Web Release Date: April 17,
Spectroscopic and Diffraction Study of Uranium Speciation in Contaminated Vadose Zone Sediments from the Hanford Site, Washington State
and


Surface and Aqueous Geochemistry Group, Department of Geological and Environmental Sciences, Stanford University, Stanford, California 94305-2115, PNC-CAT, Advanced Photon Source, Argonne National Laboratory, Argonne, Illinois 60439, Environmental Dynamics & Simulation, Pacific Northwest National Laboratory, P.O. Box 999, MS K8-96, Richland, Washington 99352, and Stanford Synchrotron Radiation Laboratory, SLAC, MS 69, 2575 Sand Hill Road, Menlo Park, California 94025
Received for review January 7, 2004
Revised manuscript received March 9, 2004
Accepted March 16, 2004
Abstract:
Contamination of vadose zone sediments under tank BX-102 at the Hanford site, Washington, resulted from the
accidental release of 7-8 metric tons of uranium dissolved
in caustic aqueous sludge in 1951. We have applied
synchrotron-based X-ray spectroscopic and diffraction
techniques to characterize the speciation of uranium in
samples of these contaminated sediments. U LIII-edge X-ray
absorption fine structure (XAFS) spectroscopic studies
demonstrate that uranium occurs predominantly as a uranium(VI) silicate from the uranophane group of minerals.
XAFS cannot distinguish between the members of this
mineral group due to the near identical local coordination
environments of uranium in these phases. However,
these phases differ crystallographically, and can be
distinguished using X-ray diffraction (XRD) methods. As
the concentration of uranium was too low for conventional
XRD to detect these phases, X-ray microdiffraction
(
XRD) was used to collect diffraction patterns on ~20
m diameter areas of localized high uranium concentration
found using microscanning X-ray fluorescence (
SXRF).
Only sodium boltwoodite, Na(UO2)(SiO3OH)·1.5H2O, was
observed; no other uranophane group minerals were present.
Sodium boltwoodite formation has effectively sequestered
uranium in these sediments under the current geochemical
and hydrologic conditions. Attempts to remediate the uranium
contamination will likely face significant difficulties
because of the speciation and distribution of uranium in
the sediments.
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