首页> 外文学位 >Regulation and Environmental Abundance of Methyl-tert-Butyl Ether Degradation Genes of Methylibium petroleiphilum PM1.
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Regulation and Environmental Abundance of Methyl-tert-Butyl Ether Degradation Genes of Methylibium petroleiphilum PM1.

机译:石油石油甲基PM1甲基叔丁基醚降解基因的调控和环境丰度。

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摘要

Methyl-tert-butyl ether (MTBE) and its degradation by-product tertiary butyl alcohol (TBA) are widespread contaminants detected frequently in groundwater in California. They are recalcitrant to biodegradation under anaerobic conditions. MTBE was used as a fuel-oxygenate for almost two decades, an important source of this contamination being leaking underground fuel storage tanks. Such leaks result in the presence of other gasoline components as groundwater co-pollutants, such as BTEX (benzene, toluene, ethylbenzene and xylenes) along with MTBE. Several bacteria are known to aerobically degrade MTBE. Of these, Methylibium petroleiphilum strain PM1 can serve as a model organism to understand the molecular mechanisms of regulation of the MTBE degradation pathway, since its genome has been sequenced. This dissertation aimed to understand these mechanisms, and relate them with MTBEdegradation in the environment.;We profiled the changes in transcription of MTBE-degradation genes in strain PM1 after exposure to MTBE, benzene and ethylbenzene. We demonstrated the direct mRNA-based evidence of high induction of genes mdpA (MTBE monooxygenase), mdpJ (TBA hydroxylase) and bmoA (benzene monooxygenase) in response to MTBE, TBA and benzene, respectively. Transcription of mdpA and mdpJ decreased 4-fold and 2.5-fold, respectively, in the presence of benzene, which also corresponded to their slower degradation rates. Our results indicate that ethylbenzene, identified previously as an inhibitor of MTBE degradation in some bacteria, directly inhibits transcription of mdpA, mdpJ and bmoA in strain PM1. Further, we demonstrated the involvement of a putative transcriptional activator gene, mdpC, in the induction of genes mdpA and mdpJ of strain PM1 by creating an mdpC- mutant strain. Our results indicate that an additional independent mechanism may be involved in the induction of mdpJ in the presence of TBA. We then examined the potential role of these MTBE- and TBA-responsive genes as biomarkers for MTBE-degradation in contaminated environments. The abundance of these genes in DNA extracted from groundwater sampled at sites that were treated via air-sparging, and at untreated sites that were undergoing monitored natural attenuation, were analyzed. We found strong correlation between PM1 genes, and MTBE and TBA concentrations at several untreated sites. Conversely, all sites undergoing treatment did not show a relationship between contaminant concentrations and degradation genes. In conclusion, a deeper understanding of regulatory mechanisms and genes involved in MTBE biodegradation, and correlation of gene abundance with contaminant concentration despite variation in geographical and hydrogeological characteristics among various environmental sites, indicate a potential for using functional-gene abundances as biomarkers for active degradation processes in the field.;Organic and inorganic contaminants pose threat to water quality globally. In the developing world, pathogenic bacterial contamination is another major factor impacting the quality of drinking water. We conducted community-engaged research with a local non-profit partner to evaluate the installation, continued use and efficiency of coliform removal by bio-sand filters in Nkokonjeru, Uganda. We found that regular and timely monitoring of installed filters, and relevant re-training of personnel involved in construction, installation and maintenance of the filters was essential for their sustained efficient use. Additionally, colloidal silver coated ceramic bricks were also evaluated for coliform removal in harvested rainwater based on standard coliform tests as well as the amount of silver released in solution after repeated use. We observed complete disinfection of harvested rainwater amended with canine feces within 24 h -- 96 h in 200 L tanks. Silver was maintained in a steady-state concentration of ∼60 ppb for up to 60 days in tanks with repeated use. Therefore, our results indicated that silver-coated ceramic bricks can serve as a feasible approach for small-scale water treatment, although their adaptation requires further research regarding socio-economic acceptance of this product in communities. -.
机译:甲基叔丁基醚(MTBE)及其降解副产物叔丁醇(TBA)是加利福尼亚州地下水中经常发现的广泛污染物。它们在厌氧条件下难以降解。 MTBE被用作燃料加氧剂已有近二十年的时间,这种污染的重要来源是地下燃料储罐的泄漏。这种泄漏导致存在其他汽油成分,如BTEX(苯,甲苯,乙苯和二甲苯)以及MTBE,作为地下水的共同污染物。已知几种细菌有氧降解MTBE。其中,因为甲基苯丙氨酸甲酯菌株PM1的基因组已被测序,它可以作为模型生物来了解MTBE降解途径调控的分子机制。本文旨在了解这些机制,并将其与环境中的MTBE降解联系起来。我们分析了暴露于MTBE,苯和乙苯后PM1菌株中MTBE降解基因转录的变化。我们证明了直接基于mRNA的证据分别对MTBE,TBA和苯有高诱导力基因mdpA(MTBE单加氧酶),mdpJ(TBA羟化酶)和bmoA(苯单加氧酶)。在苯存在下,mdpA和mdpJ的转录分别降低了4倍和2.5倍,这也与它们的降解速度较慢相对应。我们的结果表明,乙苯以前被认为是某些细菌中MTBE降解的抑制剂,可直接抑制菌株PM1中mdpA,mdpJ和bmoA的转录。此外,我们证明了推定的转录激活基因mdpC通过产生mdpC突变株而参与了菌株PM1的基因mdpA和mdpJ的诱导。我们的结果表明,在存在TBA的情况下,mdpJ的诱导可能涉及其他独立机制。然后,我们检查了这些MTBE和TBA响应基因作为受污染环境中MTBE降解的生物标志物的潜在作用。分析了这些基因在从通过空气喷射处理过的地点和经过监测的自然衰减的未处理地点采样的地下水中提取的DNA中的丰度。我们发现PM1基因与MTBE和TBA浓度在几个未经处理的位点之间有很强的相关性。相反,所有接受处理的位点均未显示污染物浓度与降解基因之间的关系。总之,对MTBE生物降解所涉及的调控机制和基因的深入了解,以及尽管各个环境地点的地理和水文地质特征有所变化,但基因丰度与污染物浓度之间的相关性,表明使用功能基因丰度作为主动降解生物标记的潜力有机和无机污染物对全球水质构成威胁。在发展中国家,病原细菌污染是影响饮用水质量的另一个主要因素。我们与当地一家非营利性合作伙伴进行了社区参与的研究,以评估在乌干达Nkokonjeru通过生物砂滤器去除大肠菌的安装,持续使用和效率。我们发现,定期,及时地监视已安装的过滤器,并对参与过滤器的制造,安装和维护的人员进行相关的再培训对于持续有效地使用它们至关重要。另外,还根据标准大肠菌群试验评估了胶体涂银陶瓷砖在收获的雨水中大肠菌群的去除情况,以及重复使用后溶液中银的释放量。我们在200 L的水箱中观察到在24小时至96小时内用犬粪对收获的雨水进行了完全消毒。在重复使用的水箱中,银可保持约60 ppb的稳态浓度长​​达60天。因此,我们的结果表明,涂​​银陶瓷砖可以用作小规模水处理的可行方法,尽管其适应性需要就该产品在社区中的社会经济接受度进行进一步研究。 -

著录项

  • 作者

    Joshi, Geetika.;

  • 作者单位

    University of California, Davis.;

  • 授予单位 University of California, Davis.;
  • 学科 Soil sciences.;Ecology.;Microbiology.
  • 学位 Ph.D.
  • 年度 2014
  • 页码 180 p.
  • 总页数 180
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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