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Published online 12 March 2007
Published in Soil Sci Soc Am J 71:306-313 (2007)
DOI: 10.2136/sssaj2005.0370
© 2007 Soil Science Society of America
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Effect of Transient Irrigation on Boron Transport in Soils

G. Communar and R. Keren*

Institute of Soil, Water and Environmental, Sciences, The Volcani Center, Agricultural Research Organization, P.O. Box 6, Bet Dagan 50250, Israel


Figure 1
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Fig. 1. Hydraulic properties of the loamy sand and sandy loam soils used in the simulations. Parameters of the hydraulic functions {theta} = {theta}(h) and K = K(h) are given in Table 2; {theta} = volumetric water content, K = hydraulic conductivity, and h = soil water pressure.

 

Figure 2
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Fig. 2. Boron adsorption isotherms for the loamy sand and sandy loam soils used in this study. The lines were calculated with Eq. [5], using the adsorption coefficients bm and k from Table 2.

 

Figure 3
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Fig. 3. Measured and simulated breakthrough curves for B transport in the loamy sand and sandy loam soils at pore-water velocity, u, of 0.25 and 2.5 cm h–1. Solid lines were obtained with the nonequilibrium (NE) model, using the adsorption and transport parameters from Table 2. The rate coefficient values in Table 2 were obtained by fitting the NE model to the high-velocity data.

 

Figure 4
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Fig. 4. Cyclic changes of water flux at the soil surface and variation of water flux with time at various depths z in the loamy sand and sandy loam soils.

 

Figure 5
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Fig. 5. Variations of water content {theta} and water pressure h with time at various depths z for the loamy sand and sandy loam soils.

 

Figure 6
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Fig. 6. Relative Br concentration vs. time at various depths for the loamy sand and sandy loam soils. The simulations with the nonequilibrium (NE) model were performed with a rate coefficent ({gamma}) = 0.

 

Figure 7
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Fig. 7. Relative B concentration vs. time at various depths in loamy sand soil and sandy loam soils, calculated for various values of the rate coefficient, {gamma}, and local equilibrium (LE). Calculations were based on the parameters of Table 2 and the input B concentration of 2.5 mg L–1 in the irrigation water.

 





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