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Parallel pathways of ethoxylated alcohol biodegradation under aerobic conditions

机译:有氧条件下乙氧基化酒精生物降解的平行途径

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摘要

Non-ionic surfactants (NS) are a major component of the surfactant flux discharged into surface water, and alcohol ethoxylates (AE) are the major component of this flux. Therefore, biodegradation pathways of AE deserve more thorough investigation. The aim of this work was to investigate the stages of biodegradation of homogeneous oxyethylated dodecanol C_(12)E_9 having 9 oxyethylene subunits, under aerobic conditions. Enterobacter strain Z3 bacteria were chosen as biodegrading organisms under conditions with C_(12)E_9 as the sole source of organic carbon. Bacterial consortia of river water were used in a parallel test as an inoculum for comparison. The LC-MS technique was used to identify the products of biodegradation. Liquid-liquid extraction with ethyl acetate was selected for the isolation of C_(12)E_9 and metabolites from the biodegradation broth. The LC-MS/MS technique operating in the multiple reaction monitoring (MRM) mode was used for quantitative determination of C_(12)E_9, C_(12)E_8, C_(12)E_7 and C_(12)E_6. Apart from the substrate, the homologues C_(12)E_8, C_(12)E_7 and C_(12)E_6, being metabolites of C_(12)E_9 biodegradation by shortening of the oxyethylene chain, as well as intermediate metabolites having a carboxyl end group in the oxyethylene chain (C_(12)E_8COOH, C_(12)E_7COOH, C_(12)E_6COOH and C_(12)E_5COOH), were identified. Polyethylene glycols) (E) having 9, 8 and 7 oxyethylene subunits were also identified, indicating parallel central fission of C_(12)E_9 and its metabolites. Similar results were obtained with river water as inoculum. It is concluded that AE, under aerobic conditions, are biodegraded via two parallel pathways: by central fission with the formation of PEG, and by Ω-oxidation of the oxyethylene chain with the formation of carboxylated AE and subsequent shortening of the oxyethylene chain by a single unit.
机译:非离子表面活性剂(NS)是排放到地表水中的表面活性剂焊剂的主要成分,醇乙氧基化物(AE)是该焊剂的主要成分。因此,AE的生物降解途径值得更深入的研究。这项工作的目的是研究有氧条件下具有9个氧乙烯亚基的均相氧乙基化十二烷醇C_(12)E_9的生物降解阶段。在C_(12)E_9为唯一有机碳源的条件下,选择肠杆菌Z3细菌作为生物降解生物。在平行试验中使用河水细菌菌落作为接种物进行比较。 LC-MS技术用于鉴定生物降解产物。选择用乙酸乙酯进行液-液萃取,以从生物降解液中分离出C_(12)E_9和代谢物。使用在多反应监测(MRM)模式下运行的LC-MS / MS技术定量确定C_(12)E_9,C_(12)E_8,C_(12)E_7和C_(12)E_6。除底物外,同系物C_(12)E_8,C_(12)E_7和C_(12)E_6是通过缩短氧乙烯链而生物降解的C_(12)E_9的代谢物,以及具有羧基末端的中间代谢物确定了氧乙烯链中的基团(C_(12)E_8COOH,C_(12)E_7COOH,C_(12)E_6COOH和C_(12)E_5COOH)。还鉴定了具有9、8和7个氧化乙烯亚基的聚乙二醇(E),表明C_(12)E_9及其代谢物平行发生中心裂变。用河水作为接种物也得到了类似的结果。结论是,AE在好氧条件下通过两条平行途径被生物降解:通过中心裂变形成PEG,通过氧化氧化乙烯链,形成羧化AE,随后氧化乙烯链被a缩短。单个单元。

著录项

  • 来源
    《The Science of the Total Environment》 |2016年第1期|612-619|共8页
  • 作者单位

    Poznan University of Technology, Faculty of Chemical Technology, pl. Sklodowskiej-Curie 5, 60-965, Poznan, Poland, Poznan University of Technology, Faculty of Chemical Technology, ul. Berdychowo 4, 60-965 Poznan, Poland;

    Poznan University of Technology, Faculty of Chemical Technology, pl. Sklodowskiej-Curie 5, 60-965, Poznan, Poland, Poznan University of Technology, Faculty of Chemical Technology, ul. Berdychowo 4, 60-965 Poznan, Poland;

    Poznan University of Technology, Faculty of Chemical Technology, pl. Sklodowskiej-Curie 5, 60-965, Poznan, Poland, Poznan University of Technology, Faculty of Chemical Technology, ul. Berdychowo 4, 60-965 Poznan, Poland;

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  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    LC-MS; LC-MS/MS; Nonionic surfactants; Oxyethylene (5-9) dodecyl ethers; Metabolites; Enterobacter sp;

    机译:LC-MS;LC-MS / MS;非离子表面活性剂;氧乙烯(5-9)十二烷基醚;代谢物肠杆菌;

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