The cement components in deep geological disposal facilities (DGFs) for spent nuclear fuel can increase groundwater pH, potentially altering minerals within natural barriers. Mineral (biotite, quartz, plagioclase, chlorite, and K-feldspar) dissolution and secondary-phase precipitation were investigated to provide visually integrated understanding of multifaceted processes. This study was based on the morphological features of granitic rock thin sections exposed to alkaline aqueous solutions (initial pH: pHo 9 and 13) using atomic force microscopy (AFM), micro-X-ray fluorescence, and scanning electron microscopy/energy-dispersive X-ray spectroscopy. Batch kinetic-alteration tests were conducted from 4 h to 20 d. The minerals exhibited more pronounced changes in surface roughness and Si release at pHo 13 than at pHo 9. Furthermore, precipitates were more abundant on the mineral surfaces at pHo 9 than at pHo 13. Fe (oxy)hydroxides and Al (oxy)hydroxides prevailed as precipitates at pHo 9, whereas Ca (oxy)hydroxides dominated at pHo 13 (pH ≥ 12.8). These findings indicate that the aqueous solutions were significantly involved in the formation of the secondary-phase precipitates. Interestingly, secondary-phase precipitates formed not only on the surface of mineral (i.e., biotite) providing constituent ions but also on the surfaces of adjacent minerals (i.e., quartz and plagioclase). Moreover, the possibility of a multistep process involving Al precursors for nucleation of gibbsite precipitates on the surface of K-feldspar at pHo 9 and colloidal particle formation through surface modification, often overlooked in mineral research, were identified via AFM image analysis. This methodological approach using rock thin sections can provide new visual insights regarding the dissolution–precipitation processes, including nucleation reactions, under conditions closely resembling the expected environmental settings within DGFs.
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