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Effects of microbial activity on perfluorinated carboxylic acids (PFCAs) generation during aerobic biotransformation of fluorotelomer alcohols in activated sludge

机译:活性污泥中含氟端粒醇的好氧生物转化过程中微生物活性对全氟羧酸生成的影响

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Biotransformation of fluorotelomer alcohols (FTOHs) in wastewater treatment plants (WWTPs) can release toxic intermediates and perfluorinated carboxylic acids (PFCAs) to the aqueous environment However, little information is known about the role of relevant microbial activity (i.e., autotrophs and/or heterotrophs) in biotransformation of FTOHs. Additionally, the dynamics of microbial community in sludge after exposure to FTOHs remain unclear. In the present research, using domestic and industrial WWTP sludge, we performed lab-scale batch experiments to characterize the FTOHs biodegradation property under aerobic condition. Both heterotrophs and the autotrophs were associated with FTOHs biotransformation. However, the microbial activity influenced PFCAs generation efficiency. Autotrophs based on ammonia oxidation (50 mgN/L) resulted in more effective generation of PFCAs than heterotrophs based on glucose (200 mgC/L) metabolism. Moreover, autotrophs generated more amounts of short-chain PFCAs (carbon number ≤7) than the heterotrophs. The ammonia monooxygenase (AM0) in ammonia oxidizing microorganisms (AOMs) are suggested as responsible for the enhanced generation of PFCAs during FTOHs biotransformation. In the sludge that had been exposed to poly- and perfluorinated alkyl substances in an industrial WWTP, Chlorobi was the predominant microorganisms (36.9%), followed by Proteobacteria (202%), Bacteroidetes (11.1%), Chloroflexi (6.2%), Crenarchaeota (5.6%), Pianctomycetes (4.2%), and Acidobacteria (3.5%). In the present research, the dosed 8:2 FTOH (12.1 mg/L) and its biotransformation products (intermediates and PFCAs) could force a shift in microbial community composition in the sludge. After 192 h, Proteobacteria significantly increased and dominated. These results provide knowledge for comprehending the effects of microbial activity on FTOHs biodegradation and the information about interaction between microbial community and the exposure to FTOHs in activated sludge.
机译:废水处理厂(WWTP)中的含氟端粒醇(FTOH)的生物转化可将有毒的中间体和全氟化羧酸(PFCA)释放到水环境中。但是,有关微生物活性(例如自养和/或异养生物)的作用的信息很少FTOH的生物转化)。此外,接触FTOH后污泥中微生物群落的动态仍不清楚。在本研究中,我们使用生活污水和工业污水处理厂的污泥,进行了实验室规模的分批实验,以表征好氧条件下FTOH的生物降解特性。异养生物和自养生物都与FTOH的生物转化有关。然而,微生物活性影响了PFCA的产生效率。基于氨氧化的自养生物(50 mgN / L)比基于葡萄糖代谢的异养生物(200 mgC / L)能更有效地生成PFCA。此外,自养生物比异养生物产生更多的短链PFCA(碳原子数≤7)。氨氧化微生物(AOM)中的氨单加氧酶(AM0)被认为是导致FTOHs生物转化过程中PFCAs产生增加的原因。在工业污水处理厂中暴露于多氟和全氟烷基物质的污泥中,主要微生物(36.9%)是绿藻菌,其次是变形杆菌(202%),拟杆菌(11.1%),绿弯曲菌(6.2%),Crenarchaeota (5.6%),片菌(4.2%)和酸菌(3.5%)。在本研究中,按剂量比例8:2的FTOH(12.1 mg / L)及其生物转化产物(中间体和PFCA)可能会迫使污泥中微生物群落组成发生变化。 192小时后,变形杆菌明显增加并占主导地位。这些结果提供了了解微生物活性对FTOHs生物降解的影响的知识,以及有关微生物群落与活性污泥中FTOH暴露之间相互作用的信息。

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