Modeling of Heavy Nitrate Corrosion in Anaerobe Aquifer Injection Water Biofilm: A Case Study in a Flow Rig

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

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