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A one-dimensional reactive multi-component transport model for biodegradation of petroleum hydrocarbons in groundwater

机译:地下水中石油烃生物降解的一维反应多组分迁移模型

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A one-dimensional (1-D) multi-component model accounting for hydro1ogical transport inorganic equilibrium chemistry and microbial activity during kinetically controlled biodegradation in groundwater of compounds such as benzene, toluene, ethylbenzene and xylenes (BTEX) is presented. The problem is solved numerically using an operator-splitting method to couple advective- dispersive transport of organic and inorganic solutes with a geochemical equilibrium package PHREEQC and a biodegradation module. The transport equations for inorganic solutes are solved for total aqueous component concentrations. Changes in such concentrations due to precipitation/dissolution of minerals and chemical speciation are accounted for within PHREEQC. For chemical elements occurring in multiple valence states, separate components are defined and transported. The biodegradation module simulates the sequential or parallel activity of multiple bacterial groups attached to soils and their biochemical effects. The model has been evaluated by comparison with an existing model simulation of a l-D inorganic redox problem. An application of the model is shown for a synthetic case where BTEX compounds are degraded by sequential reduction of aqueous electron acceptors.
机译:提出了一维(1-D)多组分模型,该模型解释了在动力学控制下的地下水中苯,甲苯,乙苯和二甲苯(BTEX)等化合物的动力学控制下的无机迁移化学和微生物活性。使用算子分解方法将有机和无机溶质的对流分散传输与地球化学平衡软件包PHREEQC和生物降解模块耦合,以数值方式解决了该问题。求解了无机溶质的输运方程,求出总含水成分的浓度。在PHREEQC中考虑了由于矿物质的沉淀/溶解和化学形态变化而导致的这种浓度变化。对于以多价态出现的化学元素,单独的成分被定义和运输。生物降解模块模拟附着在土壤上的多个细菌群的顺序或平行活性及其生化作用。通过与现有的1D无机氧化还原问题的模型仿真进行比较,对模型进行了评估。显示了该模型在合成案例中的应用,其中BTEX化合物通过依次还原含水电子受体而降解。

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