Evaluating societal risks posed by uranium contamination from waste managem
ent facilities, mining sites, and heavy industry requires knowledge about u
ranium transport in groundwater, often the most significant pathway of expo
sure to humans. It has been proposed that uranium mobility in aquifers may
be controlled by adsorption of U(VI)-carbonato complexes on oxide minerals.
The existence of such complexes has not been demonstrated, and little is k
nown about their compositions and reaction stoichiometries. We have used at
tenuated total reflectance Fourier transform infrared (ATR-FTIR) and extend
ed X-ray absorption fine structure (EXAFS) spectroscopies to probe the exis
tence, structures, and compositions of=FeOsurface-U(VI)-carbonato complexes
on hematite throughout the pH range of uranyl uptake under conditions rele
vant to aquifers. U(VI)-carbonato complexes were found to be the predominan
t adsorbed U(VI) species at all pH values examined, a much wider pH range t
han previously postulated based on analogy to aqueous U(VI)-carbonato compl
exes;, which are trace constituents at pH < 6. This result indicates the in
adequacy of the common modeling assumption that the compositions and predom
inance of adsorbed species can be inferred from aqueous species. By extensi
on, adsorbed carbonate complexes may be of major importance to the groundwa
ter transport of similar actinide contaminants such as neptunium and pluton
ium.