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Characteristics of contaminant transport in bank filtration through dunes

机译:通过沙丘进行堤岸过滤时污染物的输送特征

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A column experiment simulating bank filtration was conducted to evaluate characteristics of contaminant sorption and migration through saturated porous media. Also a mathematical model describing contaminant transport was developed to delineate results of column tests. Temporal and spatial distributions of ammonia, lead, phenol and trichloroethylene (TCE) were plotted as breakthrough curves (BTCs). BTCs of TCE and lead revealed more retardation in the transport up to 3 pore volumes compared to the other contaminants tested. It was attributed to the higher affinity of the TCE and lead to the solid surface. The mathematical model developed in the reported research, coupled with a linear sorption isotherm model, was based on the mass balance principle in two phases, i.e., solid phase and aqueous phase. The governing equation was generalized in the form of nondimensionalization and was solved by numerical analysis. The proposed model showed an excellent match with experimental results except in the case of TCE BTC. The proposed model was employed to simulate the behavior of ammonia under the environment of ongoing nitrification. Almost 60 times more biomass than ammonia mass was required to produce the reported water quality in the reported literature (KOWACO, 1994). The analysis of numerical experiments showed that the ammonia concentration in the bank filtrate will vary significantly as the bioactivity changes due to environmental factors such as temperature and pH in the system domain. (C) 1998 published by Elsevier Science Ltd. All rights reserved. [References: 7]
机译:进行了模拟银行过滤的柱实验,以评估污染物通过饱和多孔介质的吸附和迁移特征。还开发了描述污染物迁移的数学模型来描述色谱柱测试的结果。氨,铅,苯酚和三氯乙烯(TCE)的时间和空间分布绘制为穿透曲线(BTC)。与其他测试污染物相比,TCE和铅的BTCs在最多3个孔体积的传输中显示出更多的阻滞作用。这归因于TCE的更高亲和力并导致固体表面。在报告的研究中开发的数学模型,加上线性吸附等温线模型,是基于质量平衡原理的两个阶段,即固相和水相。控制方程以无量纲形式推广,并通过数值分析求解。提出的模型与TCE BTC情况下的实验结果非常吻合。该模型被用来模拟在持续硝化环境下氨的行为。在所报道的文献中,要达到所报告的水质,所需的生物量几乎是氨质量的60倍(KOWACO,1994)。数值实验分析表明,由于生物活性由于系统域中的温度和pH等环境因素而导致生物活性发生变化,银行滤液中的氨浓度将发生显着变化。 (C)1998年,Elsevier Science Ltd.保留所有权利。 [参考:7]

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