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热胁迫后微生物还原过程中的电子供体可利用性。

Electron donor availability for microbial reductive processes following thermal treatment.

机构信息

School of Civil and Environmental Engineering, Georgia Institute of Technology, 311 Ferst Drive, Atlanta, GA 30332-0512, USA.

出版信息

Water Res. 2011 Dec 15;45(20):6625-36. doi: 10.1016/j.watres.2011.09.033. Epub 2011 Oct 2.

Abstract

Thermal treatment is capable of removing significant free-phase chlorinated solvent mass while potentially enhancing bioremediation effectiveness by establishing temperature gradients in the perimeter of the source zone and by increasing electron donor availability. The objectives of this study were to determine the potential for enhanced reductive dechlorination activity at the intermediate temperatures that establish in the perimeter of the heated source zone, and to evaluate the effect of electron donor competition on the performance of the microbial reductive dechlorination process. Microcosms, constructed with tetrachloroethene- (PCE-) and trichloroethene- (TCE-) impacted soils from the Great Lakes, IL, and Ft. Lewis, WA, sites were incubated at temperatures of 24, 35, 50, 70, and 95 °C for 4 months. Reductive dechlorination did not occur in microcosms incubated at temperatures above 24 °C even though mesophilic PCE-to-cis-1,2-dichloroethene dechlorinators were present in Ft. Lewis soil suggesting electron donor limitations. Five days after cooling the microcosms to 24 °C and bioaugmentation with the methanogenic, PCE-to-ethene-dechlorinating consortium OW, at least 85% of the initial PCE and TCE were dechlorinated, but dechlorination ceased prior to complete conversion to ethene. Subsequent biostimulation with hydrogen gas mitigated the dechlorination stall, and conversion to ethene resumed. The results of this study demonstrated that temperatures >35 °C inhibit reductive dechlorination activity at the Great Lakes and Ft. Lewis sites, and that the majority of reducing equivalents released from the soil matrix during heat treatment are consumed in methanogenesis rather than reductive dechlorination. These observations suggest that bioaugmenting thermal treatment sites with cultures that do not contain methanogens may allow practitioners to realize enhanced dechlorination activity, a potential benefit of coupling thermal treatment with bioremediation.

摘要

热处理能够去除大量的游离相氯代溶剂,同时通过在源区周边建立温度梯度并增加电子供体的可用性,提高生物修复的效果。本研究的目的是确定在加热源区周边形成的中间温度下增强还原脱氯活性的潜力,并评估电子供体竞争对微生物还原脱氯过程性能的影响。使用来自伊利诺伊州大湖和华盛顿州刘易斯堡的受四氯乙烯 (PCE) 和三氯乙烯 (TCE) 污染的土壤构建微宇宙,在 24、35、50、70 和 95°C 的温度下孵育 4 个月。尽管刘易斯堡土壤中存在嗜温 PCE 顺-1,2-二氯乙烯脱氯菌,但在孵育温度高于 24°C 的微宇宙中没有发生还原脱氯,这表明电子供体受到限制。将微宇宙冷却至 24°C 并添加产甲烷的 PCE 到乙烯脱氯的 consortium OW 进行生物强化 5 天后,至少 85%的初始 PCE 和 TCE 被脱氯,但在完全转化为乙烯之前脱氯停止。随后用氢气进行生物刺激缓解了脱氯停顿,恢复了转化为乙烯的过程。本研究的结果表明,温度高于 35°C 会抑制大湖和刘易斯堡两个地点的还原脱氯活性,而且在热处理过程中从土壤基质中释放的大部分还原当量都用于甲烷生成而不是还原脱氯。这些观察结果表明,在用不含有甲烷菌的培养物生物强化热治疗地点可能会使从业者实现增强的脱氯活性,这是将热治疗与生物修复相结合的潜在益处。

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