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RD&D-Programme 2004 - SKB

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those of montmorillonite and mica. Potassium ions are, for example, bound to some extent in an<br />

illite clay, but not sodium or calcium ions. Binding of multivalent ions, usually iron or magnesium,<br />

can also take place via a bridge of hydroxide, which gives a chlorite mineral.<br />

Thus, in order for a montmorillonite to be transformed towards illite or chlorite, there must be<br />

an increase in the layer charge, which can be brought about by:<br />

• release of silicon,<br />

• exchange of aluminium,<br />

• change of valence in the structure (iron).<br />

In the event of a transformation, secondary processes may be of importance for the performance<br />

of the buffer. Release of silicon would probably lead to precipitations of different silicon<br />

minerals, which can affect the rheological properties of the buffer (cementation).<br />

Conclusions in RD&D 2001 and its review<br />

Kasam considers that it would be valuable if <strong>SKB</strong>, in connection with its studies of other<br />

compositions, also investigated how a limited illitization and cementation affects parameters<br />

of importance for the buffer.<br />

In SKI’s opinion, the mineral transformations should be studied in the laboratory, and<br />

cementation during the unsaturated phase is an important process.<br />

Newfound knowledge since RD&D 2001<br />

Extensive laboratory experiments have been conducted to study the stability of the buffer at<br />

very high pHs in the groundwater. The investigation was a part of the EU project Ecoclay,<br />

whose purpose was to shed light on the effects of cement use in a final repository. The results<br />

show that the montmorillonite is greatly affected by cement pore water from fresh Portland<br />

cement, i.e. at pHs between 13 and 14. A heavy release of silicon was measured, causing an<br />

increase in the layer charge and a loss of density in the bulk material. At lower pHs, the results<br />

showed a significant difference between highly compacted bentonite and bentonite dispersed in<br />

solution. A preliminary interpretation is that a favourable ion equilibrium is established between<br />

highly compacted bentonite and the pH solution, see section 17.2.15.<br />

<strong>Programme</strong><br />

The results of the Ecoclay project are in the process of being evaluated and published. The<br />

results are judged to be very valuable. Further modelling and verification tests will probably be<br />

carried out.<br />

Laboratory tests with natural materials of lower quality than commercial bentonites are planned.<br />

The investigations involve mineralogical description and determination of physical properties of<br />

e.g. natural materials with different degrees of transformation, for example potassium bentonite<br />

from Röstånga, Skåne.<br />

<strong>SKB</strong> plans to study changes in the buffer properties as a result of reactions with iron in<br />

bentonite with regard to two aspects:<br />

• Valence change in the octahedral layer in the mineral structure will be studied by means<br />

of diffusion tests with reducing and oxidizing solutions.<br />

• Binding of iron as a charge-compensating counterion and/or as a central ion for a<br />

hydroxide bridge between the mineral layers; this may lead to an increased corrosion<br />

rate of surrounding iron.<br />

RD&D-<strong>Programme</strong> <strong>2004</strong> 219

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