸。相比之下,模拟地下水中短链PFAS在吸附剂中的解吸显著增加(30%-100%),尤其是在ROAC和NMC+中,但ROAC中增加得更多。总体而言,三种吸附剂对长链PFAS(尤其是全氟烷基磺酸)表现出很强的稳定性,在模拟地下水的不同pH值和离子组成下,吸附可逆性极小或没有。这项研究强调了不仅要了解使用吸附剂对地下水中PFAS的吸附,还要了解PFAS的解吸的重要性,这对于PFAS污染地下水的异位和原位处理过程中的决策可能是有用的。