首页> 外文期刊>Grundwasser >Derivation of organic carbon reactivity in a redox-stratified aquifer-hydrogeochemical modelling of kinetically driven reaction systems [Ableitung der Reaktivit?t von organisch gebundenem Kohlenstoff in redoxzonierten Grundwasserleitern - Hydrogeochemische Modellierung kinetisch angetriebener Reaktionssysteme]
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Derivation of organic carbon reactivity in a redox-stratified aquifer-hydrogeochemical modelling of kinetically driven reaction systems [Ableitung der Reaktivit?t von organisch gebundenem Kohlenstoff in redoxzonierten Grundwasserleitern - Hydrogeochemische Modellierung kinetisch angetriebener Reaktionssysteme]

机译:动力学驱动反应体系的氧化还原分层含水层-水地球化学模型中的有机碳反应性的推导[氧化还原分区含水层中有机结合碳的反应活性的推导-动力学驱动反应系统的水地球化学模型]

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摘要

Within a multitude of groundwater catchment areas, ground- and raw water quality depend foremost on the reaction between organic carbon and dissolved oxidants, in particular O_(2(aq)), nitrate und sulphate. Although the redox reactions between organic carbon (as the reductive agent) and the oxidants follow the principles of chemical thermodynamics, they are often kinetically inhibited. Modelling of concentration changes in ground- and raw water quality using hydrogeochemical reactive transport models therefore requires an imple-mentation of the kinetically-limited oxidation of organic carbon. As illustrated by the case study at Forstwald (Krefeld, Germany), it is demonstrated how organic carbon reactivity can be derived from routinely measured groundwater data and implemented in a reactive transport model using the program PhreeqC. Based on equilibrium chemistry of aqueous solutions including minerals and gases, equilibrium calculations are coupled with a dual Michaelis-Menten-kinetic model to simulate the sequential oxidative degradation of solid-state, non-mobile organic carbon along the flow path. The model is verified by comparing measured and modelled data of temporal and spatial development of groundwater quality.
机译:在许多地下水集水区中,地下水和原水的质量首先取决于有机碳与溶解性氧化剂之间的反应,尤其是O_(2(aq)),硝酸盐和硫酸盐。尽管有机碳(作为还原剂)与氧化剂之间的氧化还原反应遵循化学热力学原理,但它们通常在动力学上受到抑制。因此,使用水文地球化学反应性运输模型对地下水和原水质量的浓度变化进行建模,需要对有机碳进行动力学限制的氧化。如Forstwald(德国克雷菲尔德)的案例研究所示,它证明了如何从常规测量的地下水数据中导出有机碳反应性,并使用程序PhreeqC在反应性运输模型中实现有机碳反应性。基于包括矿物质和气体在内的水溶液的平衡化学性质,将平衡计算与对偶Michaelis-Menten动力学模型相结合,以模拟固态非流动有机碳沿流动路径的顺序氧化降解。通过比较地下水质量时空发展的实测数据和模型化数据来验证该模型。

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