Scalindua wagneri

Candidatus Scalindua wagneri
Scientific classification
Domain:
Bacteria
Phylum:
Planctomycetota
Class:
Planctomycetia
Order:
Planctomycetales
Family:
Brocadiceae
Genus:
Scalindua
Species:
wagneri
Binomial name
Candidatus Scalindua wagneri
Schmid et al. 2003.

Candidatus Scalindua wagneri is a Gram-negative coccoid-shaped bacterium that was first isolated from a wastewater treatment plant.[1] This bacterium is an obligate anaerobic chemolithotroph that undergoes anaerobic ammonium oxidation (anammox).[1] It can be used in the wastewater treatment industry in nitrogen reactors to remove nitrogenous wastes from wastewater without contributing to fixed nitrogen loss and greenhouse gas emission.[2]

Characterization

Candidatus Scalindua wagneri is a coccoid-shaped bacterium with a diameter of 1 μm.[1] Like other Planctomycetes, S. wagneri is Gram-negative and does not have peptidoglycan in its cell wall.[1] In addition, the bacterium contains two inner membranes instead of having one inner membrane and one outer membrane that surrounds the cell wall.[3] Some of the near neighbors are other species within the new Scalindua genus, such as Candidatus S. sorokinii and Candidatus S. brodae.[1] Other neighbors include Candidatus Kuenenia stuttgartiensis and Candidatus Brocadia anammoxidans.[1] S. wagneri and its genus share only about 85% similarity with other members in its evolutionary line, which suggests that it is distantly related to other anaerobic ammonium oxidizing (anammox) bacteria.[1]

Discovery

Markus Schmid from the Strous lab first discovered S. wagneri in a landfill leachate treatment plant located in Pitsea, UK on August 1, 2001.[1] These bacteria doubled in number about every three weeks in laboratory conditions, which made them very difficult to isolate.[1] Therefore, the researchers used 16S rRNA (ribosomal RNA) gene analysis on the biofilm of wastewater samples to detect the presence of these bacteria.[1] They amplified and isolated the 16S rRNA gene from the biofilm using PCR and gel electrophoresis. Then, they cloned the DNA into TOPO vectors.[1] Once the researchers sequenced the DNA, they aligned the 16S rRNA gene sequences to a genome database and found that the sequences are related to the anammox bacteria.[1] One of the sequences showed a 93% similarity to Candidatus Scalindua sorokinii, which suggests that this sequence belonged to a new species within the genus Scalindua and the researchers named it Candidatus Scalindua wagneri after Michael Wagner, a microbial ecologist.[1]

Metabolism

S. wagneri is an obligate anaerobic chemolithoautotroph and undergoes anaerobic ammonium oxidation (anammox) in the intracytoplasmic compartment called an anammoxosome.[1][3] During the anammox process, ammonium is oxidized using nitrite as an electron acceptor and forms dinitrogen gas as a product.[1] It is proposed that this mechanism occurs through the production of a hydrazine intermediate using hydroxylamine, which is derived from nitrite.[1] In addition, S. wagneri uses nitrite as an electron donor to fix carbon dioxide and forms nitrate as a byproduct.[1] To the test the metabolic properties of S. wagneri, Nakajima et al. performed anammox activity tests using nitrogen compounds labeled with the 15N isotopes and measured 28N2, 29N2, and 30N2 concentrations after 15 days.[4] The researchers found that the concentrations of the 28N2 and 29N2 gases increased significantly.[4] These results suggest that ammonia and nitrite is used in equal amounts to make 29N2, and denitrification concurrently occurs with anammox metabolism.[4]

Genome

Currently, genomic information about S. wagneri is very limited.[5] Current genome sequences were collected from DNA isolated from the bacteria growing in a marine anammox bacteria (MAB) reactor.[4] Then, the 16S rRNA genes on the DNA were amplified using a specific oligonucleotide primer for Planctomycetales, separated using gel electrophoresis, and sequenced using a CEQ 2000 DNA Sequencer.[4] Analysis of the 16S rRNA gene sequences was performed using the GENETYX program, and the alignments and phylogenetic trees were made using BLAST, CLUSTALW and neighbor joining, respectively.[4] To have a better understanding of the genome, S. wagneri can be compared to one of its better-known relatives. For example, Candidatus Scalindua profunda has a genome length of 5.14 million base pairs with a GC content of 39.1%.[6] There is no genomic information about the length or % GC content for S. wagneri. However, there are hundreds of 476 base pair partial sequences for its 16S rRNA gene.[5] Using fluorescent in situ hybridization (FISH) analysis, a technique used to detect specific DNA sequences on chromosomes, researchers were not able to detect hybridization between the chromosome of S. wagneri and the putative anammox DNA probe.[1] This suggests that S. wagneri is not very similar to the known anammox bacteria, so the researchers categorized the bacterium into its own genus.[1]

Ecology

Although researchers are unable to isolate pure cultures of S. wagneri, it is believed to encompass a broad niche.[7] Using 16S rRNA gene analysis, Schmid first found evidence of the bacteria in wastewater treatment plants.[1] Other researchers also found 16S rRNA gene evidence in a petroleum reservoir held at a temperature range between 55 °C and 75 °C in addition to freshwater and marine ecosystems, such as estuaries.[7][8]

Importance and useful applications

S. wagneri allows wastewater treatment plants to reduce operation costs while reducing the adverse effects of nitrification and denitrification on the environment.[2] These bacteria contribute to the development of new technologies for wastewater management by aiding in the efficient removal of nitrogenous compounds in wastewater.[1] Usually, nitrogen reactors use both nitrification and denitrification to remove nitrogenous wastes.[2] These processes have high operation costs due to the continuous maintenance of aerobic conditions in the reactor.[2] Denitrification also produces nitrous oxide (N2O), which is a greenhouse gas that is detrimental to the environment.[9] Production of N2O contributes to the loss of fixed nitrogen, which regulates the biological productivity of ecosystems.[10][11] By inoculating wastewater reactors with the anaerobic S. wagneri, operation costs can be reduced by about ninety percent without the production of greenhouse gases.[2] This allows for better wastewater management in a more cost-efficient manner without contributing to climate change.[2][9]

References

  1. 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 Schmid, Markus; Walsh, Kerry; Webb, Rick; Rijpstra, W. Irene; van de Pas-Schoonen, Katinka; Verbruggen, Mark Jan; Hill, Thomas; Moffett, Bruce; Fuerst, John; Schouten, Stefan; Sinninghe Damsté, Jaap S.; Harris, James; Shaw, Phil; Jetten, Mike; Strous, Marc (January 2003). "Candidatus "Scalindua brodae", sp. nov., Candidatus "Scalindua wagneri", sp. nov., Two New Species of Anaerobic Ammonium Oxidizing Bacteria". Systematic and Applied Microbiology. 26 (4): 529–538. doi:10.1078/072320203770865837. PMID 14666981.
  2. 1 2 3 4 5 6 Jetten, Mike; Schmid, Markus; Schmidt, Ingo; van Loosdrescht, Mark; Abma, Wiebe; Kuenen, J. Gijs; Mulder, Jan-Willem; Strous, Marc (2004). Biodiversity and application of anaerobic ammonium-oxidizing bacteria. European Symposium on Environmental Biotechnology. pp. 21–26. ISBN 9789058096531. Retrieved 15 February 2016.
  3. 1 2 van Niftrik, Laura A.; Fuerst, John A.; Damste, Jaap S. Sinninghe; Kuenen, J. Gijs; Jetten, Mike S.M.; Strous, Marc (April 2004). "The anammoxosome: an intracytoplasmic compartment in anammox bacteria". FEMS Microbiology Letters. 233 (1): 7–13. doi:10.1016/j.femsle.2004.01.044. PMID 15098544.
  4. 1 2 3 4 5 6 Nakajima, J; Sakka, M; Kimura, T; Furukawa, K; Sakka, K (2008). "Enrichment of anammox bacteria from marine environment for the construction of a bioremediation reactor". Applied Microbiology and Biotechnology. 77 (5): 1159–1166. doi:10.1007/s00253-007-1247-7. PMID 17965857. S2CID 20103740.
  5. 1 2 "Scalindua wagneri". NCBI. NCBI. Retrieved 10 March 2015.
  6. ↑ van de Vossenberg, Jack; Woebken, Dagmar; Maalcke, Wouter J.; Wessels, Hans J. C. T.; Dutilh, Bas E.; Kartal, Boran; Janssen-Megens, Eva M.; Roeselers, Guus; Yan, Jia; Speth, Daan; Gloerich, Jolein; Geerts, Wim; van der Biezen, Erwin; Pluk, Wendy; Francoijs, Kees-Jan; Russ, Lina; Lam, Phyllis; Malfatti, Stefanie A.; Tringe, Susannah Green; Haaijer, Suzanne C. M.; Op den Camp, Huub J. M.; Stunnenberg, Henk G.; Amann, Rudi; Kuypers, Marcel M. M.; Jetten, Mike S. M. (May 2013). "The metagenome of the marine anammox bacterium 'Scalindua profunda' illustrates the versatility of this globally important nitrogen cycle bacterium". Environmental Microbiology. 15 (5): 1275–1289. doi:10.1111/j.1462-2920.2012.02774.x. PMC 3655542. PMID 22568606.
  7. 1 2 Li, Hui; Chen, Shuo; Mu, Bo-Zhong; Gu, Ji-Dong (26 August 2010). "Molecular Detection of Anaerobic Ammonium-Oxidizing (Anammox) Bacteria in High-Temperature Petroleum Reservoirs". Microbial Ecology. 60 (4): 771–783. doi:10.1007/s00248-010-9733-3. PMC 2974184. PMID 20740282.
  8. ↑ Penton, C. R.; Devol, A. H.; Tiedje, J. M. (4 October 2006). "Molecular Evidence for the Broad Distribution of Anaerobic Ammonium-Oxidizing Bacteria in Freshwater and Marine Sediments". Applied and Environmental Microbiology. 72 (10): 6829–6832. Bibcode:2006ApEnM..72.6829P. doi:10.1128/AEM.01254-06. PMC 1610322. PMID 17021238.
  9. 1 2 Hu, Z.; Lotti, T.; de Kreuk, M.; Kleerebezem, R.; van Loosdrecht, M.; Kruit, J.; Jetten, M. S. M.; Kartal, B. (15 February 2013). "Nitrogen Removal by a Nitritation-Anammox Bioreactor at Low Temperature". Applied and Environmental Microbiology. 79 (8): 2807–2812. Bibcode:2013ApEnM..79.2807H. doi:10.1128/AEM.03987-12. PMC 3623191. PMID 23417008.
  10. ↑ Wright, Jody J.; Konwar, Kishori M.; Hallam, Steven J. (14 May 2012). "Microbial ecology of expanding oxygen minimum zones". Nature Reviews Microbiology. 10 (6): 381–394. doi:10.1038/nrmicro2778. PMID 22580367. S2CID 1467645.
  11. ↑ Moore, C. M.; Mills, M. M.; Arrigo, K. R.; Berman-Frank, I.; Bopp, L.; Boyd, P. W.; Galbraith, E. D.; Geider, R. J.; Guieu, C.; Jaccard, S. L.; Jickells, T. D.; La Roche, J.; Lenton, T. M.; Mahowald, N. M.; Marañón, E.; Marinov, I.; Moore, J. K.; Nakatsuka, T.; Oschlies, A.; Saito, M. A.; Thingstad, T. F.; Tsuda, A.; Ulloa, O. (31 March 2013). "Processes and patterns of oceanic nutrient limitation". Nature Geoscience. 6 (9): 701–710. Bibcode:2013NatGe...6..701M. CiteSeerX 10.1.1.397.5625. doi:10.1038/ngeo1765.
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