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Remediating Per- and Polyfluoroalkyl Substances (PFAS)-Contaminated Water by Foam Fractionation and Electrochemical Oxidation
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Researchers combined foam fractionation with electrochemical oxidation to remove PFAS "forever chemicals" from contaminated water, demonstrating that the two-step process can eliminate 80-90% of PFOA from water within 30 minutes and subsequently destroy 90-100% of the concentrated contaminant through oxidation.
Per- and polyfluoroalkyl substances (PFASs) are a family of synthetic chemicals that were used to improve the quality of several commercial products by making them resistant to heat, oil, stains, and grease. By containing a fluorinated carbon tail and a hydrophilic head (-COOH, -SO3H), PFASs act as surfactants that are attracted to bubble–water interfaces. Foam fractionation is the process of facilitating PFAS–air bubble interactions for the purpose of removing contaminants from tainted water. In this paper, we report on the use of foam fractionation and electrochemical oxidation (EO) under stirred batch conditions (200 mL) to remediate PFAS-contaminated water. We used radiolabeled PFOA (perfluorooctanoic acid; 14C-PFOA) as a representative surrogate to quickly screen treatment variables of flow rate, pH, temperature, and soap mass. Using radiolabeled PFASs eliminated the possibility of cross-contamination and greatly reduced analytical costs and processing time. The results showed that foam fractionation can remove 80 to 90 percent of PFOA from water within 30 min and that 90 to 100 percent of the PFOA in the concentrated foamate can be oxidized via electrochemical oxidation (-14COOH → 14CO2). We also tested the efficacy of the combined foam fractionation–EO treatment in natural waters by spiking 14C-PFOA and a cosolvent (CTAB) into PFAS-contaminated water obtained from two field sites with divergent PFAS concentrations and differing sources of PFAS contamination (natural drainage ditch vs. WWTP). Using a larger-scale tank (3500 mL), we observed that foam fractionation was 90% effective in removing 14C-PFOA from the WWTP effluent but only 50% effective for the drainage ditch water. Regardless, EO was highly effective in oxidizing 14C-PFOA in the foamate from both sources with half-lives (T1/2) ranging from 8.7 to 15 min. While water chemistry differences between source waters may have influenced foam fractionation and require additional investigations, tank experiments provide the first proof-of-concept experiment using 14C-PFASs that foam fractionation and electrochemical oxidation can be used in tandem to treat PFAS-contaminated water.
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Per- and polyfluoroalkyl substances (PFAS), often called "forever chemicals," are highly persistent contaminants found in water and soil worldwide. This review evaluates the leading remediation techniques available for removing PFAS from contaminated environments, comparing their effectiveness, scalability, and cost. Given PFAS's resistance to natural degradation, engineered removal strategies are essential for protecting drinking water sources and ecosystems.
Enhancing PFAS removal: feasibility of an integrated electrocoagulation and adsorptive membrane approach
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This review examines the potential of combining electrocoagulation with adsorptive membrane filtration as a tandem system for removing per- and polyfluoroalkyl substances (PFAS) from water, noting that the two technologies complement each other by targeting different chain lengths of these persistent chemicals. The integrated approach shows promise for high removal efficiency while also potentially degrading PFAS rather than merely concentrating them.
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Heterogeneous photocatalysis and electrochemical oxidation—particularly using BDD anodes and Ti4O7 membranes—achieve near-complete PFAS degradation, with solar-driven systems offering environmental benefits despite higher energy requirements. PFAS and microplastics are co-contaminants that often travel together in water systems and share chemical resistance to conventional treatment, making these advanced oxidation findings directly applicable to combined remediation strategies.
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This study tested a 10-liter ultrasonic reactor at 850–950 kHz to degrade PFAS compounds in three complex environmental matrices—groundwater, still bottom, and aqueous film-forming foam. Ultrasound effectively defluorinated PFAS in groundwater and still bottom samples, but PFOS-dominated AFFF resisted degradation due to its strong carbon-fluorine bonds, indicating matrix-specific limitations of sonolysis.
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Per- and polyfluoroalkyl substances (PFAS) resist conventional wastewater treatment and persist globally in aquatic environments, with monitoring and removal data highly variable across regions and methods. Photocatalytic membrane technologies show promise as a cost-credible, destructive treatment approach that improves catalyst reusability and degradation efficiency at scale.
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