2009
DOI: 10.1016/j.jhydrol.2009.07.048
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Modeling the influence of an artificial macropore in sandy columns on flow and solute transfer

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Cited by 49 publications
(42 citation statements)
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“…An understanding of pollutant transfer focuses on how water infiltrates—similarly through all pores or preferentially through certain pores. Flow patterns may exert considerable impact on the transfer of nonreactive solutes (Lamy et al, 2009), and maybe even more so for the transfer of reactive solutes (Lassabatere et al, 2004, 2007). Further studies will focus on characterizing BOF slag hydrodispersive parameters (i.e., parameters related to solute transport via water), along with chemical reactions in water and the related pollutant release by BOF slag (Deneele et al, 2008; Legret et al, 2008; Chaurand et al, 2007).…”
Section: Discussionmentioning
confidence: 99%
“…An understanding of pollutant transfer focuses on how water infiltrates—similarly through all pores or preferentially through certain pores. Flow patterns may exert considerable impact on the transfer of nonreactive solutes (Lamy et al, 2009), and maybe even more so for the transfer of reactive solutes (Lassabatere et al, 2004, 2007). Further studies will focus on characterizing BOF slag hydrodispersive parameters (i.e., parameters related to solute transport via water), along with chemical reactions in water and the related pollutant release by BOF slag (Deneele et al, 2008; Legret et al, 2008; Chaurand et al, 2007).…”
Section: Discussionmentioning
confidence: 99%
“…However, hydraulic performance may not be the sole criterion to be investigated, and considerable care must also be taken regarding the transfer of pollutants carried by infiltrating water (Mikkelsen et al, 1994;Legret and Pagotto, 1999). In addition, the modification of flow may exert considerable impact on the transfer of both nonreactive solutes (Lamy et al, 2009) and reactive solutes (Lassabatere et al, 2004;Lassabatere et al, 2007). Regarding pollutant transfers, decreasing flow velocities may be useful for their retention.…”
Section: Discussionmentioning
confidence: 99%
“…For the solute transport simulation, we assumed that solute transport is governed by the advection–dispersion equation: θCwt=·[θuCw+θDCw]where C w is solute concentration in the water phase [M L −3 ], u is the pore water velocity vector [L T −1 ], and D is the local‐scale dispersion coefficient tensor (L 2 T −1 ), usually defined as D=(αnormalT|boldu|+Dm,eff)I+(αnormalLαnormalT)uboldunormalT|u|where ‖ u ‖ = √( uu T ) is the Euclidean norm of the pore water velocity vector, α L and α T are the longitudinal and transverse dispersivities, respectively, D m,eff is the effective molecular diffusion coefficient, and I is the identity matrix. We set α L to the mean grain size and α T to 1/10 of α L , which are typical values reported for saturated unconsolidated homogenous porous media (e.g., (Greiner et al, 1997; Yoon et al, 2008; Lamy et al, 2009)). The diffusion coefficient D m of Gd‐DTPA 2− in water at 25°C was assumed to be 0.4 × 10 −9 m 2 s −1 (Osuga and Han, 2004) and was multiplied by the tortuosity factor evaluated as a function of water content using the relationship of Millington and Quirk (1961) to obtain D m,eff…”
Section: Methodsmentioning
confidence: 99%