Literature DB >> 15707053

Aerobic biotransformation of 14C-labeled 8-2 telomer B alcohol by activated sludge from a domestic sewage treatment plant.

Ning Wang1, Bogdan Szostek, Patrick W Folsom, Lisa M Sulecki, Vladimir Capka, Robert C Buck, William R Berti, John T Gannon.   

Abstract

This study investigated the biodegradation potential of 3-(14)C,1H,1H,2H,2H-perfluorodecanol [CF3(CF2)6(14)CF2CH2CH2OH, 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(14)CF2CH2COOH (8-2 saturated acid); CF3(CF2)6(14)CF=CHCOOH (8-2 unsaturated acid); and CF3(CF2)6(14)COOH (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(14)CH2CH2COOH (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 beta-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 beta-oxidation due to the proton deficiency in their beta-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(14)CF2CH2COOH 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(14)CF2COOH (perfluorononanoic acid) was observed, indicating that alpha-oxidation of CF3(CF2)6(14)CF2CH2COOH 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 beta-oxidation nor any other enzyme-catalyzed reactions as a single dominant (principal) mechanism under the study conditions.

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Year:  2005        PMID: 15707053     DOI: 10.1021/es049466y

Source DB:  PubMed          Journal:  Environ Sci Technol        ISSN: 0013-936X            Impact factor:   9.028


  13 in total

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Journal:  Environ Sci Technol       Date:  2006-01-01       Impact factor: 9.028

2.  Impact of fluorotelomer alcohols (FTOH) on the molecular and macroscopic phenotype of Tetrahymena thermophila.

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3.  Perfluoroalkyl compounds in municipal WWTPs in Tianjin, China--concentrations, distribution and mass flow.

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4.  Formation of PFOA from 8:2 FTOH in closed-bottle experiments with brackish water.

Authors:  Juha Keränen; Heidi Ahkola; Juha Knuutinen; Sirpa Herve; Marko Reinikainen; Jaana Koistinen
Journal:  Environ Sci Pollut Res Int       Date:  2013-07-24       Impact factor: 4.223

5.  Perfluoroalkyl acids in selected wastewater treatment plants and their discharge load within the Lake Victoria basin in Kenya.

Authors:  Florah Chirikona; Marko Filipovic; Seline Ooko; Francis Orata
Journal:  Environ Monit Assess       Date:  2015-04-11       Impact factor: 2.513

6.  Structure-Specific Aerobic Defluorination of Short-Chain Fluorinated Carboxylic Acids by Activated Sludge Communities.

Authors:  Shun Che; Bosen Jin; Zekun Liu; Yaochun Yu; Jinyong Liu; Yujie Men
Journal:  Environ Sci Technol Lett       Date:  2021-07-26

7.  Persistence of perfluoroalkylated substances in closed bottle tests with municipal sewage sludge.

Authors:  Monica Sáez; Pim de Voogt; John R Parsons
Journal:  Environ Sci Pollut Res Int       Date:  2008-07-02       Impact factor: 4.223

8.  Neutral poly- and perfluoroalkyl substances in air and seawater of the North Sea.

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Journal:  Environ Sci Pollut Res Int       Date:  2013-05-02       Impact factor: 4.223

Review 9.  Perfluoroalkyl and polyfluoroalkyl substances in the environment: terminology, classification, and origins.

Authors:  Robert C Buck; James Franklin; Urs Berger; Jason M Conder; Ian T Cousins; Pim de Voogt; Allan Astrup Jensen; Kurunthachalam Kannan; Scott A Mabury; Stefan P J van Leeuwen
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10.  Perfluorooctanoic acid-induced immunomodulation in adult C57BL/6J or C57BL/6N female mice.

Authors:  Jamie C Dewitt; Carey B Copeland; Mark J Strynar; Robert W Luebke
Journal:  Environ Health Perspect       Date:  2008-05       Impact factor: 9.031

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