Exploring strategies to remove contaminants from subsurface plumes: iron-bearing materials and calcite

At the Hanford site in eastern Washington, depending on the particular waste site, radionuclide (Tc99/I129) laden liquid waste was not of a sufficient volume to carry the contamination through the vadose zone to the groundwater. Contaminants are therefore retained in the vadose zone, which represents a continuous source of these contaminants to groundwater through flux created by precipitation recharge. Deployment of treatment technologies in the vadose zone that will intercept flow from vadose zone recharge and sequester contaminants is needed for future groundwater protection. In this study, first we tested zero valent iron (ZVI) and sulfur modified iron (SMI) to determine the feasibility of using these materials to intercept Tc migrating from the vadose zone into the groundwater. Secondly, this study focused on testing the ZVI and SMI in conjunction with several potential amendments needed for capture of additional contaminants present (e.g., IO3) to immobilize contaminants both individually and combined. Previous testing has shown removal of IO3 by incorporation into calcite; these experiments test the effect of ZVI/SMI on the efficiency of the removal of IO3 by calcite and vice versa. Preliminary results have shown strong removal of high Tc concentrations (i.e., 22 ppm or 44 ppm) at solid to solution ratios of 1 g to 100 mL, but when the solid and the Tc concentration was scaled down to more field relevant conditions (i.e., 0.42 ppm), the Tc removal was slower and the amount of Tc removed (per gram of Fe solid) was decreased. In some tests, results indicated that there is no interference from IO3 on Tc removal, but presence of ZVI/SMI has a negative impact on the removal of IO3 by calcite incorporation, likely due to the fast reduction of iodate to iodide by the ZVI/SMI (iodide is usually not incorporated into calcite).