SUMMARYAssessing long-term performance of Category 3 waste cement grouts for radionuclide encasement requires knowledge of the radionuclide-cement interactions and mechanisms of retention (i.e. sorption or precipitation). This understanding will enable accurate prediction of radionuclide fate when the waste forms come in contact with groundwater. A set of diffusion experiments using carbonated and non-carbonated concrete-soil half cells was conducted under unsaturated conditions (4% and 7% by wt moisture content). Spiked concrete half-cell specimens were prepared with and without colloidal metallic iron addition and were carbonated using supercritical carbon dioxide. Spikes of I and Re were added to achieve measurable diffusion profile in the soil part of the half-cell. In addition, properties of concrete materials likely to influence radionuclide migration such as carbonation were evaluated in an effort to correlate these properties with the release of iodine and rhenium.The behavior of rhenium and iodine release was comparable within a given half-cell test. The release of iodine and rhenium at 4% moisture content initiated with an initial concentration spike in the sediment immediately contacting the concrete monolith. The concentration profile rapidly decreased to zero within the first 5 cm of the sediment profile. Normalized concentration profiles for iodine and rhenium in sediments at 7% moisture content were asymmetrical increasing over the first 1 to 4 cm from the interface, reaching maximum concentrations 2 -5 cm from the interface, and decreasing asymptotically thereafter. The apparent release profile for sediments at 7% moisture content may be the result of i) limited diffusion within the concrete monolith which depletes the concentration source, or ii) compaction of the sediment half-cell resulting in separation from the concrete monolith, both of which effectively "cuts off" the source. Because of the method by which the sediment was sampled, it is unknown whether or not the later occurred. However, future efforts to quantify of the concentration profile within the concrete monoliths will aid in further understanding the release profiles. Comparing the release profiles at 4% and 7% moisture content suggests the rate of diffusion increases with increasing moisture content. However, because the source term was "cut-off" from the migrating contaminant at the higher moisture content the rate of diffusion was not sustained throughout the duration of testing.Diffusivity values for iodide in soil ranged from 8.66 x 10 -8 to 1.65 x 10 -7 cm 2 /s, and from 9.70 x 10 -8 to 5.75 x 10 -8 cm 2 /s for rhenium at 4% moisture content. At 7% moisture content diffusivity values for iodide ranged from 9.793 x 10 -7 to 1.52 x 10 -6 cm 2 /s, and from 8.43 x 10 -7 to 1.23 x 10 -6 cm 2 /s for rhenium. This indicates that unsaturated conditions a 3% increase in moisture content affords a one to two order of magnitude increase in diffusivity. The concrete diffusivity of iodide and rhenium ranged from 7.95 x 10 -14 to 1.20 x ...