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SummaryRadionuclides, metals, and dense non-aqueous phase liquids have contaminated about six billion cubic meters of soil at Department of Energy (DOE) sites. The subsurface transport of many of these contaminants is facilitated by colloids (i.e., microscopic, waterborne particles). The first step in the transport of contaminants from their sources to off-site surface water and groundwater is migration through the vadose zone. Developing our understanding of the migration of colloids and colloid-associated contaminants through the vadose zone is critical to assessing and controlling the release of contaminants from DOE sites. In this study, we examined the mobilization, transport, and filtration (retention) of mineral colloids and colloidassociated radionuclides within unsaturated porous media. This investigation involved laboratory column experiments designed to identify properties that affect colloid mobilization and retention and pore-scale visualization experiments designed to elucidate mechanisms that govern these colloid-mass transfer processes. The experiments on colloid mobilization and retention were supplemented with experiments on radionuclide transport through porous media and on radionuclide adsorption to mineral colloids. Observations from all of these experimentsthe column and visualization experiments with colloids and the experiments with radionuclideswere used to guide the development of mathematical models appropriate for describing colloids and colloid-facilitated radionuclide transport through the vadose zone.
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Project ObjectivesOur research was guided by an Environmental Management and Science Program (EMSP) goal to improve conceptual and predictive models of contaminant movement in vadose-zone environments. As described in the report National Roadmap for Vadose-Zone Science and Technology [DOE, 2001], soil-water colloids are capable of adsorbing contaminants, such as radionuclides and metals, and facilitating their migration through the vadose zone and towards groundwater reservoirs. Our research centered on advancing understanding of this phenomenon. In particular, we combined laboratory experimentation with mathematical modeling to 1. elucidate the effects of porewater-flow transients on colloid mobilization in unsaturated porous media; 2. determine the sensitivity of colloid deposition rates to changes in porewater pH and colloid mineralogy; 3. identify mechanisms that govern mineral-colloid mobilization and deposition in unsaturated porous media; 4. develop and test mathematical models appropriate for simulating colloid mobilization, transport, and deposition under both steady-flow and transient-flow conditions; 5. quantify the effects of mineral-grain geometry and surface roughness on colloidfiltration rates; 6. evaluate the influences of colloids on the transport of strontium and cesium (i.e., DOEcontaminants-of-concern) through soils and sediments; and 7. explore the role of porous-medium heterogeneity on colloid transport.