Microbial Reduction of U(VI) under Alkaline Conditions: Implications for Radioactive Waste Geodisposal

Although there is consensus that microorganisms significantly influence uranium speciation and mobility in the subsurface under circumneutral conditions, microbiologically mediated U­(VI) redox cycling under alkaline conditions relevant to the geological disposal of cementitious intermediate level radioactive waste, remains unexplored. Here, we describe microcosm experiments that investigate the biogeochemical fate of U­(VI) at pH 10–10.5, using sediments from a legacy lime working site, stimulated with an added electron donor, and incubated in the presence and absence of added Fe­(III) as ferrihydrite. In systems without added Fe­(III), partial U­(VI) reduction occurred, forming a U­(IV)-bearing non-uraninite phase which underwent reoxidation in the presence of air (O₂) and to some extent nitrate. By contrast, in the presence of added Fe­(III), U­(VI) was first removed from solution by sorption to the Fe­(III) mineral, followed by bioreduction and (bio)­magnetite formation coupled to formation of a complex U­(IV)-bearing phase with uraninite present, which also underwent air (O₂) and partial nitrate reoxidation. 16S rRNA gene pyrosequencing showed that Gram-positive bacteria affiliated with the <i>Firmicutes</i> and <i>Bacteroidetes</i> dominated in the post-reduction sediments. These data provide the first insights into uranium biogeochemistry at high pH and have significant implications for the long-term fate of uranium in geological disposal in both engineered barrier systems and the alkaline, chemically disturbed geosphere