Journal of Environmental Quality · 1988 · 25 citations · 0 references
AgricultureEarth SciencesSoil SciencesSoil BiogeochemistrySoil ChemistrySoil ScienceNutrient LeachingNutrient Retention In SoilsSoil GeochemistryTrace Element ChemistryBreakthrough CurvesContaminant Breakthrough CurvesFlow In Soil ColumnsMineral Ion TransportSoil Bulk DensitySoil Matrix EffectsSoil Mineral - Solution InteractionsSolute Transport In Soils
Abstract Transport of selenate (Se 6+ ) in steady‐state, water‐saturated soil columns was evaluated under different pore water velocities, ionic compositions, and two soil bulk densities. The soil was Panoche loam (Typic Torriorthents) saturated with 0.005 M CaSO 4 , 0.005 M CaCl 2 , or 0.05 M CaCl 2 . To examine the movement of selenate in soil relative to water and SO 2− 4 (a biogeochemically similar anion), breakthrough curves of 75 SeO 2− 4 , along witH +3 H 2 O or 35 SO 2− 4 , were observed. Selenate appeared before elution of one pore volume and always ahead of the 3 H 2 O and SO 2− 4 except in 0.05 M CaCl 2 , indicating exclusion of selenate by the soil matrix. On the other hand, soil analysis of selenate following the leaching indicated that selenate was retained by the soil, suggesting simultaneous exclusion and adsorption of selenate. Increasing pore water velocity and soil bulk density did not shift the position of the breakthrough curves significantly. Assuming equilibrium linear adsorption‐desorption of selenate by soil, the values of the apparent diffusion coefficient ( D ) and the retardation factor ( R ) were obtained by fitting the solution of the solute transport equation without sink and source terms to the measured breakthrough curves of selenate. The values of D showed an increasing trend with pore water velocity and the values of R were influenced by ionic composition of the soil solution.