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Salt Disposal of Heat-Generating Nuclear Waste

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coefficient models exist (e.g., the Davies equation, the B-dot equation, Pitzer’s<br />

equations) (Wolery 1992). The use <strong>of</strong> Pitzer’s equations to model ionic<br />

interactions is appropriate for salt repositories and has been applied at WIPP.<br />

Pitzer’s equations have been incorporated into many geochemistry, atmospheric<br />

chemistry, and chemical engineering codes. These equations and the models<br />

based on them are widely used and accepted. In geochemistry, Pitzer-based<br />

models have been incorporated into EQ3/6 (Wolery 1992, Wolery and Daveler<br />

1992, Wolery and Jarek 2003), the U.S. Geological Survey codes PHRQPITZ<br />

(Plummer et al. 1988) and its successor PHREEQC (version 2.12, see<br />

http://wwwbrr.cr.usgs.gov/projects/GWC_coupled/phreeqc), and The Geochemist’s<br />

Workbench (Bethke 1996; see also http://www.rockware.com). These<br />

are some <strong>of</strong> the better-known examples and are used by geochemists worldwide.<br />

They have been applied to a wide variety <strong>of</strong> problems in aqueous geochemistry<br />

including mineral-water interactions in many different settings, brine generation<br />

by evaporation, and deliquescence <strong>of</strong> salts. The Pitzer approach presently has<br />

widespread application in the technical community although alternative<br />

approaches such as Extended UNIQUAC (Thomsen 2005) do exist and are<br />

drawing increasing interest.<br />

The Fracture-Matrix Transport (FMT) code (Babb and Novak 1995, Babb and<br />

Novak 1997, Wang 1998) was used for modeling geochemical interactions in the<br />

WIPP repository. The geochemistry part <strong>of</strong> this s<strong>of</strong>tware uses Pitzer’s equations<br />

(Pitzer 1973, 1975, 1991) to represent the thermodynamic activity coefficients <strong>of</strong><br />

aqueous species, including both solutes and the solvent, water. The standard form<br />

<strong>of</strong> the Pitzer equations is based on molalities and requires data for interaction<br />

parameters for pairs and triplets <strong>of</strong> the solute species included in the model<br />

(interaction parameters explicitly involving the solvent, water, are not employed).<br />

The FMT model is based on the classic Pitzer model <strong>of</strong> Harvie, Møller, and<br />

Weare (1984) for the “sea-salt” system at 25°C and has been extended by adding<br />

data for organic complexants (e.g., oxalate, citrate, ethylenediaminetetraacetate<br />

[EDTA]) and actinides.<br />

The WIPP project has migrated to EQ3/6 in order to facilitate future analyses <strong>of</strong><br />

their salt repository system. The EQ3/6 package <strong>of</strong> geochemistry codes has been<br />

well tested during its widespread usage. For equilibrium analyses, the package<br />

includes the EQ3NR code, which accepts the usual kinds <strong>of</strong> inputs describing an<br />

aqueous solution, such as solute component molalities and pH. The EQ6 code<br />

allows evaluation <strong>of</strong> irreversible mass-transfer reactions among liquids, solids,<br />

and gases with relative or specific kinetic rate considerations. These <strong>of</strong>fer two<br />

options to address charge balance, calculate and fix the imbalance, or adjust one<br />

<strong>of</strong> the ionic components to achieve charge balance. Also, EQ3/6 uses the later<br />

Harvie (1981) approximation, which is the one used in essentially all modern<br />

work involving Pitzer’s equations, including the Harvie, Møller, and Weare<br />

(1984) model for the sea-salt system that forms the core <strong>of</strong> the FMT CHEMDAT<br />

database. The WIPP version <strong>of</strong> EQ3/6 is Version 8.0a. This is the version <strong>of</strong> the<br />

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