Diagenetic formation of uranium-silica polymers in lake sediments over 3,300 years.
basic_science · Level V
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- Record sourced from PubMed, PMID 33479173.
- Also identified by DOI 10.1073/pnas.2021844118 and PMC identifier 7848604.
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Abstract
The long-term fate of uranium-contaminated sediments, especially downstream former mining areas, is a widespread environmental challenge. Essential for their management is the proper understanding of uranium (U) immobilization mechanisms in reducing environments. In particular, the long-term behavior of noncrystalline U(IV) species and their possible evolution to more stable phases in subsurface conditions is poorly documented, which limits our ability to predict U long-term geochemical reactivity. Here, we report direct evidence for the evolution of U speciation over 3,300 y in naturally highly U-enriched sediments (350-760 µg ⋅ g<sup>-1</sup> U) from Lake Nègre (Mercantour Massif, Mediterranean Alps, France) by combining U isotopic data (δ<sup>238</sup>U and (<sup>234</sup>U/<sup>238</sup>U)) with U <i>L</i><sub><i>3</i></sub> -edge X-ray absorption fine structure spectroscopy. Constant isotopic ratios over the entire sediment core indicate stable U sources and accumulation modes, allowing for determination of the impact of aging on U speciation. We demonstrate that, after sediment deposition, mononuclear U(IV) species associated with organic matter transformed into authigenic polymeric U(IV)-silica species that might have partially converted to a nanocrystalline coffinite (U<sup>IV</sup>SiO<sub>4</sub>·<i>n</i>H<sub>2</sub>O)-like phase. This diagenetic transformation occurred in less than 700 y and is consistent with the high silica availability of sediments in which diatoms are abundant. It also yields consistency with laboratory studies that proposed the formation of colloidal polynuclear U(IV)-silica species, as precursors for coffinite formation. However, the incomplete transformation observed here only slightly reduces the potential lability of U, which could have important implications to evaluate the long-term management of U-contaminated sediments and, by extension, of U-bearing wastes in silica-rich subsurface environments.