Methylosinus trichosporium

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Methylosinus trichosporium
Scientific classification
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M. trichosporium
Binomial name
Methylosinus trichosporium
Bowman et al. 1993 [1]
Type strain
ACM 3311, ATCC 35070, IMET 10541, NCIMB 11131, OB3b, UNIQEM 75, VKM B-2117 [2]

Methylosinus trichosporium is an obligate aerobic and methane-oxidizing bacterium species from the genus of Methylosinus . [1] [3] [4] [5] [6] Its native habitat is generally in the soil, but the bacteria has been isolated from fresh water sediments and groundwater as well. [7] Because of this bacterium's ability to oxidize methane, M. trichosporium has been popular for identifying both the structure and function of enzymes involved with methane oxidation since it was first isolated in 1970 by Roger Whittenbury and colleagues. [4] [6] Since its discovery, M. trichosporium and its soluble monooxygenase enzyme have been studied in detail to see if the bacterium could help in bioremediation treatments. [8]

Contents

Biology

As a type II methanotroph, M. trichosporium relies on methane as its primary source of carbon and energy. [9] A commonly used strain of this bacteria is strain OB3b, which is available through the American Type Culture Collection. [9] Even though all methanotrophs can form particulate methane monooxygenase (pMMO), the ability to produce soluble methane monooxygenase (sMMO) is limited to type II methanotrophs. [10] These enzymes perform the same purpose for cellular function, but sMMO has a much higher specificity compared to pMMO. [8] Another key difference between the sMMO and pMMO is that they are produced under different conditions. In environments with concentrations of copper lower than 0.25 µM, sMMO is produced, but in higher concentrations of copper, sMMO production is lost and pMMO is produced. [9]

Applications in bioremediation

The ability to produce sMMO is of particular interest to researchers due to its ability to degrade trichloroethene (TCE) at a magnitude one order higher than other microbial cultures. [9] [8] For example, in one study on removal of TCE from sources at as high of concentration as 50 mg/mL, M. trichosporium was shown to be able to remove up to 99% of TCE. [9] Despite the efficiency of sMMO, the products formed from degrading TCE are toxic to M. trichosporium. This bacterium already grows relatively slowly, so toxic effects of TCE degradation products have made it challenging to use M. trichosporium in bioremediation treatments. [8] The effect of copper on strain OB3b's ability to produce sMMO is also a limiting effect of what environments M. trichosporium can be used in.

Related Research Articles

<span class="mw-page-title-main">Nitrification</span> Biological oxidation of ammonia/ammonium to nitrate

Nitrification is the biological oxidation of ammonia to nitrate via the intermediary nitrite. Nitrification is an important step in the nitrogen cycle in soil. The process of complete nitrification may occur through separate organisms or entirely within one organism, as in comammox bacteria. The transformation of ammonia to nitrite is usually the rate limiting step of nitrification. Nitrification is an aerobic process performed by small groups of autotrophic bacteria and archaea.

Methanotrophs are prokaryotes that metabolize methane as their source of carbon and chemical energy. They are bacteria or archaea, can grow aerobically or anaerobically, and require single-carbon compounds to survive.

Methylotrophs are a diverse group of microorganisms that can use reduced one-carbon compounds, such as methanol or methane, as the carbon source for their growth; and multi-carbon compounds that contain no carbon-carbon bonds, such as dimethyl ether and dimethylamine. This group of microorganisms also includes those capable of assimilating reduced one-carbon compounds by way of carbon dioxide using the ribulose bisphosphate pathway. These organisms should not be confused with methanogens which on the contrary produce methane as a by-product from various one-carbon compounds such as carbon dioxide. Some methylotrophs can degrade the greenhouse gas methane, and in this case they are called methanotrophs. The abundance, purity, and low price of methanol compared to commonly used sugars make methylotrophs competent organisms for production of amino acids, vitamins, recombinant proteins, single-cell proteins, co-enzymes and cytochromes.

Cometabolism is defined as the simultaneous degradation of two compounds, in which the degradation of the second compound depends on the presence of the first compound. This is in contrast to simultaneous catabolism, where each substrate is catabolized concomitantly by different enzymes. Cometabolism occurs when an enzyme produced by an organism to catalyze the degradation of its growth-substrate to derive energy and carbon from it is also capable of degrading additional compounds. The fortuitous degradation of these additional compounds does not support the growth of the bacteria, and some of these compounds can even be toxic in certain concentrations to the bacteria.

<span class="mw-page-title-main">Methane monooxygenase</span> Class of enzymes

Methane monooxygenase (MMO) is an enzyme capable of oxidizing the C-H bond in methane as well as other alkanes. Methane monooxygenase belongs to the class of oxidoreductase enzymes.

Dehalococcoides is a genus of bacteria within class Dehalococcoidia that obtain energy via the oxidation of hydrogen and subsequent reductive dehalogenation of halogenated organic compounds in a mode of anaerobic respiration called organohalide respiration. They are well known for their great potential to remediate halogenated ethenes and aromatics. They are the only bacteria known to transform highly chlorinated dioxins, PCBs. In addition, they are the only known bacteria to transform tetrachloroethene to ethene.

Methylobacillus flagellatus is a species of aerobic bacteria.

Methanobactin (mb) is a class of copper-binding and reducing chromophoric peptides initially identified in the methanotroph Methylococcus capsulatus Bath - and later in Methylosinus trichosporium OB3b - during the isolation of the membrane-associated or particulate methane monooxygenase (pMMO). It is thought to be secreted to the extracellular media to recruit copper, a critical component of methane monooxygenase, the first enzyme in the series that catalyzes the oxidation of methane into methanol. Methanobactin functions as a chalkophore, similar to iron siderophores, by binding to Cu(II) or Cu(I) then shuttling the copper into the cell. Methanobactin has an extremely high affinity for binding and Cu(I) with a Kd of approximately 1020 M−1 at pH 8. Additionally, methanobactin can reduce Cu(II), which is toxic to cells, to Cu(I), the form used in pMMO. Moreover, different species of methanobactin are hypothesized to be ubiquitous within the biosphere, especially in light of the discovery of molecules produced by other type II methanotrophs that similarly bind and reduce copper (II) to copper (I).

Methylocella silvestris is a bacterium from the genus Methylocella spp which are found in many acidic soils and wetlands. Historically, Methylocella silvestris was originally isolated from acidic forest soils in Germany, and it is described as Gram-negative, aerobic, non-pigmented, non-motile, rod-shaped and methane-oxidizing facultative methanotroph. As an aerobic methanotrophic bacteria, Methylocella spp use methane (CH4), and methanol as their main carbon and energy source, as well as multi compounds acetate, pyruvate, succinate, malate, and ethanol. They were known to survive in the cold temperature from 4° to 30° degree of Celsius with the optimum at around 15° to 25 °C, but no more than 36 °C. They grow better in the pH scale between 4.5 to 7.0. It lacks intracytoplasmic membranes common to all methane-oxidizing bacteria except Methylocella, but contain a vesicular membrane system connected to the cytoplasmic membrane. BL2T (=DSM 15510T=NCIMB 13906T) is the type strain.

Alcanivorax pacificus is a pyrene-degrading marine gammaproteobacterium. It is of the genus Alcanivorax, a group of marine bacteria known for degrading hydrocarbons. When originally proposed, the genus Alcanivorax comprised six distinguishable species. However, A. pacificus, a seventh strain, was isolated from deep sea sediments in the West Pacific Ocean by Shanghai Majorbio Bio-pharm Technology Co., Ltd. in 2011. A. pacificus’s ability to degrade hydrocarbons can be employed for cleaning up oil-contaminated oceans through bioremediation. The genomic differences present in this strain of Alcanivorax that distinguish it from the original consortium are important to understand to better utilize this bacteria for bioremediation.

Methylobacter tundripaludum is a methane-oxidizing bacterium. It is Gram-negative, rod-shaped, non-motile, non-spore forming, with type strain SV96T. Its genome has been sequenced.

Xanthobacter autotrophicus is a Gram-negative, aerobic, pleomorphic and nitrogen-fixing bacterium from the family of Xanthobacteraceae which has been isolated from black pool sludge in Germany. Xanthobacter autotrophicus can utilize 1,2-dichloroethane, methanol and propane.

Streptomyces nogalater is a bacterium species from the genus of Streptomyces. Streptomyces nogalater produces nogalamycin.

Paenarthrobacter nitroguajacolicus is a bacterium species from the genus Paenarthrobacter which has been isolated from soil in the Czech Republic. Paenarthrobacter nitroguajacolicus has the ability to degrade 4-nitroguaiacol.

Methylocystis echinoides is a bacterium species from the genus of Methylocystis.

Methylocystis parvus is a methylotroph bacterium species from the genus of Methylocystis.

Methylosinus is a genus of bacteria from the family of Methylocystaceae.

Methylopila oligotropha is a methanotroph bacterium species from the genus of Methylopila which has been isolated from a groundwater aquifer.

Erythrobacter is a Gram-negative and rod-shaped bacteria genus from the family Erythrobacteraceae.

Methyloferula stellata is a Gram-negative and non-motile bacteria from the genus of Methyloferula which has been isolated from acidic peat soil from Arkhangelsk in Russia. In contrast to most known Methanotrophs Methyloferula stellata is an aerobic acidophilic methanotroph. This makes it similar to Methylocella species, however it is unable to grow on multicarbon substrates. It's genome was sequenced in March and April 2015.

References

  1. 1 2 LPSN lpsn.dsmz.de
  2. Straininfo of Methylosinus trichosporium
  3. UniProt
  4. 1 2 Stein, L. Y.; Yoon, S.; Semrau, J. D.; DiSpirito, A. A.; Crombie, A.; Murrell, J. C.; Vuilleumier, S.; Kalyuzhnaya, M. G.; Op den Camp, H. J. M.; Bringel, F.; Bruce, D.; Cheng, J.- F.; Copeland, A.; Goodwin, L.; Han, S.; Hauser, L.; Jetten, M. S. M.; Lajus, A.; Land, M. L.; Lapidus, A.; Lucas, S.; Medigue, C.; Pitluck, S.; Woyke, T.; Zeytun, A.; Klotz, M. G. (15 October 2010). "Genome Sequence of the Obligate Methanotroph Methylosinus trichosporium Strain OB3b". Journal of Bacteriology. 192 (24): 6497–6498. doi:10.1128/JB.01144-10. PMC   3008524 . PMID   20952571.
  5. editors, Don J. Brenner, Noel R. Krieg, James T. Staley (2005). Bergey's manual of systematic bacteriology (2nd ed.). New York: Springer. ISBN   978-0-387-29298-4.{{cite book}}: |last1= has generic name (help)CS1 maint: multiple names: authors list (link)
  6. 1 2 Whittenbury, R.; Phillips, K. C.; Wilkinson, J. F.YR 1970 (1970). "Enrichment, Isolation and Some Properties of Methane-utilizing Bacteria". Microbiology. 61 (2): 205–218. doi: 10.1099/00221287-61-2-205 . ISSN   1465-2080. PMID   5476891.{{cite journal}}: CS1 maint: numeric names: authors list (link)
  7. Knief, Claudia (2015-12-15). "Diversity and Habitat Preferences of Cultivated and Uncultivated Aerobic Methanotrophic Bacteria Evaluated Based on pmoA as Molecular Marker". Frontiers in Microbiology. 6: 1346. doi: 10.3389/fmicb.2015.01346 . ISSN   1664-302X. PMC   4678205 . PMID   26696968.
  8. 1 2 3 4 Sullivan, Jonathan P.; Dickinson, David; Chase, Howard A. (1998-01-01). "Methanotrophs, Methylosinus trichosporium OB3b, sMMO, and Their Application to Bioremediation". Critical Reviews in Microbiology. 24 (4): 335–373. doi:10.1080/10408419891294217. ISSN   1040-841X. PMID   9887367.
  9. 1 2 3 4 5 Phelps, Patricia A.; Agarwal, Sandeep K.; Speitel, Gerald E.; Georgiou, George (November 1992). "Methylosinus trichosporium OB3b Mutants Having Constitutive Expression of Soluble Methane Monooxygenase in the Presence of High Levels of Copper". Applied and Environmental Microbiology. 58 (11): 3701–3708. Bibcode:1992ApEnM..58.3701P. doi:10.1128/aem.58.11.3701-3708.1992. ISSN   0099-2240. PMC   183163 . PMID   16348810.
  10. Rodrigues, Andréa dos Santos; Valdman, Belkis; Salgado, Andréa Medeiros (June 2009). "Analysis of methane biodegradation by Methylosinus trichosporium OB3b". Brazilian Journal of Microbiology. 40 (2): 301–307. doi:10.1590/S1517-83822009000200017. ISSN   1517-8382. PMC   3769742 . PMID   24031362.

Further reading