Modeling
of Heavy Nitrate Corrosion in Anaerobe Aquifer
Injection Water Biofilm: A Case Study in a Flow Rig
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Abstract
Heavy
carbon steel corrosion developed during nitrate mitigation
of a flow rig connected to a water injection pipeline flowing anaerobe
saline aquifer water. Genera-specific QPCR primers quantified 74%
of the microbial biofilm community, and further 87% of the community
of the nonamended parallel rig. The nonamended biofilm hosted 6.3
× 10<sup>6</sup> SRB cells/cm<sup>2</sup> and the S<sup>35</sup>-sulfate-reduction rate was 1.1 μmol SO<sub>4</sub><sup>2–</sup>/cm<sup>2</sup>/day, being congruent with the estimated SRB biomass
formation and the sulfate areal flux. Nitrate amendment caused an
18-fold smaller SRB population, but up to 44 times higher sulfate
reduction rates. This H<sub>2</sub>S formation was insufficient to
form the observed Fe<sub>3</sub>S<sub>4</sub> layer. Additional H<sub>2</sub>S was provided by microbial disproportionation of sulfur,
also explaining the increased accessibility of sulfate. The reduced
nitrate specie nitrite inhibited the dominating H<sub>2</sub>-scavenging <i>Desulfovibrio</i> population, and sustained the formation of
polysulfide and Fe<sub>3</sub>S<sub>4</sub>, herby also dissolved
sulfur. This terminated the availability of acetate in the inner biofilm
and caused cell starvation that initiated growth upon metallic electrons,
probably by the sulfur-reducing <i>Desulfuromonas</i> population.
On the basis of these observations we propose a model of heavy nitrate
corrosion where three microbiological processes of nitrate reduction,
disproportionation of sulfur, and metallic electron growth are nicely
woven into each other