A bench‐scale treatability study was performed to evaluate the effectiveness of alkaline ozonation on removing per‐ and polyfluoroalkyl substances (PFAS) present in groundwater at a former industrial site in Michigan. The study involved testing the PFAS‐impacted groundwater under alkaline ozonating conditions under a range of experimental conditions, including modifying pH, hydrogen peroxide‐to‐ozone molar ratio doses, length of ozonation pretreatment times, and sampling techniques. PFAS‐spiked samples were used to determine if inorganic ions such as fluoride (F−), sulfate (SO42−), formate (HCOO−), acetate (CH3COO−), and trifluoroacetate (CF3COO−) were generated or if there were decreases in total organic fluorine resulting from PFAS treatment. The results from all tests indicate that decreases in PFAS concentrations were due to a combination of removal and destructive mechanisms with enhanced removal under acidic pH ozonation pretreatment conditions. Short‐chain PFAS concentrations increased during the experiments followed by an overall decrease in concentration under continuous alkaline ozonation conditions. Reductions in concentrations in perfluorooctane sulfonic acid of 75–97% were observed. Reductions in concentrations were also observed in other PFAS such as 6:2 FTS, PFHxS, PFOA, and PFNA. To our best knowledge, this is the first time that alkaline ozonation has been performed on PFAS‐impacted water while monitoring a larger suite of PFAS analytes in addition to destruction byproducts. Treatment of PFAS under the conditions discussed in this paper suggests that alkaline ozonation may be a viable remediation option for PFAS‐impacted waters.
Activated carbon (AC) adsorption continues to be the default technology to remove low levels of per-and polyfluoroalkyl substances (PFAS) from water, despite varying reports of the relatively early breakthrough of short-chain PFAS and high operating costs. Ion-exchange processes using regenerable and single-use media have been emerging as practical alternatives which may provide improved treatment and system performance. However, long-term performance with respect to the more difficult to remove short-chain PFAS such as perfluorobutanoic acid and perfluorobutanesulfonic acid is less often reported. Treatability testing on PFAS-impacted groundwater using batch-equilibration reactors and column flushing apparatus experiments was implemented to compare removal efficiency, breakthrough, and longevity of various media, specifically for shorter chain PFAS. Adsorbents tested included surface-modified natural media, synthetic resin, and AC. Results indicated that both surface modified natural media and AC achieved >99 percent removal of all detected PFAS after approximately 10,300-bed volumes (16 weeks) of column flushing, and outperformed the selected resin under site-specific conditions.In addition, unconventional breakthrough patterns (i.e., the breakthrough of longer chain PFAS before shorter chain PFAS) were observed for some PFAS including perfluoropentanoic acid, perfluorohexanesulfonic acid, and perfluorooctanesulfonic acid. The results of this study suggested that, while the generally accepted breakthrough patterns for PFAS can be reasonably anticipated, column flushing studies were preferred over batch sorption tests to reveal site-specific or mediaspecific breakthrough patterns that can impact overall performance. | INTRODUCTIONActivated carbon (AC) adsorption continues to be the default adsorption technology to remove low levels of poly-and perfluoroalkyl substances (PFAS) from water, despite varying reports of the relatively early breakthrough of short-chain PFAS and variable operating costs (Belkouteb et al., 2020;Speth et al., 2019). The adequacy of adsorption technologies to date has been judged primarily on the removal of perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) since these molecules were among the earliest to be detected in drinking water supplies and are being regulated at state levels and/or to municipal objectives. Technology performance with respect to the more difficult to remove short-chain PFAS (i.e., early breakthrough), such as perfluorobutanoic acid (PFBA) and perfluorobutanesulfonic acid (PFBS), has been gaining recognition (Westreich et al., 2018). It is anticipated that the regulated list of PFAS will continue to expand, and the
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