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Determination of liquid-solid partition coefficients (Kd) of radionuclide anionic species from a contaminated aquifer

Published online by Cambridge University Press:  21 March 2011

François Carona
Affiliation:
Current address: Dept. of Chemistry & Biochemistry, Laurentian University, Sudbury, ON, Canada, P3E 2C6;
Michael K. Haas
Affiliation:
Atomic Energy of Canada Limited, Environmental Technologies Branch, Chalk River, ON, Canada, K0J 1J0;
Edward L. Cooper
Affiliation:
Atomic Energy of Canada Limited, Environmental Technologies Branch, Chalk River, ON, Canada, K0J 1J0;
David E. Robertson
Affiliation:
Pacific Northwest National Laboratories, Richland, WA;
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Abstract

Contaminated groundwater from a former liquid waste discharge area at the Chalk River Laboratories was treated with ion exchange resins to isolate aqueous extracts of selected radionuclides (60Co, 106Ru, 137Cs, 238Pu, 239/240Pu, 241Am and 244Cm). The extracts were then mixed with native uncontaminated soil material to determine their liquid-solid partitioning coefficients (Kd). Separate Kd values of the same elements were also obtained with the usual short-term “batch” technique for comparison, but using different radioisotopes as tracers (57Co and 134Cs), spiked to the extracts. The comparison included separate Kd determinations with 239/240Pu and 241Am as tracers, added to uncontaminated groundwater.

In all cases, the radionuclides originally present in the contaminated groundwater extracts exhibited low Kd values, compared to the values obtained in the “batch” method with tracers (57Co, 134Cs, 239/240Pu and 241Am). The difference was up to two orders of magnitude. This was attributed to differences in aqueous speciation of the nuclides in the contaminated groundwater, allowing limited interactions of complexed radionuclide species with soil material. Our results indicated that all the radionuclides were predominantly in anionic form in the groundwater, whereas in the tracer “batch” experiment, 57Co and 134Cs were predominantly cationic, Pu and Am were predominantly anionic. Hydrolysis partially explains the dominant anionic character of Am and Pu in the tracer experiments, however dissolved organics are suspected to dominate the speciation of the radionuclides in contaminated groundwater. Our experiment implies that in some cases, if Kd values obtained using the “batch” method with tracers are used in transport models, radionuclide transport could be underestimated.

Type
Research Article
Copyright
Copyright © Materials Research Society 2002

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