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Influence of different redox conditions and dissolved organic matter on pesticide biodegradation in simulated groundwater systems

机译:模拟地下水系统中不同氧化还原条件和可溶性有机物对农药生物降解的影响

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Insights into the influence of redox conditions, that is the availability of electron acceptors, and dissolved organic matter (DOM) on pesticide biodegradation in groundwater are key to understanding the environmental fate of pesticides in natural groundwater systems. Here, the influence of redox conditions and supplemental DOM addition on biodegradation of pesticides, 2,4-dichlorophenoxyacetic acid (2,4-D), 2,6-dichlorobenzamide (BAM), mecoprop-p (MCPP) and bentazone, was tested in microcosm and subsequent column experiments. Pesticide degradation, functional genes and changes in specific fractions and quantity of DOM were systematically quantified. In aerobic microcosm experiments, the highest 2,4-D degradation rate was obtained with the presence of more assimilable DOM. In column experiments, minimal pesticide degradation (= 33.77%) in any anaerobic redox conditions was observed in the absence of DOM. However, in the presence of DOM, 2,4-D biodegradation was considerably enhanced under nitrate-reducing conditions (from 23.5 +/- 10.2% to 82.3 +/- 11.6%) and in a column without external electron acceptor amendment (from -63 +/- 12.6% to 31.1 +/- 36.3%). Observed preferential depletion of the fulvic add fraction of DOM provides indications for specific functional DOM properties. The qPCR results show an increase in microbial biomass and functional genes (tfdA) in liquid phase after DOM addition. The results of this work provide insights into the interplays among DOM, redox geochemistry, and pesticide biodegradation, and show the potential of a novel approach - DOM addition to groundwater systems - for in situ biostimulation technology to remove pesticides from groundwater systems. (C) 2019 Published by Elsevier B.V.
机译:深入了解氧化还原条件的影响,即电子受体的可用性以及溶​​解有机物(DOM)对地下水中农药生物降解的影响,是了解天然地下水系统中农药环境命运的关键。在这里,测试了氧化还原条件和补充DOM的添加对农药,2,4-二氯苯氧基乙酸(2,4-D),2,6-二氯苯甲酰胺(BAM),甲丙prop-p(MCPP)和苯达松的生物降解的影响。在缩影和后续的柱实验中。系统地量化了农药降解,功能基因以及特定部分和DOM量的变化。在有氧微观世界实验中,在存在更多可吸收的DOM的情况下获得了最高的2,4-D降解率。在柱实验中,在没有DOM的情况下,在任何厌氧氧化还原条件下均观察到极少的农药降解(<= 33.77%)。但是,在存在DOM的情况下,在减少硝酸盐的条件下(从23.5 +/- 10.2%到82.3 +/- 11.6%),并且在没有外部电子受体修饰的色谱柱中,2,4-D生物降解显着增强(从- 63 +/- 12.6%至31.1 +/- 36.3%)。观察到的DOM富集添加部分的优先消耗为特定的功能DOM属性提供了指示。 qPCR结果显示,添加DOM后液相中微生物的生物量和功能基因(tfdA)有所增加。这项工作的结果提供了对DOM,氧化还原地球化学和农药生物降解之间相互作用的见解,并展示了一种新方法的潜力-将DOM添加到地下水系统中-用于原位生物刺激技术以从地下水系统中去除农药。 (C)2019由Elsevier B.V.发布

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