Methane is one of the most important greenhouse gases, and its concentration in the atmosphere is increasing by approximately 1% per year (16). Methane-oxidizing bacteria, or methanotrophs, are a key group of bacteria involved in the global methane cycle and can be found in many environments. For example, they limit the efflux of methane produced in flooded soils and wetlands and consume atmospheric methane directly in aerated upland soils (2, 14). Methanotrophs have generally been considered to be obligate in nature, i.e., growing only on methane as their sole source of carbon and energy. In this issue of the Journal of Bacteriology, Dedysh and colleagues provide the first unequivocal proof of a genus of methanotrophic bacteria (Methylocella) that are capable of growth on a number of multicarbon substrates, dispelling the notion that methanotrophy is an obligate phenomenon (6). In a century of research since the Dutch microbiologist Söhngen described the first methanotroph, Bacillus methanicus, in 1906 (25), significant advances in understanding the ecology and physiology of these organisms have contributed to our understanding of methane cycling in the environment. A brief history of the field will allow the reader to appreciate the nature of this highly controversial topic in the field of bacterial one-carbon metabolism.
Claims for the existence of facultative methanotrophs (i.e., methanotrophs capable of growth on multicarbon as well as one-carbon substrates) have a long and somewhat checkered history dating back almost 30 years, when Patt et al. first isolated (22) and later described (23) Methylobacterium organophilum, which was able to grow on methane or glucose. This was followed by other reports of facultative methanotrophs, notably strain R6, Methylobacterium ethanolicum, and Methylomonas sp. strain 761M (18, 21, 32). In most cases, either the methane-oxidizing capacity was lost or the results were not substantiated in other laboratories. For example, for M. organophilum it was hypothesized that methane oxidation genes were plasmid encoded and that the loss of growth on methane was attributable to loss of a plasmid. In the case of M. ethanolicum, the culture was shown to be a very tight syntrophic association between a methanotroph and a Xanthobacter species (17). The controversy surrounding facultative methanotrophs was recently highlighted by the description of a “methane-oxidizing” methylotroph, Methylobacterium populi, and the rebuttal that followed (5, 28). Thankfully, doubts about the existence of facultative methanotrophs seem finally to have been dispelled by the meticulous experiments performed by Dedysh et al. (6). Quantitative real-time PCR targeting the mmoX gene, which encodes the hydroxylase component of the soluble methane monooxygenase (sMMO), the key enzyme for methane oxidation in Methylocella silvestris BL2, showed a parallel increase of copies of mmoX and microscopic cell counts in both methane- and acetate-grown cultures. In addition to fluorescence in situ hybridization using strain- and genus-specific oligonucleotide probes, most-probable-number dilution experiments ruled out the possibility of a contaminant present at low numbers which could catabolize the acetate and provide a carbon source for the dominant Methylocella population.
The cause or causes of obligate methanotrophy remain elusive despite decades of research on this subject, although several hypotheses have been investigated (31). Experiments performed on whole-cell suspensions and cell extracts have shown that the failure of obligate methanotrophs to grow on multicarbon substrates such as acetate, as well as amino acids and sugars, was not necessarily due to their inability to transport the substrates into the cell (11, 12, 24). The observation of specific metabolic lesions in methanotrophic bacteria, such as the absence of alpha-ketoglutarate dehydrogenase activity in type I methanotrophs, is the most likely explanation, although the question remains as to how or why these lesions arose. To complicate things further, the recently released genome sequence of Methylococcus capsulatus (Bath) revealed that the genes encoding alpha-ketoglutarate dehydrogenase were indeed present and apparently complete, although there is as yet no evidence for expression of an active enzyme (29, 31). Type II methanotrophs such as Methylocella have also been shown to lack activity of the glyoxylate cycle enzymes isocitrate lyase and malate synthase (10). Therefore, we can only speculate about whether Methylocella species use an alternative pathway for growth on acetate or whether appropriate enzyme assay conditions have not yet been found. Another interesting observation is the apparent reduced growth yields of Methylocella grown on methane as the sole substrate compared to other serine pathway methanotrophs. This may indicate a reduced efficiency of energy generation from methane, but further investigation will be necessary to determine if this is the price a facultative methanotroph pays for being more metabolically versatile.
Our outlook on methane cycling in the environment may also be outdated: our previous understanding of methanotroph physiology did not take into account the effect of multicarbon substrates on methanotrophic activity. This is highlighted by the authors' observations on the addition of acetate to a methane-grown culture of Methylocella: although the initial effect of acetate addition was to inhibit methane oxidation, the longer-term consequence was a stimulatory effect on methane oxidation (6). Previously, the positive effect of acetate addition to a tundra soil on methane oxidation was attributed to increased activity of methanogens, resulting in an indirect stimulation of the methanotrophic community (30). The discovery of facultative Methylocella species suggests that these findings need to be reappraised. Indeed, acetate is a major intermediate in carbon turnover in soil and is a major end product of anaerobic metabolism in wetlands (9, 15). Methylocella inhabits acidic wetlands and forest soils, which account for a large proportion of methane emissions globally (8, 13, 19), and thus Methylocella and potentially other, as-yet-unknown facultative methanotrophs may be major players in methane cycling in these environments and thus globally. There have been no reports on the isolation of methanotrophs capable of oxidizing methane at atmospheric concentrations, but it is tempting to speculate that since Dedysh et al. have shown that the threshold of methane oxidation was lowered following acetate addition in Methylocella (6), this type of mechanism might enable other, as-yet-undescribed facultative methanotrophs to oxidize methane at atmospheric concentrations.
These recently confirmed metabolic traits may also offer interesting new biotechnological potential for facultative methanotrophs such as Methylocella. Methylocella apparently possesses only the sMMO and not the particulate MMO (pMMO), which has been found in all other methanotrophs thus far examined (4, 7, 10, 20). The sMMO enzyme, which is found in some but not all methanotrophs that also possess a pMMO, has attracted considerable attention due to its catalytic versatility and the ability to oxidize a wide range of substrates, including alkanes, alkenes, alicyclics, aromatics, ethers, and heterocyclics (1) and several important environmental contaminants such as the halogenated hydrocarbons trichloroethylene and chloroform. These compounds are not carbon and energy sources for methanotrophs but are fortuitously cooxidized by sMMO (3, 27). In all other methanotrophs containing sMMO, copper-mediated regulation results in expression of sMMO only under low copper-to-biomass ratio growth conditions, while pMMO is expressed under high copper-to-biomass ratio conditions (26). The pMMO, in comparison to the sMMO, however, cooxidizes only a relatively narrow range of substrates such as short-chain alkanes and alkenes, in addition to oxidizing methane. Thus, Methylocella is potentially attractive from a biotechnological viewpoint in that expression of sMMO in this methanotroph might not be repressed by copper ions in the environment. One could easily envisage the benefits of stimulating indigenous or augmented Methylocella populations with acetate for bioremediation of contaminated sites. It is noteworthy, however, that the lack of pMMO in Methylocella remains a contentious issue, and the evidence presented thus far by Dedysh et al. (7) seems to be insufficient to rule out completely the presence of pMMO or an alternative methane-oxidizing system to sMMO in Methylocella.
In summary, Dedysh et al. have made an important contribution in the field of one-carbon metabolism by describing the first fully authenticated facultative methanotroph (6). This unique capacity to grow on multicarbon substrates has major implications for our outlook on methane cycling in the environment and the notion that methanotrophy is an exclusively obligate phenomenon. Future work addressing the molecular physiology of these organisms, particularly the regulation of the methane-oxidizing machinery during growth on multicarbon substrates, is essential to advance our understanding of methane cycling in the environment and to improve the possibilities of exploiting the unique characteristics of Methylocella and other facultative methanotrophs. The availability of the genome sequence of M. silvestris BL2 would further enhance such molecular physiological studies.
Acknowledgments
We gratefully acknowledge D. P. Kelly for his comments on the manuscript.
The views expressed in this Commentary do not necessarily reflect the views of the journal or of ASM.
REFERENCES
- 1.Colby, J., D. I. Stirling, and H. Dalton. 1977. The soluble methane mono-oxygenase of Methylococcus capsulatus (Bath). Its ability to oxygenate n-alkanes, n-alkenes, ethers, and alicyclic, aromatic and heterocyclic compounds. Biochem. J. 165:395-402. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 2.Conrad, R. 1996. Soil microorganisms as controllers of atmospheric trace gases (H2, CO, CH4, OCS, N2O, and NO). Microbiol. Rev. 60:609-640. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 3.Dalton, H., and D. I. Stirling. 1982. Co-metabolism. Phil. Trans. R. Soc. London B 297:481-496. [DOI] [PubMed] [Google Scholar]
- 4.Dedysh, S. N., Y. Y. Berestovskaya, L. V. Vasylieva, S. E. Belova, V. N. Khmelenina, N. E. Suzina, Y. A. Trotsenko, W. Liesack, and G. A. Zavarzin. 2004. Methylocella tundrae sp. nov., a novel methanotrophic bacterium from acidic tundra peatlands. Int. J. Syst. Evol. Microbiol. 54:151-156. [DOI] [PubMed] [Google Scholar]
- 5.Dedysh, S. N., P. F. Dunfield, and Y. A. Trotsenko. 2004. Methane utilization by Methylobacterium species: new evidence but still no proof for an old controversy. Int. J. Syst. Evol. Microbiol. 54:1919-1920. [DOI] [PubMed] [Google Scholar]
- 6.Dedysh, S. N., C. Knief, and P. F. Dunfield. 2005. Methylocella species are facultatively methanotrophic. J. Bacteriol. 187:4665-4670. [DOI] [PMC free article] [PubMed]
- 7.Dedysh, S. N., W. Liesack, V. N. Khmelenina, N. E. Suzina, Y. A. Trotsenko, J. D. Semrau, A. M. Bares, N. S. Panikov, and J. M. Tiedje. 2000. Methylocella palustris gen. nov., sp nov., a new methane-oxidizing acidophilic bacterium from peat bogs, representing a novel subtype of serine-pathway methanotrophs. Int. J. Syst. Evol. Microbiol. 50:955-969. [DOI] [PubMed] [Google Scholar]
- 8.Dedysh, S. N., N. S. Panikov, W. Liesack, R. Grosskopf, J. Z. Zhou, and J. M. Tiedje. 1998. Isolation of acidophilic methane-oxidizing bacteria from northern peat wetlands. Science 282:281-284. [DOI] [PubMed] [Google Scholar]
- 9.Duddleston, K. N., M. A. Kinney, R. P. Kiene, and M. E. Hines. 2002. Anaerobic microbial biogeochemistry in a northern bog: acetate as a dominant metabolic endproduct. Glob. Biogeochem. Cycl. 16:1063. [Google Scholar]
- 10.Dunfield, P. F., V. N. Khmelenina, N. E. Suzina, Y. A. Trotsenko, and S. N. Dedysh. 2003. Methylocella silvestris sp nov., a novel methanotroph isolated from an acidic forest cambisol. Int. J. Syst. Evol. Microbiol. 53:1231-1239. [DOI] [PubMed] [Google Scholar]
- 11.Eccleston, M., and D. P. Kelly. 1972. Assimilation and toxicity of some exogenous amino acids in the methane-oxidizing bacterium Methylococcus capsulatus. J. Gen. Microbiol. 71:541-554. [DOI] [PubMed] [Google Scholar]
- 12.Eccleston, M., and D. P. Kelly. 1973. Assimilation and toxicity of some exogenous C-1 compounds, alcohols, sugars and acetate in the methane-oxidizing bacterium Methylococcus capsulatus. J. Gen. Microbiol. 75:211-221. [DOI] [PubMed] [Google Scholar]
- 13.Fung, I., J. John, J. Lerner, E. Matthews, M. Prather, L. P. Steele, and P. J. Fraser. 1991. 3-dimensional model synthesis of the global methane cycle. J. Geophys. Res. Atmos. 96:13033-13065. [Google Scholar]
- 14.Hanson, R. S., and T. E. Hanson. 1996. Methanotrophic bacteria. Microbiol. Rev. 60:439-471. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.Kusel, K., and H. L. Drake. 1999. Microbial turnover of low molecular weight organic acids during leaf litter decomposition. Soil Biol. Biochem. 31:107-118. [Google Scholar]
- 16.Lelieveld, J., P. J. Crutzen, and C. Bruhl. 1993. Climate effects of atmospheric methane. Chemosphere 26:739-768. [Google Scholar]
- 17.Lidstrom O' Connor, M. E., G. L. Fulton, and A. E. Wopat. 1983. ‘Methylobacterium ethanolicum’—a syntrophic association of two methylotrophic bacteria. J. Gen. Microbiol. 129:3139-3148. [Google Scholar]
- 18.Lynch, M. J., A. E. Wopat, and M. L. O'Connor. 1980. Characterization of two new facultative methanotrophs. Appl. Environ. Microbiol. 40:400-407. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 19.Matthews, E., and I. Fung. 1987. Methane emission from natural wetlands: global distribution, area, and environmental characteristics of sources. Glob. Biogeochem. Cycl. 1:61-86. [Google Scholar]
- 20.Murrell, J. C., I. R. McDonald, and B. Gilbert. 2000. Regulation of expression of methane monooxygenases by copper ions. Trends Microbiol. 8:221-225. [DOI] [PubMed] [Google Scholar]
- 21.Patel, R. N., C. T. Hou, and A. Felix. 1978. Microbial oxidation of methane and methanol: isolation of methane-utilizing bacteria and characterization of a facultative methane-utilizing isolate. J. Bacteriol. 136:352-358. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 22.Patt, T. E., G. C. Cole, J. Bland, and R. S. Hanson. 1974. Isolation and characterization of bacteria that grow on methane and organic compounds as sole sources of carbon and energy. J. Bacteriol. 120:955-964. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 23.Patt, T. E., G. C. Cole, and R. S. Hanson. 1976. Methylobacterium, a new genus of facultatively methylotrophic bacteria. Int. J. Syst. Bacteriol. 26:226-229. [Google Scholar]
- 24.Shishkina, V. N., and Y. A. Trotsenko. 1982. Multiple enzymic lesions in obligate methanotrophic bacteria. FEMS Microbiol. Lett. 13:237-242. [Google Scholar]
- 25.Söhngen, N. L. 1906. Ueber Bakterien, welche Methan als Kohlenstoffnahrung und Energiequelle gebrauchen. Centralbl. Bakteriol. Parasitenk. Infektionskr. Hyg. Abt. II 15:513-517. [Google Scholar]
- 26.Stanley, S. H., S. D. Prior, D. J. Leak, and H. Dalton. 1983. Copper stress underlies the fundamental change in intracellular location of methane monooxygenase in methane oxidizing organisms—studies in batch and continuous cultures. Biotechnol. Lett. 5:487-492. [Google Scholar]
- 27.Stirling, D. I., and H. Dalton. 1979. The fortuitous oxidation and cometabolism of various carbon compounds by whole-cell suspensions of Methylococcus capsulatus (Bath). FEMS Microbiol. Lett. 5:315-318. [Google Scholar]
- 28.Van Aken, B., C. M. Peres, S. L. Doty, J. M. Yoon, and J. L. Schnoor. 2004. Methylobacterium populi sp nov., a novel aerobic, pink-pigmented, facultatively methylotrophic, methane-utilizing bacterium isolated from poplar trees (Populus deltoides × nigra DN34). Int. J. Syst. Evol. Microbiol. 54:1191-1196. [DOI] [PubMed] [Google Scholar]
- 29.Ward, N., O. Larsen, J. Sakwa, L. Bruseth, H. Khouri, A. S. Durkin, et al. 2004. Genomic insights into methanotrophy: the complete genome sequence of Methylococcus capsulatus (Bath). PLoS. Biol. 2:1616-1628. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.West, A. E., and S. K. Schmidt. 1999. Acetate stimulates atmospheric CH4 oxidation by an alpine tundra soil. Soil Biol. Biochem. 31:1649-1655. [Google Scholar]
- 31.Wood, A. P., J. P. Aurikko, and D. P. Kelly. 2004. A challenge for 21st century molecular biology and biochemistry: what are the causes of obligate autotrophy and methanotrophy? FEMS Microbiol. Rev. 28:335-352. [DOI] [PubMed] [Google Scholar]
- 32.Zhao, S. J., and R. S. Hanson. 1984. Variants of the obligate methanotroph isolate 761M capable of growth on glucose in the absence of methane. Appl. Environ. Microbiol. 48:807-812. [DOI] [PMC free article] [PubMed] [Google Scholar]
