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a Dep. of Geological and Environmental Sciences, Stanford Univ., Stanford, CA 94305-2115
b Dep. of Civil Engineering, 208 Harbert Engineering Center, Auburn Univ., Auburn, AL 36849-5337
c Environmental Sciences Division, Oak Ridge National Laboratory, P.O. Box 2008, Oak Ridge, TN 37831-6038
* Corresponding author (fendorf{at}stanford.edu)
A mechanistic understanding of U sorption in natural soils and sediments is useful for determining its transport and bioavailability in the environment. X-ray absorption spectroscopy (XAS) was used to determine the mechanisms by which U(VI) sorbs to three heterogeneous subsurface media reacted under static and dynamic flow conditions. Regardless of the media chosen, ternary surface complexes were the dominant type of sorption complex. Uranyl phosphate complexes were formed in subsurface media from more acidic environments. In contrast, uranyl carbonate ternary surface complexes formed in media from more neutral conditions. The complexes are predominantly inner-sphere, although some outer-sphere complexes may also be present, and appear to be on iron (hydr)oxides and possibly aluminosilicates. Additionally, the uranyl phosphate and carbonate complexes are highly disordered, which contributes to their reversible sorption properties.
Abbreviations:
2, Debye-Waller factor
(k), EXAFS spectral contribution CN, coordination number E0, energy of the U LIII edge EXAFS, extended x-ray adsorption fine structure spectroscopy FT, fourier transform HF, Hanford OR, Oak Ridge R, bond length RSF, radial structure function SR, Savannah River XANES, x-ray absorption near-edge structure XAS, x-ray absorption spectroscopy Z, type of the atoms coordinating U
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