首页> 外文学位 >Factors affecting biodefluorination of fluorotelomer alcohols (FTOHs): Degradative microorganisms, transformation metabolites and pathways, and effects of co-substrates.
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Factors affecting biodefluorination of fluorotelomer alcohols (FTOHs): Degradative microorganisms, transformation metabolites and pathways, and effects of co-substrates.

机译:影响氟调聚物醇(FTOHs)生物脱氟的因素:降解性微生物,转化代谢物和途径以及共底物的影响。

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摘要

Fluorotelomer alcohols (FTOHs, F(CF2)nCH2 CH2OH) are emerging contaminants in the environment. Biodegradation of 6:2 and 8:2 FTOHs has been intensively studied using soils and activated sludge. However, little is known about the bacteria responsible for biotransformation of FTOHs. This study deciphered factors affecting biodefluorination of FTOHs and their metabolites, and developed three effective FTOH-degrading consortia.;Two alkane-degrading Pseudomonas strains (P. oleovorans and P. butanovora) can defluorinate 4:2, 6:2 and 8:2 FTOHs, with a higher degree of defluorination for 4:2 FTOH. According to the identified metabolites, P. oleovorans transformed FTOHs via two pathways I and II. Pathway I led to formation of x:2 ketone (x = n-1), x:2 sFTOH and perfluorinated carboxylic acids (PFCAs). Pathway II resulted in the formation of x:3 polyfluorinated acid and relatively minor shorter-chain PFCAs. Conversely, P. butanovora transformed FTOHs by pathway I only.;Mycobacterium vaccae JOB5 (a C1-C22 alkane-degrading bacterium) and P. fluorescens DSM 8341 (a fluoroacetate-degrading bacterium) can transform 6:2 FTOH via both pathways I and II with the formation of odd-numbered short-chain PFCAs. In the presence of dicyclopropylketone or formate, P. oleovorans transformed 6:2 FTOH six times faster and produced odd-numbered PFCAs. P. butanovora, utilized both pathways I and II in the presence of lactate, and it also produced odd-numbered PFCAs. Unlike P. oleovorans, P. fluorescens DSM 8341 could slightly convert 5:3 polyfluorinated acid (a key metabolite during 6:2 FTOH degradation, [F(CF2) 5CH2CH2COOH]) to 4:3 acid and PFPeA via one-carbon removal pathways.;Three FTOH-degrading consortia transformed FTOHs, with enhanced removal of FTOHs in the presence of n-octane. A higher copy number of alkB gene was found to correspond to better removal of FTOHs, suggesting that alkane-degrading bacteria might be the key degraders in the enrichments. The three enrichment cultures showed a similar microbial community structure.;This is the first study reporting that pure strains of alkane- and fluoroacetate-degrading bacteria can bio-transform FTOHs via different or preferred transformation pathways to remove multiple --CF2-- groups from FTOHs to form shorter-chain PFCAs, and to other perfluorinated acids. The results of this study also suggest that enhanced FTOH biodegradation is possible through co-substrate addition and/or using enrichment cultures.
机译:氟调聚物醇(FTOH,F(CF2)nCH2 CH2OH)是环境中新兴的污染物。已经使用土壤和活性污泥深入研究了6:2和8:2 FTOH的生物降解。但是,关于负责FTOHs生物转化的细菌知之甚少。这项研究破译了影响FTOH及其代谢物生物脱氟的因素,并开发了三个有效的FTOH降解财团。;两个烷烃降解的假单胞菌菌株(P. oleovorans和P.butanovora)可以将4:2、6:2和8:2脱氟。 FTOH,对于4:2 FTOH具有更高的脱氟度。根据鉴定出的代谢物,油橄榄通过两个途径I和II转化了FTOH。途径I导致形成x:2酮(x = n-1),x:2 sFTOH和全氟化羧酸(PFCA)。途径II导致形成x:3多氟酸和相对较小的短链PFCA。相反地​​,丁酸假单胞菌仅通过途径I转化FTOH;牛分枝杆菌JOB5(降解C1-C22烷烃的细菌)和荧光假单胞菌DSM 8341(通过降解氟乙酸盐的细菌)可以通过途径I和I转化6:2 FTOH。形成奇数短链PFCA。在存在二环丙基酮或甲酸酯的情况下,油菜假单胞菌以6:2的FTOH转化速度快了六倍,并产生了奇数的PFCA。丁酸假单胞菌在乳酸存在下利用途径I和II,并且还产生奇数PFCA。不同于油菜假单胞菌,荧光假单胞菌DSM 8341可以通过一碳去除途径将5:3的多氟酸(6:2 FTOH降解过程中的关键代谢物,[F(CF2)5CH2CH2COOH])轻微转化为4:3的酸和PFPeA。 。;三个降解FTOH的财团转化了FTOH,并在正辛烷存在下增强了FTOH的去除率。发现更高拷贝数的alkB基因对应于更好地去除FTOH,这表明降解烷烃的细菌可能是富集过程中的关键降解剂。三种富集培养物显示出相似的微生物群落结构;这是第一项研究报告,表明降解链烷和氟乙酸盐的细菌的纯菌株可以通过不同或优选的转化途径对FTOH进行生物转化,以从中去除多个--CF2-基团。 FTOH形成短链PFCA,并形成其他全氟酸。这项研究的结果还表明,通过共底物添加和/或使用富集培养可以提高FTOH的生物降解性。

著录项

  • 作者

    Kim, Myung Hee.;

  • 作者单位

    Texas A&M University.;

  • 授予单位 Texas A&M University.;
  • 学科 Environmental engineering.;Environmental studies.;Microbiology.
  • 学位 Ph.D.
  • 年度 2012
  • 页码 152 p.
  • 总页数 152
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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