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Mixing-controlled biodegradation in a toluene plume — Results from two-dimensional laboratory experiments

机译:甲苯羽流中混合控制的生物降解—二维实验室实验的结果

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Various abiotic and biotic processes such as sorption, dilution, and degradation are known to affect the fate of organic contaminants, such as petroleum hydrocarbons in saturated porous media. Reactive transport modeling of such plumes indicates that the biodegradation of organic pollutants is, in many cases, controlled by mixing and therefore occurs locally at the plume's fringes, where electron donors and electron-acceptors mix. Herein, we aim to test whether this hypothesis can be verified by experimental results obtained from aerobic and anaerobic degradation experiments in two-dimensional sediment microcosms. Toluene was selected as a model compound for oxidizable contaminants. The two-dimensional microcosm was filled with quartz sand and operated under controlled flow conditions simulating a contaminant plume in otherwise uncontaminated groundwater. Aerobic degradation of toluene by Pseudomonas putida mt-2 reduced a continuous 8.7 mg L~(-1) toluene concentration by 35% over a transport distance of 78 cm in 15.5 h. In comparison, under similar conditions Aromatoleum aromaticum strain EbN1 degraded 98% of the toluene infiltrated using nitrate (68.5 ±6.2 mg L~(-1)) as electron acceptor. A major part of the biodegradation activity was located at the plume fringes and the slope of the electron-acceptor gradient was steeper during periods of active biodegradation. The distribution of toluene and the significant overlap of nitrate at the plume's fringe indicate that biokinetic and/or microscale transport processes may constitute additional limiting factors. Experimental data is corroborated with results from a reactive transport model using double Monod kinetics. The outcome of the study shows that in order to simulate degradation in contaminant plumes, detailed data sets are required to test the applicability of models. These will have to deal with the incorporation of existing parameters coding for substrate conversion kinetics and microbial growth.
机译:已知各种非生物和生物过程(例如吸附,稀释和降解)会影响有机污染物(例如饱和多孔介质中的石油烃)的命运。此类羽流的反应性传输模型表明,在许多情况下,有机污染物的生物降解受混合控制,因此局部发生在羽流的边缘,在此电子供体和电子受体混合。在此,我们旨在检验是否可以通过二维沉积物微观世界中需氧和厌氧降解实验的实验结果来验证该假设。选择甲苯作为可氧化污染物的模型化合物。二维缩影充满了石英砂,并在受控流量条件下运行,模拟了原本未被污染的地下水中的污染物羽流。恶臭假单胞菌mt-2对甲苯的需氧降解在15.5小时内的78 cm输送距离上连续降低了8.7 mg L〜(-1)甲苯浓度达35%。相比之下,在相似的条件下,芳香族芳香族菌株EbN1降解了使用硝酸盐(68.5±6.2 mg L〜(-1))作为电子受体渗透的甲苯98%。生物降解活性的主要部分位于羽状边缘,在活性生物降解期间,电子受体梯度的斜率更陡。甲苯分布和烟羽边缘处硝酸盐的显着重叠表明,生物动力学和/或微观尺度的运输过程可能构成其他限制因素。实验数据与使用双Monod动力学的反应性传输模型的结果得到了证实。研究结果表明,为了模拟污染物羽流的降解,需要详细的数据集来测试模型的适用性。这些将必须处理编码底物转化动力学和微生物生长的现有参数的合并。

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