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June 6, 2003 Incorporation of Uranium with Iron Oxide MineralsM.C. Duff, J.U. Coughlin, and D.B. Hunter The transport and biological availability of the toxic, radioactive element uranium (U) towards reduction to the less soluble U(IV) species may be limited by co-precipitation with Fe-oxide minerals. We examined the interaction dynamics between U(VI) and iron (Fe) oxides during crystallization by synthesizing Fe-oxide phases [0.5-5.4 mole %U/(U + Fe)] using U(VI) and Fe(III) solutions. Our studies show that U6+ is incorporated in Fe oxides as the uncommon uranate species (without axial O atoms) until saturation is reached whereby U(VI) forms crystalline U(IV)O22+ phases.
Leaching of the synthetic U-Fe oxides typically removed most sorbed and solid phase U(VI) species leaving on average ~0.6 mol % U. X-ray diffraction and infrared spectroscopic studies (Figure 2A-B) indicate that hematite (Fe2O3) formation is preferred over that of goethite (FeOOH) when the U level in the Fe-oxides exceeds 1 mol % U. Our studies with unleached U/Fe solids indicate a relationship between the mol % U in the Fe oxide, and the existence of the spectral features that can be assigned to uranyl species. These spectral features were undetectable in leached solids, suggesting solid phase and sorbed U(VI)O22+ species are extracted by leaching. Using uranium X-ray Absorption Fine Structure (XAFS) at NSLS beamlines X23A2 and X26A, analyses of unleached solids containing <1 mol % U revealed that U(VI) exists with four O atoms at radial distances of 2.21 and 2.36 Å and Fe atoms at 3.19 Å (Figure 2C). Due to the large size of UO22+ (~1.8 Å) relative to Fe3+ (0.65 Å), the UO22+ ion is unlikely to substitute for the Fe. Our results indicate that U6+ (~0.72-0.8 Å) is incorporated in the Fe oxides as uranate until a point of saturation is reached. Beyond this concentration, excess U precipitates as crystalline U(VI) phases resembling schoepite.
In summary, our findings indicate that the long-term association of U in the contaminated environment could result in the structural incorporation of U in Fe oxide host phases. In nature, precipitation of pure U phases should occur at a kinetically faster rate than the structural incorporation of U into Fe oxides. Precipitation of U as pure mineral phases should be favored at high dissolved U concentrations, whereas sorption and co-precipitation of U are most likely favored at lower U concentrations. In aged, U-contaminated Fe-rich soils, uptake of U by Fe oxides may be significant since ~1 mol % U can be incorporated. The importance of these mechanisms in U-contaminated materials has not been estimated. BEAMLINE FUNDING PUBLICATION FOR MORE INFORMATION |
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