Biological Nitrogen Removal Database

A manually curated data resource for microbial nitrogen removal


Groundwater Water systems


Experimental setup


Influent:Groundwater

Denitrification system:Chemoautotrophic hydrogenotrophic denitrification

Denitrifying reactor:Continuous flow fixed film reactor

Medium:Suspended culture

Culture taken from:Activated sludge

Organism (s) cultured:nan

Respiration:Anoxic

Electron donor:Hydrogen

Electron acceptor:Nitrate


Experimental Information


Input NO3-N (mg/l):nan

Nitrate removal rate (mg NO3-N/l/h):nan

Denitrification rate (gNO3-N removed/m3/day):2.7–5.3

Microorganisms identified:Novel hydrogenotrophic denitrifiers

Molecular tools:PCR, 16S rRNA


Information about Article


Major findings:High nitrate removal rates were recorded and the microporous membrane used in this study served as an effective barrier for preventing microbial contamination of the product water. Novel hydrogenotrophic denitrifers were identified that need to be characterized.

Authors:Mansell and Schroeder., 2002

Title:Hydrogenotrophic denitrification in a microporous membrane bioreactor. 

Pubmed link:Link

Full research link:Link

Abstract:Hydrogenotrophic denitrification of nitrate contaminated groundwater in a bench-scale microporous membrane bioreactor has been investigated. To prevent microbial contamination of the effluent from the reactor the nitrate-laden water treated was separated from the denitrifying culture with a 0.02 microm pore diameter membrane. Equal pressure was maintained across the membrane and nitrate was removed by molecular diffusion through the membrane and into the denitrifying culture. The system was operated with a hydrogenotrophic denitrification culture to circumvent the addition of an organic substrate to the water. Removal efficiencies ranging from 96% to 92% were achieved at influent concentrations ranging from 20 to 40 mg/L NO3(-)-N. The flux values achieved in this study were 2.7-5.3 g NO3-N m 2d(-1). The microporous membrane served as an effective barrier for preventing microbial contamination of the product water as evidenced by the effluent heterotrophic plate count of 9 (+/- 3.5) CFU/mL. The hydrogenotrophic culture was analyzed using available 16S and 23S rRNA-targeted oligonucleotide probes. It was determined that the enrichment process selected for organisms belonging to the beta subclass of Proteobacteria. Further analysis of the hydrogenotrophic culture indicated that the organisms may belong to the beta-3 subgroup of Proteobacteria and have yet to be identified as hydrogenotrophic denitrifiers.