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Applied and Environmental Microbiology, September 2000, p. 4136-4138, Vol. 66, No. 9
Max-Planck-Institut für terrestrische
Mikrobiologie, Karl-von-Frisch Strasse, 35043 Marburg, Germany
Received 5 May 2000/Accepted 30 June 2000
When cells of a type II methanotrophic bacterium
(Methylocystis strain LR1) were starved of methane, both
the Km(app) and the
Vmax(app) for methane decreased. The specific
affinity (aos) remained nearly
constant. Therefore, the decreased Km(app) in
starved cells was probably not an adjustment to better utilize low-methane concentrations.
Microbial oxidation of atmospheric
methane (CH4) takes place in most aerobic upland soils
(5, 10). Because these soils exhibit a lower half-saturation
constant [Km(app)] for CH4 than do
pure cultures of methanotrophic bacteria, it has been postulated that
the active bacteria are unknown species. These have been popularly
dubbed "high-affinity" methane oxidizers (5, 10).
Recently, a novel group of pmoA-like sequences was detected in several soils which oxidize atmospheric CH4 (11,
12), and incubation of soils under 14CH4
resulted in the labeling of signature phospholipid fatty acids which
differed from those of known type II methanotrophs (18). It
is therefore likely that as-yet-uncultured species are involved in
atmospheric CH4 uptake. However, it remains unknown whether atmospheric CH4 oxidation is limited to particular species
and whether these possess a specialized high-affinity CH4
oxidation enzyme.
We previously demonstrated that high-affinity CH4 oxidation
is probably not limited to uncultured methanotrophic groups. We enriched a methane-oxidizing bacterium (strain LR1) from an organic soil and identified it based on 16S rDNA, pmoA, and
mxaF gene sequences as a type II methanotrophic species of
the Methylosinus/Methylocystis cluster (8). Mixed
cultures containing strain LR1, when grown under <275 ppm volume
CH4, had a low Km(app) for
CH4 (56 to 188 nM) similar to the value measured in soil.
This increased to >1 µM when cells were grown under >1%
CH4. In the present study, we investigated the kinetics of
the isolated bacterium (culture is available upon request). Instead of
the time-consuming process of growing the organism under low
CH4 mixing ratios, we tested the effect of starving cells
of CH4.
Kinetics of strain LR1.
Culture was grown in liquid
nitrate-mineral salts (NMS) medium (8) under 10%
CH4. Purity was controlled microscopically and by plating
onto NMS agar, R2A agar, 10% strength Nutrient Agar, and 10% strength
AC Broth (Difco). After 1 to 2 months, the culture was diluted to about
109 cells ml
0099-2240/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.
Starvation Alters the Apparent Half-Saturation
Constant for Methane in the Type II Methanotroph
Methylocystis Strain LR1
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ABSTRACT
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TEXT
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Abstract
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References
1 with 0.5 mM phosphate buffer
(pH 6.0), and 7.5-ml amounts were added to 13-ml serum vials. The vials
were capped with sterile butyl rubber stoppers and incubated with
gentle shaking (6 rpm) at 25°C without added CH4. After 1 to 2 weeks, some vials were injected with CH4 to a final
mixing ratio of 1% and incubated for a further 24 h
("unstarved"). Others remained without CH4 ("starved"). Cell counts were made using a Neubauer chamber and showed that no population growth occurred during the 24-h incubation with 1% CH4 (data not shown).
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s) + kp]/[ks + k(
p)].
Limitation of reductant will decrease the reaction rate constant kp and in turn decrease
Km(app) (i.e., cause a higher apparent
affinity). The above model is a very simple explanation of the observed
variability. The truth may of course be more complex.
Bender and Conrad (2) observed that incubation of various
soils under 20% CH4 increased methanotrophic
Km(app) and Vmax(app)
values by 1 to 3 orders of magnitude, but increased methanotrophic cell
counts only 3- to 10-fold. When specific affinities were calculated
(Table 2), two of these soils (a meadow
cambisol and a cultivated cambisol) had a similar pattern as LR1
that
aos varied little despite large
changes (30- to 100-fold) of Km(app). A third
soil (forest luvisol) had a much lower
aos after enrichment than before,
suggesting that a different population had become active in
CH4-enriched soil. Comparisons must be cautiously made, but
these data suggest that the pattern noted in LR1 is applicable to some,
but not all, soils.
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ACKNOWLEDGMENTS |
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P.F.D. was supported by a stipendium from the Max Planck Society and a grant from the EC RTD Programme Biotechnology.
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FOOTNOTES |
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* Corresponding author. Mailing address: Max-Planck-Institut für terrestrische Mikrobiologie, Karl-von-Frisch Strasse, 35043 Marburg, Germany. Phone: (49) 6421-178-733. Fax: (49) 6421-178-809. E-mail: dunfield{at}mailer.uni-marburg.de.
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REFERENCES |
|---|
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|
|---|
| 1. | Andersen, B. L., G. Bidoglio, A. Leip, and D. Rembges. 1998. A new method to study simultaneous methane oxidation and methane production in soils. Global Biogeochem. Cycles 12:587-594[CrossRef]. |
| 2. | Bender, M., and R. Conrad. 1992. Kinetics of CH4 oxidation in oxic soils exposed to ambient air or high CH4 mixing ratios. FEMS Microbiol. Ecol. 101:261-270[CrossRef]. |
| 3. |
Benstead, J.,
G. M. King, and H. G. Williams.
1998.
Methanol promotes atmospheric methane oxidation by methanotrophic cultures and soils.
Appl. Environ. Microbiol.
64:1091-1098 |
| 4. |
Button, D. K.
1998.
Nutrient uptake by microorganisms according to kinetic parameters from theory as related to cytoarchitecture.
Microbiol. Mol. Biol. Rev.
62:636-645 |
| 5. |
Conrad, R.
1996.
Soil microorganisms as controllers of atmospheric trace gases (H2, CO, CH4, OCS, N2O, and NO).
Microbiol. Rev.
60:609-640 |
| 6. | Conrad, R. 2000. Soil microorganisms oxidizing atmospheric trace gases (CH4, CO, H2, NO). Ind. J. Microbiol. 39:193-203. |
| 7. | Dunfield, P. F., E. Topp, C. Archambault, and R. Knowles. 1995. Effect of nitrogen fertilizers and moisture content on CH4 and N2O fluxes in a humisol: measurements in the field and intact soil cores. Biogeochemistry 29:199-222[CrossRef]. |
| 8. |
Dunfield, P. F.,
W. Liesack,
T. Henckel,
R. Knowles, and R. Conrad.
1999.
High-affinity methane oxidation by a soil enrichment culture containing a type II methanotroph.
Appl. Environ. Microbiol.
65:1009-1014 |
| 9. | Gassner, G. T., and S. J. Lippard. 1999. Component interactions in the soluble methane monooxygenase system from Methylococcus capsulatus (Bath). Biochemistry 38:12768-12785[CrossRef][Medline]. |
| 10. |
Hanson, R. S., and T. E. Hanson.
1996.
Methanotrophic bacteria.
Microbiol. Rev.
60:439-471 |
| 11. |
Henckel, T.,
U. Jäckel,
S. Schnell, and R. Conrad.
2000.
Molecular analyses of novel methanotrophic communities in forest soil that oxidize atmospheric methane.
Appl. Environ. Microbiol.
66:1801-1808 |
| 12. |
Holmes, A. J.,
P. Roslev,
I. R. McDonald,
N. Iversen,
K. Henriksen, and J. C. Murrell.
1999.
Characterization of methanotrophic bacterial populations in soils showing atmospheric methane uptake.
Appl. Environ. Microbiol.
65:3312-3318 |
| 13. |
Jensen, S.,
A. Priemé, and L. Bakken.
1998.
Methanol improves methane uptake in starved methanotrophic microorganisms.
Appl. Environ. Microbiol.
64:1143-1146 |
| 14. | Joergensen, L., and H. Degn. 1983. Mass spectrometric measurements of methane and oxygen utilization by methanotrophic bacteria. FEMS Microbiol. Lett. 20:331-335[CrossRef]. |
| 15. |
Lontoh, S., and J. D. Semrau.
1998.
Methane and trichloroethylene degradation by Methylosinus trichosporium OB3b expressing particulate methane monooxygenase.
Appl. Environ. Microbiol.
64:1106-1114 |
| 16. | Macdonald, J. A., U. Skiba, L. J. Sheppard, K. J. Hargreaves, K. A. Smith, and D. Fowler. 1996. Soil environmental variables affecting the flux of methane from a range of forest, moorland and agricultural soils. Biogeochemistry 34:113-132. |
| 17. |
Nguyen, H. T.,
S. J. Elliott,
J. H. Yip, and S. I. Chan.
1998.
The particulate methane monooxygenase from Methylococcus capsulatus (Bath) is a novel copper-containing three-subunit enzyme.
J. Biol. Chem.
273:7957-7966 |
| 18. |
Roslev, P., and N. Iversen.
1999.
Radioactive fingerprinting of microorganisms that oxidize atmospheric methane in different soils.
Appl. Environ. Microbiol.
65:4064-4070 |
| 19. | Segel, I. H. 1993. Enzyme kinetics: behavior and analysis of rapid equilibrium and steady-state enzyme systems. John Wiley & Sons, Inc., New York, N.Y. |
| 20. |
Siegbahn, P. E. M.,
R. H. Crabtree, and P. Nordlund.
1998.
Mechanism of methane monooxygenase a structural and quantum chemical perspective.
J. Biol. Inorg. Chem.
3:314-317[CrossRef].
|
| 21. | Sipkema, E. M., W. de Koning, K. J. Ganzeveld, D. B. Janssen, and A. A. C. M. Beenackers. 1998. Experimental pulse technique for the study of microbial kinetics in continuous culture. J. Biotechnol. 64:159-176[CrossRef]. |
| 22. |
Yavitt, J. B.,
T. J. Fahey, and J. A. Simmons.
1995.
Methane and carbon dioxide dynamics in a northern hardwood ecosystem.
Soil Sci. Soc. Am. J.
59:796-804 |
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