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Biochar and surfactant synergistically enhanced PFAS destruction in UV/sulfite system at neutral pH.
He, Jianzhou; Boersma, Melissa; Song, Ziteng; Krebsbach, Samuel; Fan, Dimin; Duin, Evert C; Wang, Dengjun.
Affiliation
  • He J; School of Fisheries, Aquaculture and Aquatic Sciences, Auburn university, Auburn, 36849, United States.
  • Boersma M; Department of Chemistry and Biochemistry, Auburn university, Auburn, 36849, United States.
  • Song Z; School of Fisheries, Aquaculture and Aquatic Sciences, Auburn university, Auburn, 36849, United States.
  • Krebsbach S; School of Fisheries, Aquaculture and Aquatic Sciences, Auburn university, Auburn, 36849, United States.
  • Fan D; Geosyntec Consultants, Inc, 10211 Wincopin Circle, 4th Floor, Columbia, 21044, United States.
  • Duin EC; Department of Chemistry and Biochemistry, Auburn university, Auburn, 36849, United States.
  • Wang D; School of Fisheries, Aquaculture and Aquatic Sciences, Auburn university, Auburn, 36849, United States. Electronic address: dzw0065@auburn.edu.
Chemosphere ; 353: 141562, 2024 Apr.
Article in En | MEDLINE | ID: mdl-38417493
ABSTRACT
The UV/sulfite-based advanced reduction process (ARP) emerges as an effective strategy to combat per- and polyfluoroalkyl substances (PFAS) pollution in water. Yet, the UV/sulfite-ARP typically operates at highly alkaline conditions (e.g., pH > 9 or even higher) since the generated reductive radicals for PFAS degradation can be quickly sequestered by protons (H+). To overcome the associated challenges, we prototyped a biochar-surfactant-system (BSS) to synergistically enhance PFAS sorption and degradation by UV/sulfite-ARP. The degradation and defluorination efficiencies of perfluorooctanoic acid (PFOA) depended on solution pH, and concentrations of surfactant (cetyltrimethylammonium bromide; CTAB), sulfite, and biochar. At high pH (8-10), adding biochar and BSS showed no or even small inhibitory effect on PFOA degradation, since the degradation efficiencies were already high enough that cannot be differentiated. However, at acidic and neutral pH (6-7), an evident enhancement of PFOA degradation and defluorination efficiencies occurred. This is due to the synergies between biochar and CTAB that create favorable microenvironments for enhanced PFOA sorption and deeper destruction by prolonging the longevity of reductive radicals (e.g., SO3•-), which is less affected by ambient pH conditions. The performance of UV/sulfite/BSS was further optimized and used for the degradation of four PFAS. At the optimal experimental condition, the UV/sulfite/BSS system can completely degrade PFOA with >30% defluorination efficiency for up to five continuous cycles (n = 5). Overall, our BSS provides a cost-effective and sustainable technique to effectively degrade PFAS in water under environmentally relevant pH conditions. The BSS-enabled ARP technique can be easily tied into PFAS treatment train technology (e.g., advanced oxidation process) for more efficient and deeper defluorination of various PFAS in water.
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Full text: 1 Collection: 01-internacional Database: MEDLINE Main subject: Water Pollutants, Chemical / Pulmonary Surfactants / Caprylates / Charcoal / Fluorocarbons Language: En Journal: Chemosphere Year: 2024 Document type: Article Affiliation country: United States

Full text: 1 Collection: 01-internacional Database: MEDLINE Main subject: Water Pollutants, Chemical / Pulmonary Surfactants / Caprylates / Charcoal / Fluorocarbons Language: En Journal: Chemosphere Year: 2024 Document type: Article Affiliation country: United States