Aerobic Biotransformation of 14C-Labeled 8-2 Telomer B Alcohol by Activated Sludge from a Domestic Sewage Treatment Plant

This study investigated the biodegradation potential of 3-14C,1H,1H,2H,2H-perfluorodecanol [CF3(CF2)6 14CF2CH2CH2OH, 14C-labeled 8-2 telomer B alcohol or 14C-labeled 8-2 TBA] by diluted activated sludge from a domestic wastewater treatment plant under aerobic conditions. After sample extraction with...

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Veröffentlicht in:Environmental science & technology 2005-01, Vol.39 (2), p.531-538
Hauptverfasser: Wang, Ning, Szostek, Bogdan, Folsom, Patrick W, Sulecki, Lisa M, Capka, Vladimir, Buck, Robert C, Berti, William R, Gannon, John T
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container_end_page 538
container_issue 2
container_start_page 531
container_title Environmental science & technology
container_volume 39
creator Wang, Ning
Szostek, Bogdan
Folsom, Patrick W
Sulecki, Lisa M
Capka, Vladimir
Buck, Robert C
Berti, William R
Gannon, John T
description This study investigated the biodegradation potential of 3-14C,1H,1H,2H,2H-perfluorodecanol [CF3(CF2)6 14CF2CH2CH2OH, 14C-labeled 8-2 telomer B alcohol or 14C-labeled 8-2 TBA] by diluted activated sludge from a domestic wastewater treatment plant under aerobic conditions. After sample extraction with acetonitrile, biotransformation products were separated and quantified by LC/ARC (on-line liquid chromatography/accurate radioisotope counting) with a limit of quantification about 0.5% of the 14C counts applied to the test systems. Identification of biotransformation products was performed by quadrupole time-of-flight mass spectrometry. Three transformation products have been identified:  CF3(CF2)6 14CF2CH2COOH (8-2 saturated acid); CF3(CF2)6 14CFCHCOOH (8-2 unsaturated acid); and CF3(CF2)6 14COOH (perfluorooctanoic acid, PFOA), representing 27, 6.0, and 2.1% of the initial 14C mass (14C counts applied) after 28 days, respectively. A transformation product, not yet reported in the literature, has also been observed and tentatively identified as CF3(CF2)6 14CH2CH2COOH (2H,2H,3H,3H-perfluorodecanoic acid); it accounted for 2.3% of the mass balance after 28 days. The 2H,2H,3H,3H-perfluorodecanoic acid is likely a substrate for β-oxidation, which represents one of the possible pathways for 8-2 telomer B alcohol degradation. The 8-2 saturated acid and 8-2 unsaturated acid cannot be directly used as substrates for β-oxidation due to the proton deficiency in their β-carbon (C3 carbon) and their further catabolism may be catalyzed by some other still unknown mechanisms. The 2H,2H,3H,3H-perfluorodecanoic acid may originate either from the major transformation product CF3(CF2)6 14CF2CH2COOH or from other unidentified transformation products via multiple steps. Approximately 57% of the starting material remained unchanged after 28 days, likely due to its strong adsorption to the PTFE (poly(tetrafluoroethylene)) septa of the test vessels. No CF3(CF2)6 14CF2COOH (perfluorononanoic acid) was observed, indicating that α-oxidation of CF3(CF2)6 14CF2CH2COOH did not occur under the study conditions. Several 14C-labeled transformation products that have not yet been identified (each less than 1% of the mass balance) were also observed and together accounted for 7% of the total 14C mass balance after 28 days. It is not clear whether these unidentified transformation products were resulting from further metabolism of 8-2 saturated acid or 8-2 unsaturated acid. The results suggest
doi_str_mv 10.1021/es049466y
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After sample extraction with acetonitrile, biotransformation products were separated and quantified by LC/ARC (on-line liquid chromatography/accurate radioisotope counting) with a limit of quantification about 0.5% of the 14C counts applied to the test systems. Identification of biotransformation products was performed by quadrupole time-of-flight mass spectrometry. Three transformation products have been identified:  CF3(CF2)6 14CF2CH2COOH (8-2 saturated acid); CF3(CF2)6 14CFCHCOOH (8-2 unsaturated acid); and CF3(CF2)6 14COOH (perfluorooctanoic acid, PFOA), representing 27, 6.0, and 2.1% of the initial 14C mass (14C counts applied) after 28 days, respectively. A transformation product, not yet reported in the literature, has also been observed and tentatively identified as CF3(CF2)6 14CH2CH2COOH (2H,2H,3H,3H-perfluorodecanoic acid); it accounted for 2.3% of the mass balance after 28 days. The 2H,2H,3H,3H-perfluorodecanoic acid is likely a substrate for β-oxidation, which represents one of the possible pathways for 8-2 telomer B alcohol degradation. The 8-2 saturated acid and 8-2 unsaturated acid cannot be directly used as substrates for β-oxidation due to the proton deficiency in their β-carbon (C3 carbon) and their further catabolism may be catalyzed by some other still unknown mechanisms. The 2H,2H,3H,3H-perfluorodecanoic acid may originate either from the major transformation product CF3(CF2)6 14CF2CH2COOH or from other unidentified transformation products via multiple steps. Approximately 57% of the starting material remained unchanged after 28 days, likely due to its strong adsorption to the PTFE (poly(tetrafluoroethylene)) septa of the test vessels. No CF3(CF2)6 14CF2COOH (perfluorononanoic acid) was observed, indicating that α-oxidation of CF3(CF2)6 14CF2CH2COOH did not occur under the study conditions. Several 14C-labeled transformation products that have not yet been identified (each less than 1% of the mass balance) were also observed and together accounted for 7% of the total 14C mass balance after 28 days. It is not clear whether these unidentified transformation products were resulting from further metabolism of 8-2 saturated acid or 8-2 unsaturated acid. The results suggest that perfluorinated acid metabolites such as perfluorooctanoic acid account for only a very small portion of the transformation products observed. Also, the observed volatility and bioavailability of 14C-labeled 8-2 TBA for microbial degradation was markedly decreased as a result of the presence of a strongly adsorbing matrix such as PTFE in the experimental systems. It is apparent that the biological fate of 8-2 telomer B alcohol is determined by multiple degradation pathways, with neither β-oxidation nor any other enzyme-catalyzed reactions as a single dominant (principal) mechanism under the study conditions.</description><identifier>ISSN: 0013-936X</identifier><identifier>EISSN: 1520-5851</identifier><identifier>DOI: 10.1021/es049466y</identifier><identifier>PMID: 15707053</identifier><identifier>CODEN: ESTHAG</identifier><language>eng</language><publisher>Washington, DC: American Chemical Society</publisher><subject>Acids ; Adsorption ; Alcohol ; Applied sciences ; Bacteria, Aerobic ; Biological and medical sciences ; Biological treatment of waters ; Biotechnology ; Biotransformation ; Carbon Radioisotopes - analysis ; Catalysis ; Environment and pollution ; Exact sciences and technology ; Fluorocarbons - metabolism ; Fundamental and applied biological sciences. Psychology ; Industrial applications and implications. Economical aspects ; Labeling ; Other wastewaters ; Oxidation ; Oxidation-Reduction ; Perfluoroalkyl &amp; polyfluoroalkyl substances ; Pollution ; Sewage - chemistry ; Sewage treatment plants ; Sludge ; Studies ; Waste Disposal, Fluid ; Wastewaters ; Water treatment and pollution</subject><ispartof>Environmental science &amp; technology, 2005-01, Vol.39 (2), p.531-538</ispartof><rights>Copyright © 2005 American Chemical Society</rights><rights>2005 INIST-CNRS</rights><rights>Copyright American Chemical Society Jan 15, 2005</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://pubs.acs.org/doi/pdf/10.1021/es049466y$$EPDF$$P50$$Gacs$$H</linktopdf><linktohtml>$$Uhttps://pubs.acs.org/doi/10.1021/es049466y$$EHTML$$P50$$Gacs$$H</linktohtml><link.rule.ids>314,780,784,27074,27922,27923,56736,56786</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&amp;idt=16444278$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/15707053$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Wang, Ning</creatorcontrib><creatorcontrib>Szostek, Bogdan</creatorcontrib><creatorcontrib>Folsom, Patrick W</creatorcontrib><creatorcontrib>Sulecki, Lisa M</creatorcontrib><creatorcontrib>Capka, Vladimir</creatorcontrib><creatorcontrib>Buck, Robert C</creatorcontrib><creatorcontrib>Berti, William R</creatorcontrib><creatorcontrib>Gannon, John T</creatorcontrib><title>Aerobic Biotransformation of 14C-Labeled 8-2 Telomer B Alcohol by Activated Sludge from a Domestic Sewage Treatment Plant</title><title>Environmental science &amp; technology</title><addtitle>Environ. Sci. Technol</addtitle><description>This study investigated the biodegradation potential of 3-14C,1H,1H,2H,2H-perfluorodecanol [CF3(CF2)6 14CF2CH2CH2OH, 14C-labeled 8-2 telomer B alcohol or 14C-labeled 8-2 TBA] by diluted activated sludge from a domestic wastewater treatment plant under aerobic conditions. After sample extraction with acetonitrile, biotransformation products were separated and quantified by LC/ARC (on-line liquid chromatography/accurate radioisotope counting) with a limit of quantification about 0.5% of the 14C counts applied to the test systems. Identification of biotransformation products was performed by quadrupole time-of-flight mass spectrometry. Three transformation products have been identified:  CF3(CF2)6 14CF2CH2COOH (8-2 saturated acid); CF3(CF2)6 14CFCHCOOH (8-2 unsaturated acid); and CF3(CF2)6 14COOH (perfluorooctanoic acid, PFOA), representing 27, 6.0, and 2.1% of the initial 14C mass (14C counts applied) after 28 days, respectively. A transformation product, not yet reported in the literature, has also been observed and tentatively identified as CF3(CF2)6 14CH2CH2COOH (2H,2H,3H,3H-perfluorodecanoic acid); it accounted for 2.3% of the mass balance after 28 days. The 2H,2H,3H,3H-perfluorodecanoic acid is likely a substrate for β-oxidation, which represents one of the possible pathways for 8-2 telomer B alcohol degradation. The 8-2 saturated acid and 8-2 unsaturated acid cannot be directly used as substrates for β-oxidation due to the proton deficiency in their β-carbon (C3 carbon) and their further catabolism may be catalyzed by some other still unknown mechanisms. The 2H,2H,3H,3H-perfluorodecanoic acid may originate either from the major transformation product CF3(CF2)6 14CF2CH2COOH or from other unidentified transformation products via multiple steps. Approximately 57% of the starting material remained unchanged after 28 days, likely due to its strong adsorption to the PTFE (poly(tetrafluoroethylene)) septa of the test vessels. No CF3(CF2)6 14CF2COOH (perfluorononanoic acid) was observed, indicating that α-oxidation of CF3(CF2)6 14CF2CH2COOH did not occur under the study conditions. Several 14C-labeled transformation products that have not yet been identified (each less than 1% of the mass balance) were also observed and together accounted for 7% of the total 14C mass balance after 28 days. It is not clear whether these unidentified transformation products were resulting from further metabolism of 8-2 saturated acid or 8-2 unsaturated acid. The results suggest that perfluorinated acid metabolites such as perfluorooctanoic acid account for only a very small portion of the transformation products observed. Also, the observed volatility and bioavailability of 14C-labeled 8-2 TBA for microbial degradation was markedly decreased as a result of the presence of a strongly adsorbing matrix such as PTFE in the experimental systems. It is apparent that the biological fate of 8-2 telomer B alcohol is determined by multiple degradation pathways, with neither β-oxidation nor any other enzyme-catalyzed reactions as a single dominant (principal) mechanism under the study conditions.</description><subject>Acids</subject><subject>Adsorption</subject><subject>Alcohol</subject><subject>Applied sciences</subject><subject>Bacteria, Aerobic</subject><subject>Biological and medical sciences</subject><subject>Biological treatment of waters</subject><subject>Biotechnology</subject><subject>Biotransformation</subject><subject>Carbon Radioisotopes - analysis</subject><subject>Catalysis</subject><subject>Environment and pollution</subject><subject>Exact sciences and technology</subject><subject>Fluorocarbons - metabolism</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Industrial applications and implications. Economical aspects</subject><subject>Labeling</subject><subject>Other wastewaters</subject><subject>Oxidation</subject><subject>Oxidation-Reduction</subject><subject>Perfluoroalkyl &amp; polyfluoroalkyl substances</subject><subject>Pollution</subject><subject>Sewage - chemistry</subject><subject>Sewage treatment plants</subject><subject>Sludge</subject><subject>Studies</subject><subject>Waste Disposal, Fluid</subject><subject>Wastewaters</subject><subject>Water treatment and pollution</subject><issn>0013-936X</issn><issn>1520-5851</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2005</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNpFkVtv1DAQhS0EotvCA38AWUg8BsbxNY_bLaWglai0y-XNcpIxpCRxsb3A_nsMXbpPI818OjNzDiHPGLxiULPXmEA0Qqn9A7JgsoZKGskekgUA41XD1ZcTcprSDQDUHMxjcsKkBg2SL8h-iTG0Q0fPh5Cjm5MPcXJ5CDMNnjKxqtauxRF7aqqabnEME0Z6TpdjF76FkbZ7uuzy8NPlgmzGXf8VqY9hoo5eFDTlIr3BX660txFdnnDO9Hp0c35CHnk3Jnx6qGfk4-Wb7eqqWn94-261XFeuNjWvOAoBAhrnAXrZGKOwYS2gFj1KaZxXrRQ1sA68ZsIbo700WCtQfePLv_yMvLjTvY3hx65cZG_CLs5lpS1uMG7EP-j5Adq1E_b2Ng6Ti3v736gCvDwALnVu9MWqbkhHTgkham0KV91xQ8r4-37u4nerNNfSbq83VnNz9f7T5wvLjrquS8fDGNi_wdr7YPkfLieO6g</recordid><startdate>20050115</startdate><enddate>20050115</enddate><creator>Wang, Ning</creator><creator>Szostek, Bogdan</creator><creator>Folsom, Patrick W</creator><creator>Sulecki, Lisa M</creator><creator>Capka, Vladimir</creator><creator>Buck, Robert C</creator><creator>Berti, William R</creator><creator>Gannon, John T</creator><general>American Chemical Society</general><scope>BSCLL</scope><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>7QO</scope><scope>7ST</scope><scope>7T7</scope><scope>7U7</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>P64</scope><scope>SOI</scope></search><sort><creationdate>20050115</creationdate><title>Aerobic Biotransformation of 14C-Labeled 8-2 Telomer B Alcohol by Activated Sludge from a Domestic Sewage Treatment Plant</title><author>Wang, Ning ; Szostek, Bogdan ; Folsom, Patrick W ; Sulecki, Lisa M ; Capka, Vladimir ; Buck, Robert C ; Berti, William R ; Gannon, John T</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-a2823-3e440409af00d59886e91b0e74de558af6b54201c0f714f887f58e2606d9f0233</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2005</creationdate><topic>Acids</topic><topic>Adsorption</topic><topic>Alcohol</topic><topic>Applied sciences</topic><topic>Bacteria, Aerobic</topic><topic>Biological and medical sciences</topic><topic>Biological treatment of waters</topic><topic>Biotechnology</topic><topic>Biotransformation</topic><topic>Carbon Radioisotopes - analysis</topic><topic>Catalysis</topic><topic>Environment and pollution</topic><topic>Exact sciences and technology</topic><topic>Fluorocarbons - metabolism</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Industrial applications and implications. Economical aspects</topic><topic>Labeling</topic><topic>Other wastewaters</topic><topic>Oxidation</topic><topic>Oxidation-Reduction</topic><topic>Perfluoroalkyl &amp; polyfluoroalkyl substances</topic><topic>Pollution</topic><topic>Sewage - chemistry</topic><topic>Sewage treatment plants</topic><topic>Sludge</topic><topic>Studies</topic><topic>Waste Disposal, Fluid</topic><topic>Wastewaters</topic><topic>Water treatment and pollution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Wang, Ning</creatorcontrib><creatorcontrib>Szostek, Bogdan</creatorcontrib><creatorcontrib>Folsom, Patrick W</creatorcontrib><creatorcontrib>Sulecki, Lisa M</creatorcontrib><creatorcontrib>Capka, Vladimir</creatorcontrib><creatorcontrib>Buck, Robert C</creatorcontrib><creatorcontrib>Berti, William R</creatorcontrib><creatorcontrib>Gannon, John T</creatorcontrib><collection>Istex</collection><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>Biotechnology Research Abstracts</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Toxicology Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Environment Abstracts</collection><jtitle>Environmental science &amp; technology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Wang, Ning</au><au>Szostek, Bogdan</au><au>Folsom, Patrick W</au><au>Sulecki, Lisa M</au><au>Capka, Vladimir</au><au>Buck, Robert C</au><au>Berti, William R</au><au>Gannon, John T</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Aerobic Biotransformation of 14C-Labeled 8-2 Telomer B Alcohol by Activated Sludge from a Domestic Sewage Treatment Plant</atitle><jtitle>Environmental science &amp; technology</jtitle><addtitle>Environ. Sci. Technol</addtitle><date>2005-01-15</date><risdate>2005</risdate><volume>39</volume><issue>2</issue><spage>531</spage><epage>538</epage><pages>531-538</pages><issn>0013-936X</issn><eissn>1520-5851</eissn><coden>ESTHAG</coden><abstract>This study investigated the biodegradation potential of 3-14C,1H,1H,2H,2H-perfluorodecanol [CF3(CF2)6 14CF2CH2CH2OH, 14C-labeled 8-2 telomer B alcohol or 14C-labeled 8-2 TBA] by diluted activated sludge from a domestic wastewater treatment plant under aerobic conditions. After sample extraction with acetonitrile, biotransformation products were separated and quantified by LC/ARC (on-line liquid chromatography/accurate radioisotope counting) with a limit of quantification about 0.5% of the 14C counts applied to the test systems. Identification of biotransformation products was performed by quadrupole time-of-flight mass spectrometry. Three transformation products have been identified:  CF3(CF2)6 14CF2CH2COOH (8-2 saturated acid); CF3(CF2)6 14CFCHCOOH (8-2 unsaturated acid); and CF3(CF2)6 14COOH (perfluorooctanoic acid, PFOA), representing 27, 6.0, and 2.1% of the initial 14C mass (14C counts applied) after 28 days, respectively. A transformation product, not yet reported in the literature, has also been observed and tentatively identified as CF3(CF2)6 14CH2CH2COOH (2H,2H,3H,3H-perfluorodecanoic acid); it accounted for 2.3% of the mass balance after 28 days. The 2H,2H,3H,3H-perfluorodecanoic acid is likely a substrate for β-oxidation, which represents one of the possible pathways for 8-2 telomer B alcohol degradation. The 8-2 saturated acid and 8-2 unsaturated acid cannot be directly used as substrates for β-oxidation due to the proton deficiency in their β-carbon (C3 carbon) and their further catabolism may be catalyzed by some other still unknown mechanisms. The 2H,2H,3H,3H-perfluorodecanoic acid may originate either from the major transformation product CF3(CF2)6 14CF2CH2COOH or from other unidentified transformation products via multiple steps. Approximately 57% of the starting material remained unchanged after 28 days, likely due to its strong adsorption to the PTFE (poly(tetrafluoroethylene)) septa of the test vessels. No CF3(CF2)6 14CF2COOH (perfluorononanoic acid) was observed, indicating that α-oxidation of CF3(CF2)6 14CF2CH2COOH did not occur under the study conditions. Several 14C-labeled transformation products that have not yet been identified (each less than 1% of the mass balance) were also observed and together accounted for 7% of the total 14C mass balance after 28 days. It is not clear whether these unidentified transformation products were resulting from further metabolism of 8-2 saturated acid or 8-2 unsaturated acid. The results suggest that perfluorinated acid metabolites such as perfluorooctanoic acid account for only a very small portion of the transformation products observed. Also, the observed volatility and bioavailability of 14C-labeled 8-2 TBA for microbial degradation was markedly decreased as a result of the presence of a strongly adsorbing matrix such as PTFE in the experimental systems. It is apparent that the biological fate of 8-2 telomer B alcohol is determined by multiple degradation pathways, with neither β-oxidation nor any other enzyme-catalyzed reactions as a single dominant (principal) mechanism under the study conditions.</abstract><cop>Washington, DC</cop><pub>American Chemical Society</pub><pmid>15707053</pmid><doi>10.1021/es049466y</doi><tpages>8</tpages></addata></record>
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source MEDLINE; ACS Publications
subjects Acids
Adsorption
Alcohol
Applied sciences
Bacteria, Aerobic
Biological and medical sciences
Biological treatment of waters
Biotechnology
Biotransformation
Carbon Radioisotopes - analysis
Catalysis
Environment and pollution
Exact sciences and technology
Fluorocarbons - metabolism
Fundamental and applied biological sciences. Psychology
Industrial applications and implications. Economical aspects
Labeling
Other wastewaters
Oxidation
Oxidation-Reduction
Perfluoroalkyl & polyfluoroalkyl substances
Pollution
Sewage - chemistry
Sewage treatment plants
Sludge
Studies
Waste Disposal, Fluid
Wastewaters
Water treatment and pollution
title Aerobic Biotransformation of 14C-Labeled 8-2 Telomer B Alcohol by Activated Sludge from a Domestic Sewage Treatment Plant
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