Kinetics and Mechanism of Ultrasonic Defluorination of Fluorotelomer SulfonatesClick to copy article linkArticle link copied!
- William P. FaganWilliam P. FaganDepartment of Civil, Environmental, and Geodetic Engineering, The Ohio State University, Columbus, Ohio 43210, United StatesMore by William P. Fagan
- Shannon R. ThayerShannon R. ThayerDepartment of Civil, Environmental, and Geodetic Engineering, The Ohio State University, Columbus, Ohio 43210, United StatesMore by Shannon R. Thayer
- Linda K. Weavers*Linda K. Weavers*Phone: (614) 292-4061. Fax: (614) 292-3780. Email: [email protected]Department of Civil, Environmental, and Geodetic Engineering, The Ohio State University, Columbus, Ohio 43210, United StatesMore by Linda K. Weavers
Abstract

Ultrasound degrades “legacy” per- and polyfluoroalkyl substances (PFAS) via thermolysis at the interface of cavitation bubbles. However, compared to “legacy” PFAS, polyfluoroalkyl substances have a lesser affinity to the interface and may react with •OH. To understand the effect of size on degradation kinetics and mechanism of polyfluoroalkyl substances, this work compared ultrasonic treatment (f = 354 kHz) of n:2 fluorotelomer sulfonates (FTSAs) of varying chain lengths (n = 4, 6, 8). Of the congeners tested, 4:2 fluorotelomer sulfonate (FtS) degraded the fastest in individual solutions and in mixtures. Sonolytic rate constants correlated to diffusion coefficients of FTSAs, indicating that diffuse short-chain FTSAs outcompete long-chain FTSAs to adsorb and react at the bubble interface. Interestingly, 4:2 and 8:2 FtS had different evolutions of fluoride-to-sulfate ratios, [F–]/[SO42–], over time. Initially, [F–]/[SO42–]4:2 FtS and [F–]/[SO42–]8:2 FtS were respectively higher and lower than theoretical ratios. This difference was attributed to the lower maximum surface excess of 8:2 FtS, hindering its ability to pack and, consequently, defluorinate at the interface. In the presence of an •OH scavenger, FTSAs had similar %F– release compared to no scavenger, whereas %SO42– release was drastically diminished. Therefore, thermolysis is the primary degradation pathway of FTSAs; •OH supplements SO42– formation. These results indicate that ultrasound directly cleaves C–F bonds within the fluoroalkyl chain. This work shows that ultrasound efficiently degrades FTSAs of various sizes and may potentially treat other classes of polyfluoroalkyl substances.
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This article is cited by 5 publications.
- Emily O’Rourke, Sara Losada, Jonathan L. Barber, Graham Scholey, Isobel Bain, M. Glória Pereira, Frank Hailer, Elizabeth A. Chadwick. Persistence of PFOA Pollution at a PTFE Production Site and Occurrence of Replacement PFASs in English Freshwaters Revealed by Sentinel Species, the Eurasian Otter (Lutra lutra). Environmental Science & Technology 2024, 58
(23)
, 10195-10206. https://doi.org/10.1021/acs.est.3c09405
- Xuexiang He, Danni Cui, Natalia Quinete, Kevin E O’Shea. Ultrasound induced mineralization of legacy and emerging per- and polyfluoroalkyl substances (PFAS). Chemical Engineering Journal 2025, 516 , 164019. https://doi.org/10.1016/j.cej.2025.164019
- Haleigh A. Fernandez, Linda K. Weavers. The impact of inorganic salts on the ultrasonic degradation of contaminants: A review. Ultrasonics Sonochemistry 2024, 111 , 107076. https://doi.org/10.1016/j.ultsonch.2024.107076
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