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氟调聚物醇的生物降解——全氟化碳链分解的直接证据。

Fluorotelomer alcohol biodegradation-direct evidence that perfluorinated carbon chains breakdown.

作者信息

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

机构信息

DuPont Central Research and Development, Glasgow Business Community 301, P.O. Box 6101, Newark, Delaware 19714, USA.

出版信息

Environ Sci Technol. 2005 Oct 1;39(19):7516-28. doi: 10.1021/es0506760.

Abstract

There is increasing scientific interest to understand the environmental fate of fluorotelomer alcohols (FTOHs) and fluorotelomer-based products which may break down to FTOHs. Both are expected to enter aqueous waste streams, which would be processed in a wastewater treatment plant and therein subject to microbial biodegradation. We investigated the biodegradation of 3-14C, 1H,1H,2H,2H-perfluorodecanol [CF3(CF2)6(14)CF2CH2CH2OH, 14C-8-2 FTOH] in mixed bacterial culture and activated sludge. 14CO2 and 14C-organic volatiles in the headspace of the sealed bottles and bottles with continuous air flow were analyzed up to 4 months. After sample extraction with acetonitrile, 14C-labeled biotransformation products (metabolites) were quantified by LC/ARC (on-line liquid chromatography/ accurate radioisotope counting) and identified by quadrupole time-of-flight (Q-TOF) mass spectrometry and GC/MSD (mass selective detector). Three metabolites not yet reported in the literature have been identified as CF3(CF2)6(14)CHOHCH3 (7-2 sFTOH), CF3(CF2)6(14)CH=CHCOOH (7-3 unsaturated acid or 7-3 u acid), and CF3(CF2)6(14)CH=CHCONH2 (7-3 u amide) along with five previously reported metabolites [CF3(CF2)6(14)CF2CH2CHO (8-2 FTAL), CF3(CF2)6 (14)CF2CH2COOH (8-2 acid), CF3(CF2)6(14)CF=CHCOOH (8-2 u acid), CF3(CF2)6(14)CH2CH2COOH (7-3 acid), and CF3(CF2)6(14)COOH (PFOA)]. No CF3(CF2)6(14)CF2COOH (14C-PFNA) was observed, indicating that alpha-oxidation does not take place. It was found that strong adsorption to the activated sludge and subsequent transformation, even under continuous air flow, greatly reduced partitioning of 8-2 FTOH or any transformation products to air. CF3(CF2)4COOH (PFHA; perfluorohexanoic acid) was observed and increased in mixed bacterial culture over 28 days and accounted for about 1% of the initial 14C-8-2 FTOH concentration from day 28 to day 90. 14CO2 accounted for 1% of initial 14C in activated sludge with continuous air flow at day 1 and increased over time. In closed bottles, 14CO2 in the headspace of activated sludge medium increased to 12% of the available 14C over 135 days with periodic addition of ethanol, as compared to 3% when no additional ethanol was added. These results show that replenishment of organic carbon enhanced microbial mineralization of multiple--CF2--groups in the fluorocarbon chain of 14C-8-2 FTOH. At day 90 the net increase of fluoride ion in the mixed bacterial culture was 93 microg L(-1), equivalent to 12% of total mineralization (destruction) of the 14C-8-2 FTOH. These results demonstrate that perfluorinated carbon bonds of 14C-8-2 FTOH are defluorinated and mineralized by microorganisms under conditions which may occur in a wastewater treatment plant, forming shorter fluorinated carbon metabolites.

摘要

人们对了解氟调聚物醇(FTOHs)以及可能分解为FTOHs的氟调聚物基产品在环境中的归宿越来越感兴趣。预计这两者都会进入含水废物流,这些废物流将在废水处理厂进行处理,并在其中进行微生物生物降解。我们研究了3-14C、1H,1H,2H,2H-全氟癸醇[CF3(CF2)6(14)CF2CH2CH2OH,14C-8-2 FTOH]在混合细菌培养物和活性污泥中的生物降解情况。对密封瓶和有连续气流的瓶顶空中的14CO2和14C-有机挥发物进行了长达4个月的分析。用乙腈萃取样品后,通过LC/ARC(在线液相色谱/精确放射性同位素计数)对14C标记的生物转化产物(代谢物)进行定量,并通过四极杆飞行时间(Q-TOF)质谱和GC/MSD(质量选择检测器)进行鉴定。已鉴定出三种文献中尚未报道的代谢物,分别为CF3(CF2)6(14)CHOHCH3(7-2 sFTOH)、CF3(CF2)6(14)CH=CHCOOH(7-3不饱和酸或7-3 u酸)和CF3(CF2)6(14)CH=CHCONH2(7-3 u酰胺),以及五种先前报道的代谢物[CF3(CF2)6(14)CF2CH2CHO(8-2 FTAL)、CF3(CF2)6(14)CF2CH2COOH(8-2酸)、CF3(CF2)6(14)CF=CHCOOH(8-2 u酸)、CF3(CF2)6(14)CH2CH2COOH(7-3酸)和CF3(CF2)6(14)COOH(PFOA)]。未观察到CF3(CF2)6(14)CF2COOH(14C-PFNA),表明α-氧化未发生。研究发现,即使在连续气流下,14C-8-2 FTOH或任何转化产物对活性污泥的强烈吸附及其随后的转化,也大大减少了其向空气中的分配。观察到CF3(CF2)4COOH(PFHA;全氟己酸),其在混合细菌培养物中28天内增加,并在第28天至第90天占初始14C-8-2 FTOH浓度的约1%。在有连续气流的情况下,活性污泥中14CO2在第1天占初始14C的1%,并随时间增加。在封闭瓶中,活性污泥培养基顶空中的14CO2在135天内通过定期添加乙醇增加到可用14C的12%,而不添加额外乙醇时为3%。这些结果表明,有机碳的补充增强了14C-8-2 FTOH碳氟链中多个-CF2-基团的微生物矿化作用。在第90天,混合细菌培养物中氟离子的净增加量为93 μg L(-1),相当于14C-8-2 FTOH总矿化(分解)量的12%。这些结果表明,在废水处理厂可能出现的条件下,微生物可使14C-8-2 FTOH的全氟碳键脱氟并矿化,形成较短的含氟碳代谢物。

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