Biological Nitrogen Removal Database

A manually curated data resource for microbial nitrogen removal


Marine systems


Experimental setup


Influent:Seawater

Denitrification system:Recirculating aquaculture systems Heterotrophic Denitrification

Denitrifying reactor:Packed bed

Medium:Stationary filament biofilter substrate (BIOPOLYMA™)

Culture taken from:Bacillus sp.

Organism (s) cultured:Black tiger shrimp (Penaeus monodon)

Respiration:Aerobic

Electron donor:Ethanol/methanol

Electron acceptor:Nitrate


Experimental Information


Input NO3-N (mg/l):165

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

Denitrification rate (gNO3-N removed/m3/day):158

Microorganisms identified:nan

Molecular tools:nan


Information about Article


Major findings:The denitrification system was modified (carbon source, substrate and hydraulic residence time) which enhanced the removal of nitrate and the system's pH was stabilized improving the water quality. The shrimp grew quite well

Authors:Menasveta et al., 2001

Title:Design and function of a closed, recirculating seawater system with denitrification for the culture of black tiger shrimp broodstock.

Pubmed link:None

Full research link:Link

Abstract:A closed, recirculating seawater system with a denitrification process was designed for the culture of black tiger shrimp broodstock. The system comprised a circular rearing tank (9 m3 volume), a nitrifying biofilter (6 m3 volume) and denitrification process. The denitrification process comprised a deoxygenation column, a bacterial substrate column (143 L volume) and a re-aeration column connected to the biofilter. The experimental period was 81 weeks, consisting of 3 sequential trials using different substrates, bacterial inoculates and carbon sources: Trial 1- porous plastic balls for substrate, mangrove soil for inoculant and ethanol for the carbon source; Trial 2- crushed oyster shell for substrate, a strain of laboratory cultured bacteria for inoculant and ethanol for the carbon source; and Trial 3- crushed oyster shell for the substrate, no inoculant and methanol for the carbon source. The nitrifying biofilter controlled ammonium-N and nitrite-N within acceptable ranges (<0.5 and <0.2 mg L?1, respectively). The nitrate-N, however, became elevated gradually during trial 1 (<50 mg L?1). During trial 2, modification of bacterial substrate and the inoculation with denitrifying bacteria reduced nitrate-N in the denitrification column and the rearing tank (p<0.05). Changing the carbon source to methanol and increasing the hydraulic residence time in trial 3 resulted in a significant reduction (P<0.05) in nitrate-N (from >160 to <25 mg l?1) without the need for bacterial inoculation.