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Published online 22 August 2006
Published in Soil Sci Soc Am J 70:1677-1687 (2006)
DOI: 10.2136/sssaj2006.0035
© 2006 Soil Science Society of America
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Modeling the Transport and Retention of Arsenic (V) in Soils

Hua Zhang and H. M. Selim*

Sturgis Hall, Dep. of Agronomy and Environmental Management, Louisiana State Univ. Agric. Center, Baton Rouge, LA 70803-2110


Figure 1
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Fig. 1. A schematic diagram of the multireaction transport model (MRM). Here C is concentration in solution, Se, Sk, Si, and Sirr are the amounts sorbed on equilibrium, kinetic, and irreversible sites, respectively, where Ke, k1, k2, k3, and kirr are the respective rates of reactions.

 

Figure 2
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Fig. 2. Tritium breakthrough curves for soils. Solid curves depict results of curve-fitting with convection dispersion equation (CDE) for non-reactive solutes.

 

Figure 3
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Fig. 3. Arsenate adsorption isotherms for Olivier, Sharkey, and Windsor soils after 24 h of reaction time. Solid curves depict results of curve-fitting with Freundlich Eq. [8].

 

Figure 4
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Fig. 4. Freundlich Parameters KF and b versus retention time.

 

Figure 5
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Fig. 5. Arsenate concentration in soil solution versus time during adsorption for Olivier, Sharkey, and Windsor soils. Symbols are for different initial As(V) concentrations (Co) of 20, 40, 80, 100 mg L–1. Solid curves are multireaction transport model (MRM) simulations.

 

Figure 6
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Fig. 6. Comparison of multireaction transport model (MRM) formulations M1-M8 for predicting As(V) breakthrough curves for Olivier soil (top) and Windsor soil (bottom). Model parameters were those from the batch kinetic experiment (Table 4).

 

Figure 7
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Fig. 7. Comparison of multireaction transport model (MRM) formulations M1-M8 model for predicting As(V) breakthrough curves for Olivier soil column 101. Model parameters were obtained using nonlinear inverse modeling.

 

Figure 8
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Fig. 8. Comparison of multireaction transport model (MRM) formulations M1-M8 for predicting As(V) breakthrough curves for Olivier soil column 102. Model parameters were obtained using nonlinear inverse modeling.

 

Figure 9
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Fig. 9. Comparison of multireaction transport model (MRM) formulations M1-M8 for predicting As(V) breakthrough curves for Windsor soil column 103. Model parameters were obtained using nonlinear inverse modeling.

 

Figure 10
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Fig. 10. Comparison of multireaction transport model (MRM) formulations M1-M8 for predicting As(V) breakthrough curves for Windsor soil column 104. Model parameters were obtained using nonlinear inverse modeling.

 

Figure 11
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Fig. 11. Comparison of predictions and simulations using multireaction transport model (MRM) formulation M8 for predicting As(V) breakthrough curves for Sharkey soil column 105.

 





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