Answers are grounded in this paper and cite their sources.
Demonstrates iodine species adsorption in alkali-activated slag cement, highlighting its implications for radioactive waste management.
Alkali-activated slag cement (AAS) is a sustainable and promising matrix for immobilizing radioactive wastes. Strätlingite (siliceous AFm-type phase), a typical hydration product in AAS, plays a crucial role in stabilizing anionic species. However, the immobilization mechanisms of iodine species within strätlingite remain unclear. In this study, strätlingite demonstrated a greater affinity for IO₃⁻ than I⁻, with adsorption capacities of 0.291 and 0.0016 mmol/g, respectively. Approximate site energy distribution revealed a more diverse energy partitioning of adsorption sites for IO₃⁻ than I⁻, and strong interactions between IO₃⁻ and Ca sites through O-Ca bonds forming. Conversely, the differential charge density between I⁻ and Ca sites was weak. The surface adsorption energy of IO₃⁻ to Ca sites was -5.05 eV, substantially higher than the -1.08 eV for I⁻ adsorption. A stronger overlap between the 2p orbitals of O atoms and the 3d orbitals of Ca was observed upon IO₃⁻ adsorption than I⁻ adsorption. Moreover, the anion selectivity of strätlingite followed the order: CO₃²⁻ > SO₄²⁻ ≥ IO₃⁻ > OH⁻ > Cl⁻ > NO₃⁻ ≥ I⁻. These findings provide valuable insights into the migration behavior of iodine species in repositories and alkaline environments.
No takes yet. Share an insight, caveat, or question.
Guo et al. (2026) studied this question.
Synapse has enriched 10 related papers. Consider them for comparative context: