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Anammox

 
Wikipedia: Anammox
Enrichment culture of the anammox bacterium Kuenenia stuttgartiensis, Radboud University Nijmegen

Anammox, an abbreviation for ANaerobic AMMonium OXidation, is a stage in the nitrogen cycle. It takes place in many natural environments and anammox is also the name for an ammonium removal technology that has been developed[1] by the Delft University of Technology

Contents

Process background

In this biological process, nitrite and ammonium are converted directly into dinitrogen gas. This process contributes up to 50% of the dinitrogen gas produced in the oceans. It is thus a major sink for fixed nitrogen and so limits oceanic primary productivity. The overall catabolic reaction is:

NH4+ + NO2 → N2 + 2H2O.

The bacteria that perform the anammox process belong to the bacterial phylum planctomycetes, of which Planctomyces and Pirellula are the best known genera. Currently four genera of anammox bacteria have been (provisionally) defined: Brocadia, Kuenenia, Anammoxoglobus (all fresh water species), and Scalindua (marine species). The anammox bacteria are characterized by several striking properties: they all possess one anammoxosome, a membrane bound compartment inside the cytoplasm which is the locus of anammox catabolism. Further, the membranes of these bacteria mainly consist of ladderane lipids so far unique in biology. Of special interest is the turnover of hydrazine (normally used as a high-energy rocket fuel, and poisonous to most living organisms) as an intermediate. A final striking feature of the organism is the extremely slow growth rate. The doubling time is nearly two weeks. The anammox process was originally found to occur only from 20oC to 43oC[2] but more recently, anammox has been observed at temperatures from 36oC to 52oC in hot springs [3] and 60oC to 85oC at hydrothermal vents located along the Mid-Atlantic Ridge[4].

History

For a long time the general consensus was that ammonium could only be oxidised under aerobic conditions. The Austrian theoretical chemist Engelbert Broda was the first to recognise the possibility of anaerobic ammonium oxidation in 1977[5]. The simultaneous removal of ammonium and production of nitrogen gas was observed in an industrial wastewater treatment in The Netherlands in 1986.

Application

The application of the anammox process lies in the removal of nitrogen in wastewater treatment. Instead of the conventional nitrification-denitrification process, only half of the nitrogen has to be oxidized partly to nitrite. For the enrichment of the anammox organisms a biofilm system seems to be especially suited in which the necessary sludge age of more than 20 days can be ensured. Other possibilities are sequencing batch reactors (SBR) or gas-lift-loop reactors using granular sludge. The cost reduction compared to conventional nitrogen removal is considerable; the technique is still young but proven in several fullscale installations. The first full scale sludge-water treatment plant where the Anammox process is observed was built 2000 in Germany (Hattingen). As of 2006 there are three full scale processes in The Netherlands. One on a municipal wastewater treatment plant (in Rotterdam), and two on industrial effluent. One is a tannery, the other a potato processing plant.

References

  1. ^ Jetten Michael Silvester Maria, Van Loosdrecht Marinus Corneli; Technische Universiteit Delft, patent WO9807664
  2. ^ Strous, M., Kuenen, J.G., Jetten, M.S. 1999. Key Physiology of Anaerobic Ammonium Oxidation. App. Environ. Microb. (3248-3250)
  3. ^ Jaeschke et al. 2009. 16s rRNA gene and lipid biomarker evidence for anaerobic ammonium-oxidizing bacteria (anammox) in California and Nevada hot springs. FEMS Microbiol. Ecol. 343-350
  4. ^ Byrne, N., Strous, M., Crepeau, V, et al. 2008. Presence and activity of anaerobic ammonium-oxidizing bacteria at deep-sea hydrothermal vents. The ISME Journal.
  5. ^ Brochier, C., Philippe, H. (2002), A non-hyperthermophilic ancestor for bacteria. Nature, 417, 244-

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