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

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P.1<br />

APPENDIX P<br />

MINERALS THAT COULD BE USED TO CONTAIN RADIONUCLIDES<br />

This appendix presents a review <strong>of</strong> minerals that are candidates for the isolation <strong>of</strong><br />

radionuclides in synthetic minerals, as discussed in Section 4.3.2.3. Analyses <strong>of</strong> the<br />

potential hazard from certain HLLW radionuclides suggest the greatest effort in solidifica-<br />

tion into synthetic minerals would be placed on the following groups <strong>of</strong>. elements:<br />

* Actinides and Lanthanides. The actinides Np, Pu, Am, Cm and their daughters constitute<br />

the major hazard in nuclear wastes from about 1000 to 5000 years <strong>of</strong> storage, with the<br />

exception <strong>of</strong> 2 26 Ra, which does not become significant until about 105 years<br />

(Cohen 1977). The majority <strong>of</strong> the lanthanide elements (La, Ce, Pr, Nd, Pm, Sm, Eu,<br />

Gd, Tb, Dy, Ho) are present as stable isotopes after a few years, and only trace<br />

amounts <strong>of</strong> a few Sm and Eu radionuclides have long half-lives. However, the<br />

lanthanides could be included with the actinides for several reasons: they occur<br />

together at one stage <strong>of</strong> partitioning; lanthanides and actinides are<br />

crystallographically and chemically very<br />

similar and usually occur together in the same minerals; the lanthanides can act as<br />

diluents in synthetic minerals for a-emitting actinides in order to minimize radiation<br />

effects.<br />

* Strontium and cesium. These elements constitute both the major heat producers and bio-<br />

hazards in nuclear wastes for the first 600 years or so (Cohen 1977).<br />

* Techetium and iodine. These two fission products have long-lived isotopes ( 9 Tc, tl/2<br />

= 2.1 x 105 y; 129I, t/2 = 1.7 x 107 y) and are biohazards. They have the additional<br />

characteristics <strong>of</strong> forming anions that can migrate in soils and rocks as fast as the<br />

solutions in which they are dissolved (Rai and Seine 1978), i.e., without any substan-<br />

tial hold-up due to ion exchange or adsorption.<br />

The minerals reviewed here are either known to contain substantial amounts <strong>of</strong> these<br />

elements or are likely to accept these elements based on compatible crystal chemistry. The<br />

physico-chemical and crystal chemical criteria for selecting host minerals, along with the<br />

common mineral synthesis methods, are discussed and tables <strong>of</strong> candidates are presented. A<br />

thorough treatment <strong>of</strong> what is known about the process <strong>of</strong> metamictization and metamict min-<br />

erals is also included.<br />

P.1 PHYSICO-CHEMICAL PRINCIPLES<br />

P.1.1 Stability Criteria<br />

The physical and chemical foundations used to define whether a known mineral is classi-<br />

fied as very stable, relatively unstable, or very unstable with respect to alteration,<br />

weathering and diagenesis include solubility and geologic data.

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