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Management of Commercially Generated Radioactive Waste - U.S. ...

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P.12<br />

as a waste element fixation mechanism, because the mineral's stability may be better con-<br />

trolled by the host composition. In other words, the waste ion would be sufficiently dilute<br />

in the host structure that it does not substantially modify the stability <strong>of</strong> that host.<br />

Isostructural Compounds<br />

Crystals that allow solid solution necessarily have the same crystal structure for the<br />

end memers. Compounds with the same structure may show no or very limited solid solu-<br />

biflty, usually because <strong>of</strong> marked size differences <strong>of</strong> the ions involved. Sih isostructural<br />

groups may have similar stability properties. Thus it may be useful to identify families<br />

<strong>of</strong> compounds with certain structural properties that may predict the existence <strong>of</strong> a stable<br />

compound <strong>of</strong> a particular waste element. Calcium compounds, for example, may indicate possible<br />

strontium compounds. Bromides and chloride compounds may indicate possible iodide<br />

compounds. Several isostructural possiblities are identified below.<br />

P.1.4 Synthesis<br />

Preparation <strong>of</strong> synthetic minerals requires that the desired elements from the waste<br />

streams be mixed with other materials. The mixture is then reacted to form the synthetic<br />

mineral. Considered here are the problems that may arise in the processing <strong>of</strong> nuclear<br />

wastes into synthetic minerals.<br />

The purity <strong>of</strong> the partitioned waste stream will determine whether side reactions will<br />

lead to additional phases in the synthetic mineral assemblage. The controlling factors will<br />

be the ionic size and the ionic charge <strong>of</strong> the additional cations present. Ions whose size<br />

and charge are similar to those <strong>of</strong> the element being packaged will dissolve into the synthetic<br />

mineral as a minor solid solution. Many <strong>of</strong> the mineral phases are very "forgiving";<br />

that is, they will accept many elements into solid solution at least in small amounts. If<br />

there is a large size or charge mismatch, the impurity elements in the waste stream will<br />

react to form secondary minerals <strong>of</strong> their own. Whether this is detrimental to the proces-<br />

sing will have to be evaluated in individual cases.<br />

Three general methods <strong>of</strong> reaction are in common use among geochemists for the synthesis<br />

<strong>of</strong> minerals: calcination, solid state reaction, and hydrothermal reaction. In each method,<br />

it is necessary to mix the waste elements with the other components in the right proportions<br />

to form the minerals. Many minerals are nearly stoichiometric, that is the components must<br />

be mixed in exactly the proportions called for in the mineral formula. If this is not done,<br />

some components will be left over to form additional phases. The stoichiometry <strong>of</strong> minerals<br />

that form solid solutions is not quite so critical.<br />

Mineral synthesis by calcination involves these steps:<br />

* taking each component into solution (for example, as the nitrates)<br />

* mixing the solutions in correct proportions using volumetric methods<br />

* precipitating the solution as a gel, spray drying, or by another method forming a<br />

calcine (a highly reactive fine-grained, <strong>of</strong>ten poorly-crystallized powder)

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