Application, eco-physiology and biodiversity of anaerobic ammonium-oxidizing bacteria

被引：56

作者：

Kartal B. ^{[1
]}

Van Niftrik L. ^{[2
]}

Sliekers O. ^{[2
]}

Schmid M.C. ^{[1
,2
]}

Schmidt I. ^{[1
,5
]}

Van De Pas-Schoonen K. ^{[1
]}

Cirpus I. ^{[2
]}

Van Der Star W. ^{[2
]}

Van Loosdrecht M. ^{[2
]}

Abma W. ^{[3
]}

Kuenen J.G. ^{[2
]}

Mulder J.-W. ^{[4
]}

Jetten M.S.M. ^{[1
,2
]}

Op Den Camp H. ^{[1
]}

Strous M. ^{[1
]}

Van De Vossenberg J. ^{[1
]}

机构：

[1] Department of Microbiology, Institute for Water and Wetland Research, Radboud University Nijmegen, NL 6525 ED Nijmegen

[2] Department of Biotechnology, TU Delft

[3] Department of Microbiology, University of Bayreuth

来源：

Reviews in Environmental Science and Bio/Technology | 2004年 / 3卷 / 3期

关键词：

16S rRNA gene; Anammox; Brocadia; Denitrification; Nitrification; Nitrite; Nitrogen removal; Planctomycetes; Urea;

D O I：

10.1007/s11157-004-7247-5

中图分类号：

学科分类号：

摘要：

The demand for new and sustainable systems for nitrogen removal has increased dramatically in the last decade. It is clear that the conventional systems cannot deal with the increasing nitrogen loads in a cost effective way. As an alternative, the implementation of the anammox (anaerobic ammonium oxidation) process in the treatment of wastewater with high ammonium concentrations has been started. The compact anammox reactors can sustain high nitrogen loads without any problems. The highest observed anammox capacity is 8.9 kg N removed m-3 reactor day-1. The first 75 m 3 anammox reactor is operating in Rotterdam, the Netherlands, combined with the partial nitrification process Single reaction system for High Ammonium Removal Over Nitrite (SHARON). Partial nitrification and anammox can also be combined in one reactor systems like Completely Autotrophic Nitrogen removal Over Nitrite (CANON) or Oxygen Limited Ammonium removal via Nitrification Denitrification (OLAND) where aerobic ammonium-oxidizing bacteria (AOB) and anammox bacteria cooperate under oxygen-limitation. These systems remove about 1.5 kg N m-3 reactor day-1. In addition to ammonium, urea can also be converted in the CANON system after a two-week adaptation period. The ecophysiological properties of the anammox bacteria make them very well suited to convert ammonium and nitrite. The Ks values for ammonium and nitrite are below 5 μM. However, nitrite above 10 mM is detrimental for the anammox process, and oxygen reversibly inhibits the process at concentrations as low as 1 μM. Acetate and propionate can be used by the anammox bacteria to convert nitrite and nitrate, whereas methanol and ethanol severely inhibit the anammox reaction. The enzyme hydroxylamine/hydrazine oxidoreductase (HAO), one of the key enzymes, is located in the anammoxosome, which is a membrane bound organelle. The membranes of the anammox bacteria contain unique ladderane lipids and hopanoids. The bacteria responsible for the anammox reaction are related to the Planctomycetes. The first anammox bacteria were isolated via Percoll centrifugation and characterized as Candidatus "Brocadia anammoxidans". Survey of different wastewater treatment plants using anammox specific 16S rRNA gene primers and anammox specific oligonucleotide probes has revealed the presence of at least three other anammox bacteria, which have been tentatively named Candidatus "Kuenenia stuttgartiensis", Candidatus "Scalindua wagneri" and Candidatus "Scalindua brodae". A close relative of the latter, Candidatus "Scalindua sorokinii" was found to be responsible for about 50% of the nitrogen conversion in the anoxic zone of the Black Sea, making the anammox bacteria an important player in the oceanic nitrogen cycle. © Springer 2004.

引用

页码：255 / 264

页数：9

共 70 条

[1]

Dalsgaard T., Canfield D.E., Petersen J., Thamdrup B., Acuna-Gonzalez J., Anammox is a significant pathway of N <sub>2</sub> production in the anoxic water column of Golfo Dulce, Costa Rica, Nature, 422, pp. 606-608, (2003)

[2]

Dalsgaard T., Thamdrup B., Factors controlling anaerobic ammonium oxidation with nitrite in marine sediments, Appl. Environ. Microbiol, 68, pp. 3802-3808, (2002)

[3]

Dapena-Mora A., Arrojo B., Campos J.L., Mosquera-Corral A., Mendez R., Improvement of the settling properties of Anammox sludge in an SBR, J. Chem. Technol. Biotechnol, 79, pp. 1417-1420, (2004)

[4]

Dapena-Mora A., Campos J.L., Mosquera-Corral A., Jetten M.S., Mendez R., Stability of the ANAMMOX process in a gas-lift reactor and a SBR, J. Biotechnol, 110, 2, pp. 159-170, (2004)

[5]

Dapena-Mora A., Van Hulle S.W.H., Campos J.L., Mendez R., Vanrolleghem P.A., Jetten M.S.M., Enrichment of Anammox biomass from municipal activated sludge: Experimental and modelling results, J. Chem. Technol. Biotechnol, 79, pp. 1421-1428, (2004)

[6]

Dong X., Tollner E.W., Evaluation of Anammox and denitrification during anaerobic digestion of poultry manure, Bioresour. Technol, 86, 2, pp. 139-145, (2003)

[7]

Egli K., Bosshard F., Werlen C., Lais P., Siegrist H., Zehnder A.J., Van der Meer J.R., Microbial composition and structure of a rotating biological contactor biofilm treating ammonium-rich wastewater without organic carbon, Microbiol. Ecol, 45, 4, pp. 419-432, (2003)

[8]

Egli K., Franger U., Alvarez P.J.J., Siegrist H., Vandermeer J.R., Zehnder A.J.B., Enrichment and characterization of an anmmox bacterium from a rotating biological contractor treating ammonium-rich leachate, Arch. Microbiol, 175, pp. 198-207, (2001)

[9]

Fujii T., Sugino H., Rouse J.D., Furukawa K., Characterization of the microbial community in an anaerobic ammonium-oxidizing biofilm cultured on a non-woven biomass carrier, J Biosci. Bioeng, 94, 5, pp. 412-418, (2002)

[10]

Furukawa K., Rouse J.D., Yoshida N., Hatanaka II, Mass cultivation of anaerobic ammonium-oxidizing sludge using a novel nonwoven biomass carrier, J. Chem. Eng. Jpn, 36, 10, pp. 1163-1169, (2003)

← 1 2 3 4 5 6 7 →