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Anaerobic bio-oxidation of vinyl chloride and ethene.

机译:氯乙烯和乙烯的厌氧生物氧化。

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摘要

The overall purpose of this project was to improve the methods needed to document the fate of vinyl chloride (VC) and ethene in situ. The specific objectives were (1) to document in microcosms the anaerobic oxidation of VC, using groundwater from a hazardous waste site where the field evidence suggests that bio-oxidation is occurring; (2) to document in microcosms the anaerobic oxidation of ethene, using uncontaminated soil as a source of inoculum, under a variety of anaerobic conditions; (3) to determine if microbes subjected to anaerobic conditions for longer than one year are then able to aerobically oxidize VC; and (4) to determine if nitrate can replace oxygen as a terminal electron acceptor under oxygen-limited conditions that still permit the use of oxygen as a reactant for the alkene monooxygenase.;In approximately eight of the 83 microcosms prepared with first flush groundwater from a hazardous waste site, significant levels of VC bio-oxidation occurred. However, there was considerable uncertainty whether the process observed was anaerobic or aerobic, as a consequence of oxygen leaking into the bottles. Lines of evidence in support of each scenario were reviewed. Overall, the weight of evidence suggests the activity was aerobic. Some of the considerations include the detection of low levels of oxygen by analysis of headspace samples (coupled with controls that indicated these measurements were not false positives), the pink color of resazurin during most of the time when VC was consumed, consumption of methane during or after the VC was consumed (methane is generally recalcitrant under anaerobic conditions), and the ability of microbes that grow aerobically on VC to use oxygen to the point when it is no longer detectable. Incubation of five of the active microcosms is on-going, to further assess the question of aerobic versus anaerobic activity.;Anaerobic oxidation of ethene was observed in microcosms amended with Fe(III) and Fe(III) chelated with ethylenediaminetetraacetic acid (EDTA), and in a chlororespiring enrichment culture amended with sulfate. Ethene oxidation occurred when the concentration of ethene in the headspace was increased to 1% (v/v) or higher. Prior to that, ethene was stoichiometrically reduced to ethane. Oxidation was not observed in unamended microcosms and ones with nitrate and glucose added. Unlike the results with VC, there was a high level of confidence that oxidation occurred under anaerobic conditions. Compared to VC, the rate of ethene oxidation was considerably slower. Also, oxidation activity often slowed down after 10% or less of the ethene was consumed. This type of pattern suggested the process may be cometabolic, although additional studies are needed to verify this. Also, confirmation of oxidation is needed using [ 14C]ethene.;Microcosms were prepared with soil and groundwater from a hazardous waste site and incubated under anaerobic conditions for 1.7 years, with no evidence for biodegradation of VC. When oxygen was added to the microcosms, only two of the 12 exhibited biodegradation of VC, along with methane. The results of this study indicate that aerobic biodegradation of VC may not always occur when soil and groundwater have been subjected to anaerobic conditions for an extended period, in this case 1.7 years.;The results of this study indicated that nitrate did not substitute for oxygen as a terminal electron acceptor under conditions with limited oxygen (but enough to allow functioning of the alkene monooxygenase) and an excess of nitrate. However, the results may be specific to the enrichment culture that was tested, which was able to biodegrade VC aerobically and also use acetate as a substrate under denitrifying conditions. If this process is possible, it would decrease the stoichiometric amount of oxygen needed for VC oxidation.;The inconsistencies in observations of anaerobic bio-oxidation of VC leave many questions unanswered. Considerable uncertainties also remain for the occurrence of anaerobic oxidation of ethene. As promising as previous studies appear, the hallmark of advances in science is reproducibility. Until the results of others can be replicated under conditions that are unquestionably anaerobic, the uncertainties surrounding anaerobic oxidation of VC and ethene will persist. (Abstract shortened by UMI.)
机译:该项目的总体目的是改进记录原位氯乙烯(VC)和乙烯命运的方法。具体目标是(1)使用危险废物现场的地下水在微观范围内记录VC的厌氧氧化,现场证据表明正在发生生物氧化; (2)在各种厌氧条件下,使用未污染的土壤作为接种物,以微观的方式记录乙烯的厌氧氧化; (3)确定经受厌氧条件超过一年的微生物随后是否能够对VC进行需氧氧化; (4)确定在有限的氧气条件下硝酸盐是否可以代替氧气作为末端电子受体,该条件仍允许使用氧气作为烯烃单加氧酶的反应物。在用第一个冲洗地下水制得的83个微观世界中,约有八个在一个危险废物现场,发生了大量的VC生物氧化。但是,由于氧气泄漏到瓶子中,观察到的过程是厌氧还是好氧存在很大的不确定性。审查了支持每种情况的证据线。总体而言,有证据表明该活动是有氧运动。一些考虑因素包括通过分析顶空样品(结合表明这些测量结果不是假阳性的对照)来检测低水平的氧气,在消耗VC的大部分时间里刃天青的粉红色,在消耗VC的过程中甲烷的消耗或消耗掉VC后(在厌氧条件下甲烷通常是难降解的),以及在VC上需氧生长的微生物使用氧气的能力达到无法检测到的程度。正在进行中的五个活性缩醛的培养,以进一步评估好氧与厌氧活性之间的关系;;在用Fe(III)和被乙二胺四乙酸(EDTA)螯合的Fe(III)修饰的缩醛中观察到乙烯的厌氧氧化,并在氯化呼吸富集培养中用硫酸盐修正。当顶部空间中的乙烯浓度增加到1%(v / v)或更高时,发生乙烯氧化。在此之前,乙烯化学计量还原为乙烷。在未修改的微观世界以及添加硝酸盐和葡萄糖的微观世界中未观察到氧化。与VC的结果不同,有很高的可信度认为在厌氧条件下会发生氧化。与VC相比,乙烯的氧化速度要慢得多。同样,在消耗了10%或更少的乙烯后,氧化活性通常会降低。这种类型的模式表明该过程可能是新陈代谢的,尽管还需要进一步的研究来验证这一点。此外,还需要使用[14C]乙烯来确认氧化。缩微样品是从危险废物场所的土壤和地下水中制备的,并在厌氧条件下孵育1.7年,没有VC发生生物降解的证据。当将氧气添加到微观世界时,这12个中只有两个显示出VC和甲烷的生物降解。这项研究的结果表明,当土壤和地下水长期处于厌氧条件下(在这种情况下为1.7年)时,VC的好氧生物降解可能并不总是发生;;该研究结果表明硝酸盐不能替代氧气在有限的氧气(但足以允许烯烃单加氧酶起作用)和过量的硝酸盐的条件下作为末端电子受体。但是,结果可能与所测试的富集培养物有关,该培养物能够对VC进行好氧生物降解,并且还可以在反硝化条件下使用乙酸盐作为底物。如果该过程可行,则将减少VC氧化所需的化学计量的氧气。VC厌氧生物氧化观察中的不一致之处使许多问题没有得到解答。乙烯的厌氧氧化的发生还存在相当大的不确定性。正如以前的研究一样有希望,科学发展的标志就是可再现性。除非可以在毫无疑问的厌氧条件下复制其他结果,否则围绕VC和乙烯的厌氧氧化的不确定性将持续存在。 (摘要由UMI缩短。)

著录项

  • 作者

    Reid, Anthony T.;

  • 作者单位

    Clemson University.;

  • 授予单位 Clemson University.;
  • 学科 Engineering Environmental.
  • 学位 M.S.
  • 年度 2010
  • 页码 249 p.
  • 总页数 249
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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