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Exploring the capacity for anaerobic biodegradation of polycyclic aromatic hydrocarbons and naphthenic acids by microbes from oil-sands-process-affected waters

机译:探索受油砂工艺影响的水中微生物对多环芳烃和环烷酸进行厌氧生物降解的能力

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摘要

© 2015 Elsevier Ltd. Both polycyclic aromatic hydrocarbons (PAHs) and naphthenic acids (NAs) are natural components of fossil fuels, but they are also widespread toxic and environmentally persistent pollutants. They are the major cause of environmental toxicity in oil-sands-process waters (OSPW). This study aimed to investigate the anaerobic biodegradation of the PAHs pyrene and 2-methylnaphthalene, and the NAs adamantane-1-carboxylic acid and a "natural" NA mixture (i.e., acid-extractable NAs from OSPW) under sulfate-reducing and methanogenic conditions by a microbial community derived from an oil sands tailings pond. Using gas-chromatography mass spectrometry (GC-MS), the rate of biodegradation was measured in relation to changes in bacterial community composition. Only 2-methylnaphthalene was significantly degraded after 260 days, with significantly more degradation under sulfate-reducing (40%) than methanogenic conditions (25%). During 2-methylnaphthalene biodegradation, a major metabolite was produced and tentatively identified as 2-naphthoic acid. Denaturing gradient gel electrophoresis (DGGE) demonstrated an increase in intensity of bands during the anaerobic biodegradation of 2-methylnaphalene, which derived from species of the genera Fusibacter, Alkaliphilus, Desulfobacterium, Variovorax, Thaurea, and Hydrogenophaga. Despite the biodegradation of 2-methylnaphthalene, this study demonstrates that, under anaerobic conditions, NAs and high-molecular-weight PAHs are the predominant molecules likely to persist in OSPW. Therefore alternative remediation strategies are required.
机译:©2015 Elsevier Ltd.多环芳烃(PAH)和环烷酸(NAs)都是化石燃料的天然成分,但它们也是广泛的有毒和对环境有害的污染物。它们是油砂工艺水(OSPW)对环境毒性的主要原因。这项研究旨在研究在硫酸盐还原和产甲烷条件下,PAHs and和2-甲基萘,NAs金刚烷-1-羧酸和“天然” NA混合物(即来自OSPW的酸可萃取NAs)的厌氧生物降解。由源自油砂尾矿池的微生物群落组成。使用气相色谱质谱法(GC-MS),测量了生物降解速率与细菌群落组成的变化之间的关系。在260天后,只有2-甲基萘被显着降解,在还原硫酸盐的条件下(40%),降解程度比在产甲烷条件下(25%)明显多。在2-甲基萘生物降解过程中,产生了主要代谢产物,并初步鉴定为2-萘甲酸。变性梯度凝胶电泳(DGGE)显示了2-甲基萘的厌氧生物降解过程中条带强度的增加,该甲基化来源于Fusibacter,Alkaliphilus,Desulfobacter,Variovorax,Thaurea和Hydrogenophaga属。尽管2-甲基萘被生物降解,但这项研究表明,在厌氧条件下,NAs和高分子量PAHs是OSPW中可能持续存在的主要分子。因此,需要其他补救策略。

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