Transport of reactive solute in unsaturated soils under an infiltration-redistribution cycle is investigated. The study is based on the model of vertical flow and transport in the unsaturated zone proposed by Indelman et al. (1998), and generalizes it by accounting for linear nonequilibrium kinetics. An exact analytical solution is derived for an irreversible desorption reaction. The transport of solute obeying linear kinetics is modeled by assuming equilibrium during the redistribution stage. The model which accounts for nonequilibrium during the infiltration and assumes equilibrium at the redistribution stage is termed PEIRM (partial equilibrium infiltration-redistribution model). It allows to derive approximate closed form solutions for transport in one-dimensional homogeneous soils. These solutions are further applied to computing the field-scale concentration by adopting the Dagan and Bresler (1979) column model. The effect of soil heterogeneity on the solute spread is investigated by modeling the hydraulic saturated conductivity as a random function of horizontal coordinates. The quality of the PEIRM is illustrated by calculating the critical values of the Damköhler number which provide the achievable accuracy in estimating the solute mass in the mobile phase. The distinguishing feature of transport during the infiltration-redistribution cycle as compared to that of infiltration only is the finite depth of solute penetration. For irreversible desorption the maximum solute penetration W/θr is determined by the amount of applied water W and the residual water content θr. For sorption-desorption kinetics the maximum depth of penetration also depends on the ratio between the rate of application and the column saturated conductivity. It is shown that zr is bounded between the depths W/(θr+Kd) and W/θr corresponding to the maximum solute penetration for equilibrium transport and for irreversible desorption, respectively. This feature of solute penetration explains the unusual phenomena of plume contraction after an initial period of spreading (Lessoff et al., 2002). Unlike transport under equilibrium conditions, when the solute is completely concentrated at the front, the solute under nonequilibrium conditions is spread out behind the front. Heterogeneity leads to additional spreading of the plume.

Analytical Solutions for Reactive Solute Transport Under an Infiltration-Redistribution Cycle / Severino, Gerardo; Indelman, P.. - In: JOURNAL OF CONTAMINANT HYDROLOGY. - ISSN 0169-7722. - STAMPA. - 70:1(2004), pp. 89-115. [10.1016/j.jconhyd.2003.08.007]

Analytical Solutions for Reactive Solute Transport Under an Infiltration-Redistribution Cycle

SEVERINO, GERARDO;
2004

Abstract

Transport of reactive solute in unsaturated soils under an infiltration-redistribution cycle is investigated. The study is based on the model of vertical flow and transport in the unsaturated zone proposed by Indelman et al. (1998), and generalizes it by accounting for linear nonequilibrium kinetics. An exact analytical solution is derived for an irreversible desorption reaction. The transport of solute obeying linear kinetics is modeled by assuming equilibrium during the redistribution stage. The model which accounts for nonequilibrium during the infiltration and assumes equilibrium at the redistribution stage is termed PEIRM (partial equilibrium infiltration-redistribution model). It allows to derive approximate closed form solutions for transport in one-dimensional homogeneous soils. These solutions are further applied to computing the field-scale concentration by adopting the Dagan and Bresler (1979) column model. The effect of soil heterogeneity on the solute spread is investigated by modeling the hydraulic saturated conductivity as a random function of horizontal coordinates. The quality of the PEIRM is illustrated by calculating the critical values of the Damköhler number which provide the achievable accuracy in estimating the solute mass in the mobile phase. The distinguishing feature of transport during the infiltration-redistribution cycle as compared to that of infiltration only is the finite depth of solute penetration. For irreversible desorption the maximum solute penetration W/θr is determined by the amount of applied water W and the residual water content θr. For sorption-desorption kinetics the maximum depth of penetration also depends on the ratio between the rate of application and the column saturated conductivity. It is shown that zr is bounded between the depths W/(θr+Kd) and W/θr corresponding to the maximum solute penetration for equilibrium transport and for irreversible desorption, respectively. This feature of solute penetration explains the unusual phenomena of plume contraction after an initial period of spreading (Lessoff et al., 2002). Unlike transport under equilibrium conditions, when the solute is completely concentrated at the front, the solute under nonequilibrium conditions is spread out behind the front. Heterogeneity leads to additional spreading of the plume.
2004
Analytical Solutions for Reactive Solute Transport Under an Infiltration-Redistribution Cycle / Severino, Gerardo; Indelman, P.. - In: JOURNAL OF CONTAMINANT HYDROLOGY. - ISSN 0169-7722. - STAMPA. - 70:1(2004), pp. 89-115. [10.1016/j.jconhyd.2003.08.007]
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Utilizza questo identificativo per citare o creare un link a questo documento: https://hdl.handle.net/11588/111936
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