Nitrate reductase activity in spheroplasts from Rhodobacter capsulatus E1F1 requires a periplasmic protein

Biokinetic and biotransformation of nitrogen during photosynthetic bacteria wastewater treatment

Photosynthetic bacteria (PSB) show a strong potential to degrade pollutants and meanwhile produce valuable biomass, thus realising both wastewater treatment and nutrient recovery. This paper detailed the study of nitrogen distribution forms, biokinetics and transformation during PSB wastewater treatment. The results showed that the total nitrogen (TN) and ammonium (NH₄⁺) removal reached 90.5% and 95.3%, respectively. The nitrogen removal and biomass production fit a quadratic and a cubic regression equation with an R² of 0.9793 and 0.9730, respectively. Mass balance showed that the influent nitrogen was transformed into valuable PSB cells (63.2%), gaseous N₂ (26.9%) and residual NH₄⁺, nitrate (NO₃^-) and organic nitrogen in the effluent (8.9%). In addition, 53.0% of the influent nitrogen was bio-transformed to protein nitrogen. Excellent nitrogen resource recovery was thus achieved.

Interactions between nitrate assimilation and 2,4-dinitrophenol cometabolism in Rhodobacter capsulatus E1F1

The phototrophic, nitrate-photoassimilating bacterium Rhodobacter capsulatus E1F1 cometabolizes 2,4-dinitrophenol (DNP) by photoreducing it to 2-amino-4-nitrophenol under anaerobic conditions. DNP uptake and nitrate metabolism share some biochemical features, and in this article we show that both processes are influenced by each other. Thus, as was demonstrated for nitrate assimilation, DNP uptake requires a thermolabile periplasmic component. Nitrate assimilation is inhibited by DNP, which probably affects the nitrite reduction step because neither nitrate reductase activity nor the transport of nitrate or nitrite is inhibited. On the other hand, DNP uptake is competitively inhibited by nitrate, probably at the transport level, because the nitroreductase activity is not inhibited in vitro by nitrate, nitrite, or ammonium. In addition, the decrease in the intracellular DNP concentration in the presence of nitrate probably inactivates the nitroreductase. These results allow prediction of a negative environmental effect if nitrate and DNP are released together to natural habitats, because it may lead to a lower rate of DNP metabolism and to nitrite accumulation.

The assimilatory nitrate reduction system of the phototrophic bacterium Rhodobacter capsulatus E1F1

The phototrophic bacterium Rhodobacter capsulatus E1F1 assimilates nitrate under anaerobic phototrophic growth conditions. A 17 kb DNA region encoding the nitrate assimilation (nas) system of this bacterium has been cloned and sequenced. This region includes the genes coding for a putative ABC (ATP-binding cassette)-type nitrate transporter (nasFED) and the structural genes for the enzymes nitrate reductase (nasA), nitrite reductase (nasB) and hydroxylamine reductase (hcp). Three genes code for putative regulatory proteins: a nitrite-sensitive repressor (nsrR), a transcription antiterminator (nasT) and a nitrate sensor (nasS). Other genes probably involved in nitrate assimilation are also present in this region. The sequence analysis of these genes and the biochemical properties of the purified nitrate, nitrite and hydroxylamine reductases are reviewed.

The assimilatory nitrate reductase from the phototrophic bacterium, Rhodobacter capsulatus E1F1, is a flavoprotein

The assimilatory nitrate reductase from the phototrophic bacterium Rhodobacter capsulatus has been purified to electrophoretic homogeneity and its molecular and kinetic parameters determined. The native nitrate reductase is a dimer of 144 kDa composed of two subunits of 46 and 95 kDa. The purified enzyme catalyzes the electron transfer from NADH, reduced bromophenol blue or reduced viologens to nitrate. The nitrate reductase contains 1 mol FAD per mole of enzyme and also reduces cytochrome c or dichlorophenol indophenol with NADH as the electron donor. The diaphorase activity is located in the small subunit.