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Euradwaste '08 - EU Bookshop - Europa

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Figure 4: SEM image of the alteration zone from a cement-bentonite diffusion experiment showing<br />

the presence of brucite and tri-octahedral Mg-smectite [6].<br />

4.3 Saline groundwaters<br />

The interaction of waters of different salinities with MX-80 bentonite has minor effects on the mineralogical<br />

composition of bentonite [8], with only minor amounts of montmorillonite being dissolved<br />

leading to the precipitation of pyrophyllite. However, the most relevant changes occur in the<br />

octahedral layer of smectite, where Mg is replaced by Al. This replacement has two effects: 1) a<br />

decrease of the interlayer charge; and 2) an increase in Mg in solution leads to the replacement of<br />

Na by Mg in the interlayer space. The swelling pressure of bentonite is expected to depend on the<br />

ionic strength of pore water, as already identified by the results of other experiments prior to NF-<br />

PRO. This was also recognised in NF-PRO, where experiments conducted with MX-80 bentonite<br />

showed that swelling pressure decreases as ionic strength increases [8]. Moreover, a clear correlation<br />

exists between interlayer charge and swelling pressure. In pure water, swelling pressure increases<br />

with increasing interlayer charge, whereas in low salinity solutions, swelling pressure decreases<br />

with interlayer charge (water uptake capacity is lower for multivalent cations than for Na).<br />

Finally, in high salinity solutions, swelling pressure is subject to an initial increase, and then a decrease.<br />

This different behaviour depends upon specific mineralogical transformations.<br />

5. Radionuclide Transport<br />

An experimental programme was designed in order to contribute to an improved understanding of<br />

the basic processes underlying diffusion/retention of charged and uncharged radionuclides in compacted<br />

bentonite. This programme included studies on pure clay minerals (montmorillonite, illite,<br />

kaolinite) and bentonite in both dispersed and compacted form. From the behaviour of the radionuclides<br />

in the pure clay systems, the behaviour in the complex systems was evaluated (‘bottom-up<br />

approach’).<br />

189

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