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

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P.1.1.1 Use <strong>of</strong> Solubility Data<br />

P.2<br />

Chemical weathering and alteration are most <strong>of</strong>ten the result <strong>of</strong> the interaction between<br />

an electrolyte aqueous solution and the various minerals being weathered. Several factors<br />

are important in determining the mobility <strong>of</strong> elements via weathering ionic solutions. One<br />

group <strong>of</strong> factors is related to the overall physical properties <strong>of</strong> the "weathering system,"<br />

i.e., <strong>of</strong> the hydrologic system and the host mineral assemblage. For example, the flow rate<br />

<strong>of</strong> solution through a permeable system is determined by Darcy's Law:<br />

S k u<br />

u = - (pg + VP) v -=<br />

where u = fluid flux vector (g/cm 2 /sec)<br />

S= true fluid velocity (cm/sec)<br />

= gravity force vector (cm/sec<br />

k = permeability <strong>of</strong> the rock assemblage (cm<br />

P = viscosity <strong>of</strong> the fluid (cm 2 /sec)<br />

P = density <strong>of</strong> 3 the fluid ) (g/cm<br />

P = pressure (bars)<br />

0= porosity <strong>of</strong> rock.<br />

2 )<br />

Clearly, then, the water flow depends on gravity and the pressure gradient at the given<br />

locality (a property <strong>of</strong> the hydrologic system as a whole) as well as on the porosity and<br />

permeability <strong>of</strong> the rock assemblage in the locality, and the density and viscosity <strong>of</strong> the<br />

fluid.<br />

The hydrodynamic equations, which incorporate Darcy's Law, allow us to calculate the<br />

hydrodynamic mobility <strong>of</strong> a given cation or anion in solution from its original location<br />

within a given mineral <strong>of</strong> the weathered rock to its place <strong>of</strong> deposition such as a sedimen-<br />

tary deposit, rivers, oceans or the biosphere. We can obtain absolute flux rates for a<br />

given ion (i.e., moles/cm2/sec), however; only iff we know its concentration in the percolating<br />

solution.<br />

The magnitude <strong>of</strong> the concentration <strong>of</strong> a given element in a solution that is in contact<br />

with a weathering mineral assemblage is the central element used in establishing the intrin-<br />

sic stability <strong>of</strong> a particular nuclear waste element-containing mineral to alteration and<br />

weathering. This concentration is generally a function <strong>of</strong> time, since it is kinetically<br />

controlled. Nevertheless, almost all geochemical work on the mobility <strong>of</strong> elements via solu-<br />

tions has applied a thermodynamic and not a true kinetic approach. Whether true thermodynamic<br />

equilibrium is reached between solution and a particular mineral depends, among other<br />

things, on how long they are in contact (i.e., the flow rate); this concept <strong>of</strong>ten appears<br />

as the ambiguous "water-rock ratio" in the literature. It seems likely that under most cir-<br />

cumstances the concentration <strong>of</strong> an element in a'weathering solution will be kinetically con-<br />

trolled. Unfortunately, there is a dire need for suitable kinetic data. The kinetic<br />

factors involved in the time dependence <strong>of</strong> the concentration, which may keep the concentration<br />

well below the thermodynamic limit, will be discussed below.<br />

2 )

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