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

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P.3<br />

One can usually establish only an upper limit to the concentration <strong>of</strong> a given element<br />

by the use <strong>of</strong> thermodynamics. Assuming equilibrium between minerals and solution, the con-<br />

centration <strong>of</strong> any particular nuclear waste element will then be governed by the solubility<br />

<strong>of</strong> the minerals containing it.<br />

Before discussing the thermodynamic approach to stability, a brief review <strong>of</strong> the gen-<br />

eral qualitative work on weathering stability in the literature is presented. Soil geochem-<br />

ists have set up a qualitative scale <strong>of</strong> the different inherent tendencies <strong>of</strong> minerals to<br />

alter by weathering processes. The weathering rate depends on the structure and composition<br />

<strong>of</strong> the minerals, as well as the weathering environment. Goldich (1938) formulated such a<br />

weathering stability series for the major elements. He found that the major elements are<br />

removed from rocks and minerals in the order:<br />

+2 + ++ +<br />

Ca > Na > Mg > K > SiO 2 > Fe203 > Al 20 3.<br />

Loughnan (1969) gives a similar result (see Table P.1.1).<br />

Much less is known about the relative mobilities <strong>of</strong> the trace elements (lanthanides,<br />

actinides, and others). Jackson and his colleagues (Jackson et al. 1948, 1952, Jackson and<br />

Sherman 1953) set up a weathering sequence <strong>of</strong> clay-size minerals in soils and sedimentary<br />

deposits (see Table P.1.2). Pettijohn (1941) compared the frequency <strong>of</strong> occurrence <strong>of</strong> each<br />

species in recent and older sediments and established an order <strong>of</strong> persistence, which is in<br />

agreement with the Goldich series (see Table P.1.3).<br />

TABLE P.1.1 Mobilities <strong>of</strong> the Common Cations<br />

t 1. Ca++, Mg+, Na+--readily lost under leaching conditions.<br />

~ 2. K --readily lost under leaching conditions but rate may be retarded through<br />

o Es fixation in the illite structure.<br />

S£ 3. Fe++--rate <strong>of</strong> loss dependent on the redox potential and degree <strong>of</strong> leaching.<br />

>." 4+<br />

a 4. Si --slowly lost under leaching conditions.<br />

0 G 5. Ti4--may show limited mobility if released from the parent mineral as<br />

i35 Ti(OH) 4 ; if TiO2 forms, immobile.<br />

Ub 6. Fe 3 --immobile under oxidizing conditions.<br />

S4- 7. A3+--immobile in the pH range <strong>of</strong> 4.9 to 9.5.<br />

Although still poorly understood, structure must play an important part in the accessi-<br />

bility <strong>of</strong> waters to the soluble cations. Thus, orthosilicates, e.g., olivine, weather much<br />

faster than framework silicates, e.g., feldspars and quartz. However, zircon, also an<br />

orthosilicate, is highly resistant to weathering, which indicates that resistance to weath-<br />

ering cannot be based solely on such a simple structural division <strong>of</strong> the silicates.<br />

The qualitative lists <strong>of</strong> minerals in Tables P.1.2 and P.1.3 should be quantitatively<br />

understood in terms <strong>of</strong> both thermodynamics (i.e., solubility data) and kinetics (i.e.,<br />

leaching rates). The solubility and hence the thermodynamic stability <strong>of</strong> a particular

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