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Enhanced perfluorooctanoic acid (PFOA) degradation by electrochemical activation of peroxydisulfate (PDS) during electrooxidation for water treatment.
Samuel, Melvin S; Kadarkarai, Govindan; Ryan, Donald R; McBeath, Sean T; Mayer, Brooke K; McNamara, Patrick J.
Afiliación
  • Samuel MS; Department of Civil, Construction and Environmental Engineering, Marquette University, Milwaukee, WI 53233, United States.
  • Kadarkarai G; Department of Civil, Construction and Environmental Engineering, Marquette University, Milwaukee, WI 53233, United States.
  • Ryan DR; Department of Civil, Construction and Environmental Engineering, Marquette University, Milwaukee, WI 53233, United States.
  • McBeath ST; Department of Civil and Environmental Engineering, University of Massachusetts Amherst, Amherst, MA 01003, United States.
  • Mayer BK; Department of Civil, Construction and Environmental Engineering, Marquette University, Milwaukee, WI 53233, United States.
  • McNamara PJ; Department of Civil, Construction and Environmental Engineering, Marquette University, Milwaukee, WI 53233, United States. Electronic address: patrick.mcnamara@marquette.edu.
Sci Total Environ ; 942: 173736, 2024 Sep 10.
Article en En | MEDLINE | ID: mdl-38839010
ABSTRACT
Improved treatment of per- and polyfluoroalkyl substances (PFAS) in water is critically important in light of the proposed United States Environmental Protection Agency (USEPA) drinking water regulations at ng L-1 levels. The addition of peroxymonosulfate (PMS) during electrooxidation (EO) can remove and destroy PFAS, but ng L-1 levels have not been tested, and PMS itself can be toxic. The objective of this research was to test peroxydisulfate (PDS, an alternative to PMS) activation by boron-doped diamond (BDD) electrodes for perfluorooctanoic acid (PFOA) degradation. The influence of PDS concentration, temperature, and environmental water matrix effects, and PFOA concentration on PDS-EO performance were systematically examined. Batch reactor experiments revealed that 99 % of PFOA was degraded and 69 % defluorination was achieved, confirming PFOA mineralization. Scavenging experiments implied that sulfate radicals (SO4-) and hydroxyl radicals (HO) played a more important role for PFOA degradation than 1O2 or electrons (e-). Further identification of PFOA degradation and transformation products by liquid chromatography-mass spectrometry (LC-MS) analysis established plausible PFOA degradation pathways. The analysis corroborates that direct electron transfers at the electrode initiate PFOA oxidation and SO4- improves overall treatment by cleaving the CC bond between the C7F15 and COOH moieties in PFOA, leading to possible products such as C7F15 and F-. The perfluoroalkyl radicals can be oxidized by SO4- and HO, resulting in the formation of shorter chain perfluorocarboxylic acids (e.g., perfluorobutanoic acid [PFBA]), with eventual mineralization to CO2 and F-. At an environmentally relevant low initial concentration of 100 ng L-1 PFOA, 99 % degradation was achieved. The degradation of PFOA was slightly affected by the water matrix as less removal was observed in an environmental river water sample (91 %) compared to tests conducted in Milli-Q water (99 %). Overall, EO with PDS provided a destructive approach for the elimination of PFOA.
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Texto completo: 1 Colección: 01-internacional Base de datos: MEDLINE Idioma: En Revista: Sci Total Environ Año: 2024 Tipo del documento: Article País de afiliación: Estados Unidos Pais de publicación: Países Bajos

Texto completo: 1 Colección: 01-internacional Base de datos: MEDLINE Idioma: En Revista: Sci Total Environ Año: 2024 Tipo del documento: Article País de afiliación: Estados Unidos Pais de publicación: Países Bajos