The long term corrosion rate of nuclear waste glass in a repository might b
e controlled by the steady-state diffusion of dissolved silica and would be
enhanced by the sorption of silica onto clay minerals. Irreversible sorpti
on and moderate retardation have been observed for dissolved silica in Boom
Clay. Values of eta/R between 10 and 20 have been determined by means of f
our Flow-Through migration experiments, while K-d in the range 20 to 100 cm
(3).g(-1) have been measured by batch sorption tests with Si-32 on fresh an
d slightly oxidized Boom Clay. As non specific interactions cannot explain
the sorption of neutral Si(OH)(4), or of negative silicate species (Donnan
exclusion), onto negatively charged clay minerals other mechanisms must be
invoked: i.a., the chemisorption of dissolved silica Si(OH)(4) onto specifi
c Lewis acid sites (Al3+, Fe3+) present at the clay surface. The suggested
mechanism could be similar to this explaining the irreversible chemisorptio
n of oxy-anions of weak acids (as phosphate, or berate) onto aluminum and i
ron hydroxides in soils. Ligand exchange of aqueous silica with a hydroxyl
group of Al(OH)(3) may form a hydroxy-aluminosilicate (HAS) surface complex
. Gibbsite layers accessible on the basal plane of kaolinite and on the edg
es of illite and smectite are possible sorption sites for the dissolved sil
ica in Boom Clay. Moreover, hydrous ferric oxide produced by pyrite oxidati
on significantly increases the extent of silica sorption.