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Adsorption Desorption Processes in Subsurface Reactive Transport Modeling

机译:地下反应迁移模型中的吸附解吸过程

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摘要

Adsorption–desorption reactions are important processes that affect the transport of contaminants in the environment. Various empirical approaches, such as the distribution coefficient and Freundlich and Langmuir isotherm equations, have been used to represent adsorption. The empirical approaches are not capable of accounting for the effects of variable chemical conditions, such as pH, on adsorption reactions. This can be done using chemical models such as surface complexation models. These models define specific surface species, chemical reactions, equilibrium constants, mass balances, and charge balances, and their molecular features can be given thermodynamic significance. Ion adsorption mechanisms and surface configurations for the surface complexation models can be established from independent experimental observations. These include both indirect measurements, such as point of zero charge shifts, ionic strength effects, and calorimetry, and direct spectroscopic techniques, including vibrational spectroscopy, nuclear magnetic resonance (NMR) spectroscopy, and X-ray absorption spectroscopy. Surface complexation models were developed for single mineral phases but have now been applied to natural mineral assemblages using both component additivity (CA) and generalized composite (GC) approaches. Surface complexation models have been incorporated into subsurface transport models at several field sites, although simplifying assumptions are needed to deal with heterogeneous materials. Surface complexation models for contaminant adsorption have the potential to increase the confidence and scientific credibility of transport modeling by reducing the uncertainty in quantifying retardation and providing a means of quantifying that uncertainty.
机译:吸附-解吸反应是影响环境中污染物迁移的重要过程。 各种经验方法,如分布系数 和Freundlich和Langmuir等温线方程已用于 来表示吸附。经验方法不能 解释可变化学条件(例如pH)对吸附反应的影响。可以使用 化学模型(例如表面络合模型)来完成。这些模型 定义比表面种类,化学反应,平衡 常数,质量平衡和电荷平衡,以及它们的分子 特征可以赋予热力学意义。 。可以通过独立的实验观察来建立表面络合模型的离子吸附 机制和表面构型。 包括间接测量,例如点的测量。零 电荷位移,离子强度效应和量热法,以及 直接光谱技术,包括振动光谱, 核磁共振(NMR)光谱和X射线吸收 光谱学。表面络合模型是针对 单一矿物相开发的,但是现在已使用成分加和(CA)和广义 复合材料将其应用于天然矿物 组合( GC)方法。尽管需要简化假设以 处理非均质材料,但表面络合模型已在多个 现场站点引入了地下传输模型。用于污染物吸附的表面络合模型 可以通过减少量化延迟的不确定性并提供 的可能性和运输模型 的科学可信度。 sup> 一种量化不确定性的方法。

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  • 来源
    《Vadose Zone Journal 》 |2007年第3期| 407-435| 共29页
  • 作者单位

    USDA-ARS, U.S. Salinity Lab., 450 W. Big Springs Rd., Riverside, CA 92507;

    Sandia National Lab., P.O. Box 5800, MS 0750, Albuquerque, NM 87185-0750;

    Center for Nuclear Waste Regulatory Analyses, 6220 Culebra Rd., San Antonio, TX 78284;

    U.S. Geological Survey, 345 Middlefield Rd., Menlo Park, CA 94025;

    Pacific Northwest National Lab., P.O. Box 999, Richland, WA 99352;

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  • 正文语种 eng
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