The
radionuclide selenium-79 (Se-79) is predicted to be a key contributor
to the long-term radiologic hazards associated with geological high-level
waste (HLW) repositories; hence its release is of pertinent concern
in the safety assessment of repositories. However, interactions of
reduced Se species with aqueous Fe(II) species and solid phases arising
from the corrosion of a steel overpack could play a role in mitigating
its migration to the surrounding environment. In this study, we examined
the immobilization mechanisms of Se(−II) during its interaction
with aqueous Fe(II) and freshly precipitated Fe(OH)2 at
circumneutral and alkaline conditions, respectively, its response
to changes in pH, and its behavior during aging at 90 °C. Using
microscopic and spectroscopic techniques, we observed β-FeSe
precipitation, regardless of whether Se(−II) reacts with aqueous
species or solid phases, and that modifying the pH following initial
immobilization did not remobilize Se(−II). These observations
indicate that Se(−II) migration beyond the overpack can be
effectively and rapidly retarded via interactions with Fe(II) species
arising from overpack corrosion. Thermodynamic calculations, however,
showed that iron selenides became metastable at alkaline conditions
and will dissolve in the long term. Aging experiments at 90 °C
showed that Se(−II) can be completely retained via the crystallization
of ferroselite at circumneutral conditions, while it will be largely
remobilized at alkaline conditions. Our results show that Se(−II)
mobility can be significantly influenced by its interactions with
the corrosion products of the steel overpack and that these behaviors
will have to be considered in repository safety assessments.