Electrochemical oxidation of PFOA and PFOS in concentrated waste streams
The electrochemical oxidation (EO) of environmentally persistent perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) with a Magnéli phase Ti4O7 electrode was investigated in this study. After 3 hours (hr) of electrolysis, 96.0 percent of PFOA (10 milligrams per liter [mg/L] in 100...
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Veröffentlicht in: | Remediation (New York, N.Y.) N.Y.), 2018-03, Vol.28 (2), p.127-134 |
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description | The electrochemical oxidation (EO) of environmentally persistent perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) with a Magnéli phase Ti4O7 electrode was investigated in this study. After 3 hours (hr) of electrolysis, 96.0 percent of PFOA (10 milligrams per liter [mg/L] in 100 milliliters [mL] 100 millimolar [mM] Na2SO4 solution) was removed following pseudo first‐order kinetics (k = 0.0226 per minute [min]) with the degradation half‐life of 30.7 min. Under the same treatment conditions, PFOS (10 mg/L in 100 mL 100 mM Na2SO4 solution) removal reached 98.9 percent with a pseudo first‐order degradation rate constant of 0.0491/min and the half‐life of 14.1 min. Although, the degradation of PFOA was slower than PFOS, when subjected to EO treatment in separate solutions, PFOA appeared to degrade faster than PFOS when both are present in the same solution, indicating possible competition between PFOA and PFOS during Ti4O7 anode‐based EO treatment with PFOA having the competitive advantage. Moreover, the EO treatment was applied to degrade highly concentrated PFOA (100.5 mg/L) and PFOS (68.6 mg/L) in ion‐exchange resin regenerant (still bottom) with high organic carbon content (15,800 mg/L). After 17‐hr electrolysis, the total removal of PFOA and PFOS was 77.2 and 96.5 percent, respectively, and the fluoride concentration increased from 0.84 mg/L to 836 mg/L. Also, the dark brown color of the original solution gradually faded during EO treatment. In another test using still bottom samples with lower total organic carbon (9,880 mg/L), the PFOA (15.5 mg/L) and PFOS (25.5 mg/L) concentrations were reduced to levels below the limits of quantification after 16‐hr treatment. In addition, the performance of EO treatment using different batch reactor setups was compared in this study, including one‐sided (one anode:one cathode) and two‐sided (one anode:two cathodes) setups. The two‐sided reactor configuration significantly enhanced the degradation efficiency, likely due to the larger anode area available for reactions. |
doi_str_mv | 10.1002/rem.21554 |
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After 3 hours (hr) of electrolysis, 96.0 percent of PFOA (10 milligrams per liter [mg/L] in 100 milliliters [mL] 100 millimolar [mM] Na2SO4 solution) was removed following pseudo first‐order kinetics (k = 0.0226 per minute [min]) with the degradation half‐life of 30.7 min. Under the same treatment conditions, PFOS (10 mg/L in 100 mL 100 mM Na2SO4 solution) removal reached 98.9 percent with a pseudo first‐order degradation rate constant of 0.0491/min and the half‐life of 14.1 min. Although, the degradation of PFOA was slower than PFOS, when subjected to EO treatment in separate solutions, PFOA appeared to degrade faster than PFOS when both are present in the same solution, indicating possible competition between PFOA and PFOS during Ti4O7 anode‐based EO treatment with PFOA having the competitive advantage. Moreover, the EO treatment was applied to degrade highly concentrated PFOA (100.5 mg/L) and PFOS (68.6 mg/L) in ion‐exchange resin regenerant (still bottom) with high organic carbon content (15,800 mg/L). After 17‐hr electrolysis, the total removal of PFOA and PFOS was 77.2 and 96.5 percent, respectively, and the fluoride concentration increased from 0.84 mg/L to 836 mg/L. Also, the dark brown color of the original solution gradually faded during EO treatment. In another test using still bottom samples with lower total organic carbon (9,880 mg/L), the PFOA (15.5 mg/L) and PFOS (25.5 mg/L) concentrations were reduced to levels below the limits of quantification after 16‐hr treatment. In addition, the performance of EO treatment using different batch reactor setups was compared in this study, including one‐sided (one anode:one cathode) and two‐sided (one anode:two cathodes) setups. The two‐sided reactor configuration significantly enhanced the degradation efficiency, likely due to the larger anode area available for reactions.</description><identifier>ISSN: 1051-5658</identifier><identifier>EISSN: 1520-6831</identifier><identifier>DOI: 10.1002/rem.21554</identifier><language>eng</language><publisher>New York: Wiley Subscription Services, Inc</publisher><subject>Anodes ; Batch reactors ; Carbon content ; Cathodes ; Competitive advantage ; Degradation ; Electrochemical oxidation ; Electrochemistry ; Electrolysis ; Fluorides ; Kinetics ; Organic carbon ; Oxidation ; Perfluorooctane sulfonic acid ; Perfluorooctanoic acid ; Reaction kinetics ; Reactors ; Sodium sulfate ; Total organic carbon ; Waste management ; Waste streams</subject><ispartof>Remediation (New York, N.Y.), 2018-03, Vol.28 (2), p.127-134</ispartof><rights>2018 Wiley Periodicals, Inc.</rights><rights>Copyright © 2018 Wiley Periodicals, Inc., a Wiley Company</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c3634-6c29d43a8bda1dfba14f3e4deea37b1493f94f6deb8ab083ad6f90f15694f973</citedby><cites>FETCH-LOGICAL-c3634-6c29d43a8bda1dfba14f3e4deea37b1493f94f6deb8ab083ad6f90f15694f973</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://onlinelibrary.wiley.com/doi/pdf/10.1002%2Frem.21554$$EPDF$$P50$$Gwiley$$H</linktopdf><linktohtml>$$Uhttps://onlinelibrary.wiley.com/doi/full/10.1002%2Frem.21554$$EHTML$$P50$$Gwiley$$H</linktohtml><link.rule.ids>314,780,784,1417,27924,27925,45574,45575</link.rule.ids></links><search><creatorcontrib>Liang, Shangtao</creatorcontrib><creatorcontrib>Pierce, Randall "David"</creatorcontrib><creatorcontrib>Lin, Hui</creatorcontrib><creatorcontrib>Chiang, Sheau‐Yun (Dora)</creatorcontrib><creatorcontrib>Huang, Qingguo "Jack"</creatorcontrib><title>Electrochemical oxidation of PFOA and PFOS in concentrated waste streams</title><title>Remediation (New York, N.Y.)</title><description>The electrochemical oxidation (EO) of environmentally persistent perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) with a Magnéli phase Ti4O7 electrode was investigated in this study. After 3 hours (hr) of electrolysis, 96.0 percent of PFOA (10 milligrams per liter [mg/L] in 100 milliliters [mL] 100 millimolar [mM] Na2SO4 solution) was removed following pseudo first‐order kinetics (k = 0.0226 per minute [min]) with the degradation half‐life of 30.7 min. Under the same treatment conditions, PFOS (10 mg/L in 100 mL 100 mM Na2SO4 solution) removal reached 98.9 percent with a pseudo first‐order degradation rate constant of 0.0491/min and the half‐life of 14.1 min. Although, the degradation of PFOA was slower than PFOS, when subjected to EO treatment in separate solutions, PFOA appeared to degrade faster than PFOS when both are present in the same solution, indicating possible competition between PFOA and PFOS during Ti4O7 anode‐based EO treatment with PFOA having the competitive advantage. Moreover, the EO treatment was applied to degrade highly concentrated PFOA (100.5 mg/L) and PFOS (68.6 mg/L) in ion‐exchange resin regenerant (still bottom) with high organic carbon content (15,800 mg/L). After 17‐hr electrolysis, the total removal of PFOA and PFOS was 77.2 and 96.5 percent, respectively, and the fluoride concentration increased from 0.84 mg/L to 836 mg/L. Also, the dark brown color of the original solution gradually faded during EO treatment. In another test using still bottom samples with lower total organic carbon (9,880 mg/L), the PFOA (15.5 mg/L) and PFOS (25.5 mg/L) concentrations were reduced to levels below the limits of quantification after 16‐hr treatment. In addition, the performance of EO treatment using different batch reactor setups was compared in this study, including one‐sided (one anode:one cathode) and two‐sided (one anode:two cathodes) setups. The two‐sided reactor configuration significantly enhanced the degradation efficiency, likely due to the larger anode area available for reactions.</description><subject>Anodes</subject><subject>Batch reactors</subject><subject>Carbon content</subject><subject>Cathodes</subject><subject>Competitive advantage</subject><subject>Degradation</subject><subject>Electrochemical oxidation</subject><subject>Electrochemistry</subject><subject>Electrolysis</subject><subject>Fluorides</subject><subject>Kinetics</subject><subject>Organic carbon</subject><subject>Oxidation</subject><subject>Perfluorooctane sulfonic acid</subject><subject>Perfluorooctanoic acid</subject><subject>Reaction kinetics</subject><subject>Reactors</subject><subject>Sodium sulfate</subject><subject>Total organic carbon</subject><subject>Waste management</subject><subject>Waste streams</subject><issn>1051-5658</issn><issn>1520-6831</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2018</creationdate><recordtype>article</recordtype><recordid>eNp1kE9LAzEQxYMoWKsHv0HAk4etyeZPd4-ltFaoVLT3kE0muGV3U5Mttd_e1PUqc5jH8Jv34CF0T8mEEpI_BWgnORWCX6ARFTnJZMHoZdJE0ExIUVyjmxh3hNA0bIRWiwZMH7z5hLY2usH-u7a6r32HvcNvy80M686exQeuO2x8Z6Drg-7B4qOOPeDYB9BtvEVXTjcR7v72GG2Xi-18la03zy_z2TozTDKeSZOXljNdVFZT6ypNuWPALYBm04rykrmSO2mhKnRFCqatdCVxVMh0LqdsjB4G233wXweIvdr5Q-hSosoJY6IQySJRjwNlgo8xgFP7ULc6nBQl6tyTSj2p354S-zSwx7qB0_-gel-8Dh8_vyxpVw</recordid><startdate>20180301</startdate><enddate>20180301</enddate><creator>Liang, Shangtao</creator><creator>Pierce, Randall "David"</creator><creator>Lin, Hui</creator><creator>Chiang, Sheau‐Yun (Dora)</creator><creator>Huang, Qingguo "Jack"</creator><general>Wiley Subscription Services, Inc</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7QF</scope><scope>7QL</scope><scope>7QQ</scope><scope>7SC</scope><scope>7SE</scope><scope>7SP</scope><scope>7SR</scope><scope>7ST</scope><scope>7T7</scope><scope>7TA</scope><scope>7TB</scope><scope>7TV</scope><scope>7U5</scope><scope>7U9</scope><scope>8BQ</scope><scope>8FD</scope><scope>C1K</scope><scope>F28</scope><scope>FR3</scope><scope>H8D</scope><scope>H8G</scope><scope>H94</scope><scope>JG9</scope><scope>JQ2</scope><scope>KR7</scope><scope>L7M</scope><scope>L~C</scope><scope>L~D</scope><scope>M7N</scope><scope>P64</scope><scope>SOI</scope></search><sort><creationdate>20180301</creationdate><title>Electrochemical oxidation of PFOA and PFOS in concentrated waste streams</title><author>Liang, Shangtao ; Pierce, Randall "David" ; Lin, Hui ; Chiang, Sheau‐Yun (Dora) ; Huang, Qingguo "Jack"</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c3634-6c29d43a8bda1dfba14f3e4deea37b1493f94f6deb8ab083ad6f90f15694f973</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2018</creationdate><topic>Anodes</topic><topic>Batch reactors</topic><topic>Carbon content</topic><topic>Cathodes</topic><topic>Competitive advantage</topic><topic>Degradation</topic><topic>Electrochemical oxidation</topic><topic>Electrochemistry</topic><topic>Electrolysis</topic><topic>Fluorides</topic><topic>Kinetics</topic><topic>Organic carbon</topic><topic>Oxidation</topic><topic>Perfluorooctane sulfonic acid</topic><topic>Perfluorooctanoic acid</topic><topic>Reaction kinetics</topic><topic>Reactors</topic><topic>Sodium sulfate</topic><topic>Total organic carbon</topic><topic>Waste management</topic><topic>Waste streams</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Liang, Shangtao</creatorcontrib><creatorcontrib>Pierce, Randall "David"</creatorcontrib><creatorcontrib>Lin, Hui</creatorcontrib><creatorcontrib>Chiang, Sheau‐Yun (Dora)</creatorcontrib><creatorcontrib>Huang, Qingguo "Jack"</creatorcontrib><collection>CrossRef</collection><collection>Aluminium Industry Abstracts</collection><collection>Bacteriology Abstracts (Microbiology B)</collection><collection>Ceramic Abstracts</collection><collection>Computer and Information Systems Abstracts</collection><collection>Corrosion Abstracts</collection><collection>Electronics & Communications Abstracts</collection><collection>Engineered Materials Abstracts</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Materials Business File</collection><collection>Mechanical & Transportation Engineering Abstracts</collection><collection>Pollution Abstracts</collection><collection>Solid State and Superconductivity Abstracts</collection><collection>Virology and AIDS Abstracts</collection><collection>METADEX</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ANTE: Abstracts in New Technology & Engineering</collection><collection>Engineering Research Database</collection><collection>Aerospace Database</collection><collection>Copper Technical Reference Library</collection><collection>AIDS and Cancer Research Abstracts</collection><collection>Materials Research Database</collection><collection>ProQuest Computer Science Collection</collection><collection>Civil Engineering Abstracts</collection><collection>Advanced Technologies Database with Aerospace</collection><collection>Computer and Information Systems Abstracts Academic</collection><collection>Computer and Information Systems Abstracts Professional</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Environment Abstracts</collection><jtitle>Remediation (New York, N.Y.)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Liang, Shangtao</au><au>Pierce, Randall "David"</au><au>Lin, Hui</au><au>Chiang, Sheau‐Yun (Dora)</au><au>Huang, Qingguo "Jack"</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Electrochemical oxidation of PFOA and PFOS in concentrated waste streams</atitle><jtitle>Remediation (New York, N.Y.)</jtitle><date>2018-03-01</date><risdate>2018</risdate><volume>28</volume><issue>2</issue><spage>127</spage><epage>134</epage><pages>127-134</pages><issn>1051-5658</issn><eissn>1520-6831</eissn><abstract>The electrochemical oxidation (EO) of environmentally persistent perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) with a Magnéli phase Ti4O7 electrode was investigated in this study. After 3 hours (hr) of electrolysis, 96.0 percent of PFOA (10 milligrams per liter [mg/L] in 100 milliliters [mL] 100 millimolar [mM] Na2SO4 solution) was removed following pseudo first‐order kinetics (k = 0.0226 per minute [min]) with the degradation half‐life of 30.7 min. Under the same treatment conditions, PFOS (10 mg/L in 100 mL 100 mM Na2SO4 solution) removal reached 98.9 percent with a pseudo first‐order degradation rate constant of 0.0491/min and the half‐life of 14.1 min. Although, the degradation of PFOA was slower than PFOS, when subjected to EO treatment in separate solutions, PFOA appeared to degrade faster than PFOS when both are present in the same solution, indicating possible competition between PFOA and PFOS during Ti4O7 anode‐based EO treatment with PFOA having the competitive advantage. Moreover, the EO treatment was applied to degrade highly concentrated PFOA (100.5 mg/L) and PFOS (68.6 mg/L) in ion‐exchange resin regenerant (still bottom) with high organic carbon content (15,800 mg/L). After 17‐hr electrolysis, the total removal of PFOA and PFOS was 77.2 and 96.5 percent, respectively, and the fluoride concentration increased from 0.84 mg/L to 836 mg/L. Also, the dark brown color of the original solution gradually faded during EO treatment. In another test using still bottom samples with lower total organic carbon (9,880 mg/L), the PFOA (15.5 mg/L) and PFOS (25.5 mg/L) concentrations were reduced to levels below the limits of quantification after 16‐hr treatment. In addition, the performance of EO treatment using different batch reactor setups was compared in this study, including one‐sided (one anode:one cathode) and two‐sided (one anode:two cathodes) setups. The two‐sided reactor configuration significantly enhanced the degradation efficiency, likely due to the larger anode area available for reactions.</abstract><cop>New York</cop><pub>Wiley Subscription Services, Inc</pub><doi>10.1002/rem.21554</doi><tpages>8</tpages></addata></record> |
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subjects | Anodes Batch reactors Carbon content Cathodes Competitive advantage Degradation Electrochemical oxidation Electrochemistry Electrolysis Fluorides Kinetics Organic carbon Oxidation Perfluorooctane sulfonic acid Perfluorooctanoic acid Reaction kinetics Reactors Sodium sulfate Total organic carbon Waste management Waste streams |
title | Electrochemical oxidation of PFOA and PFOS in concentrated waste streams |
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