Fahrenfeld N, Pruden A, Widdowson M
Civil & Environmental Engineering, Rutgers, The State University of New Jersey, 96 Frelinghuysen Rd., Piscataway, NJ, 08854, USA.
Civil & Environmental Engineering, Virginia Tech, 418 Durham Hall, Blacksburg, VA, 24061-0246, USA.
Biodegradation. 2017 Feb;28(1):27-36. doi: 10.1007/s10532-016-9775-4. Epub 2016 Oct 20.
Methyl ethyl ketone (MEK) is a common groundwater contaminant often present with more toxic compounds of primary interest. Because of this, few studies have been performed to determine the effect of microbial community structure on MEK biodegradation rates in aquifer sediments. Here, microcosms were prepared with aquifer sediments containing MEK following a massive spill event and compared to laboratory-spiked sediments, with MEK biodegradation rates quantified under mixed aerobic/anaerobic conditions. Biodegradation was achieved in MEK-contaminated site sediment microcosms at about half of the solubility (356 mg/L) with largely Firmicutes population under iron-reducing conditions. MEK was biodegraded at a higher rate [4.0 ± 0.74 mg/(L days)] in previously exposed site samples compared to previously uncontaminated sediments [0.51 ± 0.14 mg/(L days)]. Amplicon sequencing and denaturing gradient gel electrophoresis of 16S rRNA genes were combined to understand the relationship between contamination levels, biodegradation, and community structure across the plume. More heavily contaminated sediments collected from an MEK-contaminated field site had the most similar communities than less contaminated sediments from the same site despite differences in sediment texture. The more diverse microbial community observed in the laboratory-spiked sediments reduced MEK concentration 47 % over 92 days. Results of this study suggest lower rates of MEK biodegradation in iron-reducing aquifer sediments than previously reported for methanogenic conditions and biodegradation rates comparable to previously reported nitrate- and sulfate-reducing conditions.
甲乙酮(MEK)是一种常见的地下水污染物,常与更具毒性的主要关注化合物同时存在。正因如此,很少有研究来确定微生物群落结构对含水层沉积物中MEK生物降解速率的影响。在此,在一次大规模泄漏事件后,用含有MEK的含水层沉积物制备了微观模型,并与实验室添加MEK的沉积物进行比较,在有氧/厌氧混合条件下对MEK生物降解速率进行了量化。在铁还原条件下,MEK污染场地沉积物微观模型中实现了生物降解,降解量约为溶解度(356mg/L)的一半,主要菌群为厚壁菌门。与先前未受污染的沉积物[0.51±0.14mg/(L·天)]相比,先前暴露场地的样品中MEK的生物降解速率更高[4.0±0.74mg/(L·天)]。结合16S rRNA基因的扩增子测序和变性梯度凝胶电泳,以了解羽流中污染水平、生物降解和群落结构之间的关系。尽管沉积物质地不同,但从MEK污染现场采集的污染更严重的沉积物与同一地点污染较轻的沉积物具有最相似的群落。在实验室添加MEK的沉积物中观察到的更多样化的微生物群落,在92天内使MEK浓度降低了47%。本研究结果表明,与先前报道的产甲烷条件相比,铁还原含水层沉积物中MEK的生物降解速率较低,且与先前报道的硝酸盐和硫酸盐还原条件下的生物降解速率相当。