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N’Guessan and 6 co-authors in 2009 evaluated the influence of changes in the microbial community  structure on reoxidation of reduced uranium during a postbiostimulation period.  Effluent groundwater from acetate-stimulated sediment flow-through columns  was analyzed over 60 days after acetate amendment was discontinued.

Geochemical changes in flow-through columns' effluent groundwater.
Acetate (a), uranium (b), iron (c), and sulfate (d).

Only a small  reoxidation of iron or uranium (17%) occurred in the presence of 1–2 mg L-1 O2   influent groundwater for the 2-month period. Most uranium reoxidation occurred  during the first 2 weeks after biostimulation with acetate was discontinued.  Groundwater and sediment microbial community compositions suggested that  two processes played important roles immediately after the cessation of acetate  addition.

The first process was characterized by a predominance of both sediment-  bound and planktonic microorganisms most closely related to Hydrogenophaga  sp., Thiobacillus sp., and Gallionella sp., which could oxidize a variety of reduced  compounds. The second process was characterized by organisms closely related to  Lysobacter sp. and Sterolibacterium sp., with the potential to feed on complex  organic compounds from biomass turnover.

The presence of these bacteria and the  lack of uranium oxidation implied that after acetate addition was stopped, reduced  inorganic compounds and dead biomass became electron donors for a microbial  community capable of using low ambient oxygen as a terminal electron acceptor,  contributing to the preservation, at least temporarily, of biogenic U(IV). 

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