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      Electrochemical degradation of perfluorinated compounds by Ag coated Ti (Ti/Ag) anode: electrode preparation, characterization and application

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          Abstract

          Perfluorinated compounds (PFCs) are environmentally persistent, bioaccumulative, and globally distributed pollutants, which exhibit potential toxicity to both humans and ecosystems.

          Abstract

          Perfluorinated compounds (PFCs) are environmentally persistent, bioaccumulative, and globally distributed pollutants, which exhibit potential toxicity to both humans and ecosystems. In this study, the electrochemical degradation of PFCs in the effluent of a municipal wastewater treatment plant (MWWTP) was conducted using an Ag coated titanium (Ti/Ag) anode. Results from the Tafel polarization analysis showed that the Ag film was uniformly coated on the surface of a Ti plate, and a higher corrosion potential (−0.3086 V) was obtained when compared with that of the original Ti electrode (−0.9707 V). To optimize the degradation process, response surface methodology (RSM) combined with a Box–Behnken design (BBD) was applied to optimize the factors that could affect the degradation of the PFCs. Results indicated that the maximum removal efficiencies of short chain PFCs (C–F < 7), long chain PFCs (C–F ≥ 7), and chemical oxygen demand (COD) were about 70.8%, 91.5%, and 92.0%, respectively, under optimum conditions, at which the current density was 20.0 mA cm −2, the pH was 6, the electrode distance was 1.6 cm within 100 min of electrolysis time. Moreover, triplicate tests were carried out and demonstrated that the relative standard deviation (RSD%) was lower than 5.0% which meant that the experimental design and the optimized factors were significant. The degradation kinetic analysis suggested that the degradation of COD and PFCs was in agreement with the pseudo-first-order kinetic reaction, and the COD degradation occurred prior to the long-chain PFCs and short-chain PFCs degradation.

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          Behaviour and fate of perfluoroalkyl and polyfluoroalkyl substances (PFASs) in drinking water treatment: a review.

          This article reviews perfluoroalkyl and polyfluoroalkyl substance (PFAS) characteristics, their occurrence in surface water, and their fate in drinking water treatment processes. PFASs have been detected globally in the aquatic environment including drinking water at trace concentrations and due, in part, to their persistence in human tissue some are being investigated for regulation. They are aliphatic compounds containing saturated carbon-fluorine bonds and are resistant to chemical, physical, and biological degradation. Functional groups, carbon chain length, and hydrophilicity/hydrophobicity are some of the important structural properties of PFASs that affect their fate during drinking water treatment. Full-scale drinking water treatment plant occurrence data indicate that PFASs, if present in raw water, are not substantially removed by most drinking water treatment processes including coagulation, flocculation, sedimentation, filtration, biofiltration, oxidation (chlorination, ozonation, AOPs), UV irradiation, and low pressure membranes. Early observations suggest that activated carbon adsorption, ion exchange, and high pressure membrane filtration may be effective in controlling these contaminants. However, branched isomers and the increasingly used shorter chain PFAS replacement products may be problematic as it pertains to the accurate assessment of PFAS behaviour through drinking water treatment processes since only limited information is available for these PFASs.
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            Advanced Oxidation/Reduction Processes treatment for aqueous perfluorooctanoate (PFOA) and perfluorooctanesulfonate (PFOS) – A review of recent advances

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              Perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) in surface waters, sediments, soils and wastewater - A review on concentrations and distribution coefficients.

              The sorption of perfluorinated compounds (PFCs) to soils and sediments determines their fate and distribution in the environment, but there is little consensus regarding distribution coefficients that should be used for assessing the environmental fate of these compounds. Here we reviewed sorption coefficients for PFCs derived from laboratory experiments and compared these values with the gross distribution between the concentrations of PFCs in surface waters and sediments or between wastewater and sewage sludge. Sorption experiments with perfluorooctanesulfonic acid (PFOS) and perfluorooctanoic acid (PFOA) suggest that their sorption can be described reasonably well as a partitioning-like process with an average log K(oc) of approximately 2.8 for PFOA and 3.0 for PFOS. However, median concentrations in sediments (PFOA, 0.27 ng g(-1); PFOS, 0.54 ng g(-1)) or sewage sludge (PFOA, 37 ng g(-1); PFOS, 69 ng g(-1)) in relation to median concentrations in surface water (PFOA, 3ngl(-1); PFOS, 3ngl(-1)) or wastewater treatment effluent (PFOA, 24 ng l(-1); PFOS, 11 ng l(-1)), suggest that effective log K(oc) distribution coefficients for the field situation may be close to 3.7 for PFOA and 4.2 for PFOS. Applying lab-based log K(oc) distribution coefficients can therefore result in a serious overestimation of PFC concentrations in water and in turn to an underestimation of the residence time of PFOA and PFOS in contaminated soils. Irrespective of the dissipation kinetics, the majority of PFOA and PFOS from contaminated soils will be transported to groundwater and surface water bodies. Copyright © 2013 Elsevier Ltd. All rights reserved.
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                Author and article information

                Contributors
                (View ORCID Profile)
                Journal
                ESWRAR
                Environmental Science: Water Research & Technology
                Environ. Sci.: Water Res. Technol.
                Royal Society of Chemistry (RSC)
                2053-1400
                2053-1419
                February 11 2021
                2021
                : 7
                : 2
                : 455-467
                Affiliations
                [1 ]School of Chemical & Environmental Engineering
                [2 ]China University of Mining & Technology (Beijing)
                [3 ]Beijing 100083
                [4 ]China
                [5 ]Environmental Protection Research Institute of Light Industry
                [6 ]College of Chemistry and Environmental Engineering
                [7 ]Shenzhen University
                [8 ]Shenzhen 518060
                Article
                10.1039/D0EW00785D
                a71427f4-7ade-4ec5-8124-ddc4f8861e1e
                © 2021

                http://rsc.li/journals-terms-of-use

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