Abstract

Bentonite is used as part of engineered barrier in the geological disposal of high-level nuclear waste (HLW) from nuclear plants. Fe(II)-montmorillonite, Fe(II)-Mt, is a potential altered clay in such a system due to clay mineral interaction with the carbon steel (overpack material) under reducing water chemistry conditions. To understand the long-term integrity of the HLW, the basic studies on Fe(II)-Mt are needed. In this study, we have focused on the synthesis of homoionic Fe(II)-Mt by using weak ferrous complexe for cation-exchange with Na-Mt. We prepared Fe(II)-salicylate by dissolving Fe0 in salicylic acid at 80°C under N2 atmosphere. Dissolution rate constants are in the range of 0.8–1.6×10−3min−1. A colorless Fe(II)-L, was reasonably stable in the inert atmosphere, but was rapidly oxidized in air to a red colored Fe(III)-L (λmax 475nm). The solution redox potential and UV–Vis absorption spectra of these complexes are recorded here. Na-Mt was subjected for ion-exchange reaction with Fe(II)-L to form Fe(II)-Mt. The formation of Fe(II)-Mt was confirmed from the interlayer Fe2+ ions released by interacting with 0.5M H2SO4. The cumulative amount of Fe2+ ions are equivalent to CEC of 1.10meq/g and Fe2+/Fetotal≈1. The X-ray diffraction patterns (d001) and infrared spectra also support the formation of Fe(II)-Mt. The cation exchange achieved here was possible through dissociation of Fe(II)-L owing to its intermediate stability constant (log K=6.55), unlike the Fe(III)-L (log K=16.35). We believe the present method is one of the best approaches for obtaining homoionic Fe(II)-Mt.

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