GSA Annual Meeting in Denver, Colorado, USA - 2016

Paper No. 131-8
Presentation Time: 3:25 PM

ACTINIDE SORPTION IN A DOLOMITE ROCK SYSTEM: EVALUATING THE DEGREE OF CONSERVATISM IN KD RANGES USED IN PERFORMANCE ASSESSMENT MODELS


DITTRICH, Timothy M., Earth and Environmental Sciences Division, Los Alamos National Laboratory, 1400 University Dr., Carlsbad, NM 88220, DUGAS, Michael P., Actinide Chemistry and Repository Science Program, Los Alamos National Laboratory, 1400 University Dr., Carlsbad, NM 88220 and REED, Donald T., Earth and Environmenal Sciences Division, Los Alamos National Laboratory, 1400 University Drive, Carlsbad, NM 88220, timothy.dittrich@colorado.edu

The Waste Isolation Pilot Plant (WIPP) near Carlsbad, NM has been accepting transuranic (TRU) waste since 1999 and is the only operating nuclear waste repository in the US. The WIPP is located in a salt deposit approximately 650 m below the surface overlain by multiple layers of dolomite and other geologic material. Performance assessment (PA) modeling for a 10,000 year period is required to recertify the operating license with the US EPA every five years. Human intrusion caused by drilling operations is the main pathway of concern for environmental release of radioactive material. We are evaluating the degree of conservatism in the estimated sorption partition coefficients (Kds) based on a complementary batch and column method (Dittrich and Reimus, 2016, 2015; Dittrich et al., 2015). The main focus of this work is to investigate the role of ionic strength, solution chemistry, and oxidation state (III-VI) in actinide sorption to dolomite rock. Based on redox conditions and solution chemistry expected at the WIPP, possible actinide species include Pu(III), Pu(IV), U(IV), U(VI), Np(IV), Np(V), Am(III), and Th(IV). We will present (1) a conceptual overview of Kd use in the PA model, (2) background and evolution of the Kd ranges used, and (3) results from batch and column experiments and model predictions for Kds with WIPP geologic media. We will also briefly discuss the challenges of upscaling from lab experiments to field scale predictions, the presence of ligands (e.g., acetate, citrate, EDTA), the role of colloids and microbes, and the effect of engineered barrier materials (e.g., MgO) on sorption and transport conditions.

References:

Dittrich, T.M., Reimus, P.W. 2016. Reactive transport of uranium in fractured crystalline rock: Upscaling in time and distance. J Environ Manage 165, 124-132

Dittrich, T.M., Reimus, P.W. 2015. Uranium transport in a crushed granodiorite: experiments and reactive transport modeling. J Contam Hydrol 175-176: 44-59.

Dittrich, T.M., Boukhalfa, H., Ware, S.D., Reimus, P.W. 2015. Laboratory investigation of the role of desorption kinetics on americium transport associated with bentonite colloids. J Environ Radioactiv 148: 170-182.