Previous Article | Next Article 
Applied and Environmental Microbiology, February 2002, p. 1005-1009, Vol. 68, No. 2
0099-2240/02/$04.00+0 DOI: 10.1128/AEM.68.2.1005-1009.2002
Copyright © 2002, American Society for Microbiology. All Rights Reserved.
Tolerance and Metabolic Response of Acetogenic Bacteria toward Oxygen
Arno Karnholz, Kirsten Küsel, Anita Gößner, Andreas Schramm, and Harold L. Drake*
Department of Ecological Microbiology, BITOEK, University of Bayreuth, 95440 Bayreuth, Germany
Received 27 July 2001/
Accepted 13 November 2001

ABSTRACT
The acetogens
Sporomusa silvacetica,
Moorella thermoacetica,
Clostridium magnum,
Acetobacterium woodii, and
Thermoanaerobacter kivui (i) grew in both semisolid and liquid cultivation media
containing O
2 and (ii) consumed small amounts of O
2. Low concentrations
of O
2 caused a lag phase in growth but did not alter the ability
of these acetogens to synthesize acetate via the acetyl coenzyme
A pathway. Cell extracts of
S. silvacetica,
M. thermoacetica,
and
C. magnum contained peroxidase and NADH oxidase activities;
catalase and superoxide dismutase activities were not detected.

INTRODUCTION
Acetogens have been termed obligate or strict anaerobes. They
do not grow aerobically, are isolated mostly from anoxic habitats,
and utilize a pathway (the acetyl coenzyme A pathway) that contains
enzymes that are extremely sensitive to O
2 (
6,
7,
22). However,
acetogens (i) can be readily isolated from leaf litter and the
mineral soil of well-drained, oxic soils (
8,
9), (ii) can tolerate
periods of oxygenation in soils (
21), (iii) are active in termite
guts that have steep oxygen gradients (
20), and (iv) occur in
high numbers in transiently oxygenated rhizosphere sediments
colonized by sea grass (
12). These observations suggest that
certain acetogens must cope with O
2 under in situ conditions.
In preliminary studies, the classic acetogen
Moorella thermoacetica was found to reduce resazurin in O
2-supplemented medium (A.
Gößner and H. L. Drake, unpublished data), and the
objective of the present study was to determine the tolerance
and metabolic response of model acetogens toward O
2 (for a preliminary
report of this study, see A. Karnholz, K. Küsel, and H.
L. Drake, Abstr. 100th Gen. Meet. Am. Soc. Microbiol. 2000,
abstr. I-91, p. 401, 2000).

Organisms, media, and growth conditions.
The acetogens used in this study were selected because each
is a well-described model acetogen that has been isolated from
a different habitat. The temperatures of incubation for
Sporomusa silvacetica (DSM 10669; isolated from soil),
M. thermoacetica (DSM 1974; isolated from horse manure),
Clostridium magnum (DSM
2767; isolated from fresh water sediment),
Acetobacterium woodii (DSM 1030; isolated from a marine estuary), and
Thermoanaerobacter kivui (DSM 2030; isolated from lake sediment) were 30, 55, 30,
30, and 55°C, respectively. The acetogens were cultivated
in a carbonate-buffered, undefined (U) medium containing yeast
extract, vitamins, and trace metals but no reducing agents (
4).
Medium was dispensed under CO
2 into 27-ml crimp seal culture
tubes (7 ml of medium per tube) or 1-liter infusion bottles
(500 ml of medium per bottle; used for preparation of cell extracts),
which were then sealed and autoclaved; the pH was approximately
6.7. Anoxic aqueous stock solutions of glucose or fructose (prepared
under argon) were filter sterilized and added to the medium
by syringe injection by using O
2-free techniques. Culture tubes
and bottles containing liquid medium were incubated in a horizontal,
static position. Culture tubes were shaken vigorously before
optical densities were measured.
Escherichia coli K-12 (DSM
423) was cultivated aerobically in nutrient broth (8 g per liter;
Difco Laboratories, Detroit, Mich.) at pH 6.8 and 37°C.

Measurement of O2 in semisolid medium with microsensors.
Semisolid U medium was U medium supplemented with 5 g of Gelrite
(Carl Roth GmbH, Karlsruhe, Germany) per liter. The 27-ml crimp
seal culture tubes containing 10 ml of semisolid U medium were
autoclaved, cooled to approximately 50°C, and then inoculated
with 0.5 ml of freshly grown culture. As soon as the inoculated
medium had solidified at room temperature, sterile O
2 was injected
by syringe until a final concentration of 21% (vol/vol) was
reached. The tubes were incubated vertically, and O
2 in the
semisolid medium was measured with a microelectrode immediately
after the tubes were opened. The microelectrode setup consisted
of a micromanipulator-controlled O
x10 sensor (5- to 10-µm
tip diameter; Unisense, Aarhus, Denmark) and a PA 2000 picoammeter
(Unisense) that was attached to a strip chart recorder. The
microelectrode was calibrated with air-saturated (for 100% control)
and N
2-saturated (for 0% control) water that had the same temperature
as the culture tubes (i.e., either 30 or 55°C), and O
2 concentrations
were calculated according to standard tables (http://www.unisense.com/support/pdf/gas-tables.pdf).
The detection limit was 1 µM O
2. Since tubes were only
assayed once, a series of replicate tubes were inoculated for
each organism so that O
2 concentrations could be assessed periodically.

Enzyme assays and analytic methods.
Cell extracts were prepared under anoxic conditions (
10). Cell
extracts used for enzyme assays were obtained from cells grown
in U medium supplemented with 10 mM fructose (for
S. silvacetica)
or 10 mM glucose (for
M. thermoacetica and
C. magnum) and with
0.5% (vol/vol) O
2 in the gas phase. Catalase, peroxidase, NADH
oxidase, and superoxide dismutase activities were assayed according
to standard protocols (
1,
2,
18,
19) at room temperature (22°C).
The assays with extracts from
M. thermoacetica, however, were
conducted at 50°C. The catalase, peroxidase, NADH oxidase,
and superoxide dismutase activities are expressed, respectively,
in the following units: micromoles of H
2O
2 consumed per minute,
milligrams of pyrogallol oxidized per minute, micromoles of
NADH oxidized per minute, and micromoles of nitrotetrazolium
blue chloride not reduced per minute. Growth was measured as
the optical density at 660 nm (OD
660); the optical path width
(i.e., the inner diameter of the culture tubes) was 1.6 cm.
Uninoculated medium served as a reference. Protein in cell extracts
was determined colorimetrically (
3). The amounts of substrates
and products present in culture fluids and headspaces were determined
by high-performance liquid chromatography and gas chromatography
(
4,
11,
17). The results are representative of replicate experiments.

Effect of O2 on the growth of acetogens.
When nonreduced, semisolid medium was inoculated with
S. silvacetica,
M. thermoacetica,
C. magnum,
A. woodii, or
T. kivui and then
incubated with a gas phase that contained 21% (vol/vol) O
2 (equivalent
to the concentration of O
2 in air), the extent of the oxidized
surface of the medium was less in inoculated tubes than it was
in uninoculated controls (Fig.
1 and data not shown). Growth,
determined visually as an increase in opaqueness or in the formation
of colonies within the semisolid medium was apparent only in
the portions of the tubes with negligible O
2. For example, as
shown in Fig.
1C, the growth of
C. magnum at 12 h was apparent
at and below a depth of 13 mm, the portion of the tube where
O
2 was not detectable, but growth was not apparent between depths
of 0 and 12 mm, where O
2 was detectable. Culture tubes were
under positive pressure during incubation, and the slight increase
(i.e., peak) in the concentration of O
2 in the first few millimeters
of the semisolid medium was due to the initial release of O
2 as the medium equilibrated to atmospheric pressure when the
tubes were opened.
S. silvacetica,
M. thermoacetica,
C. magnum,
A. woodii, and
T. kivui also grew in nonreduced liquid culture medium containing
small amounts of O
2 in the gas phase (Fig.
2 and data not shown).
Increasing amounts of O
2 caused an increase in the lag phase
of growth and a decrease in the final optical densities achieved.
As illustrated by the large error bars in some of the growth
curves in Fig.
2, growth became less reproducible once the concentration
of O
2 became at least partially inhibitory. Of the five acetogens
tested,
A. woodii and
T. kivui were the most sensitive to O
2 and did not grow in nonreduced U medium when O
2 in the gas phase
exceeded 0.3 and 0.5% (vol/vol), respectively.

Metabolic response of acetogens to O2.
C. magnum displayed the shortest doubling times of the acetogens
examined (Fig.
2), so it was chosen for a detailed evaluation
of the potential effects of O
2 on the formation of products
during growth (Fig.
3). When the gas phase of cultures was supplemented
with approximately 1% O
2 (vol/vol), O
2 was consumed throughout
lag, log, and stationary phases of growth and trace levels of
H
2 were produced (Fig.
3A). O
2 was not consumed in uninoculated
controls. In contrast to the case with anoxic cultures, the
initial presence of O
2 in the gas phase of cultures caused a
delay in the conversion of glucose to acetate; however, the
final ratio of acetate produced to glucose consumed for both
anoxic controls and O
2-supplemented cultures approximated 3
(Fig.
3B), a value indicative of homoacetogenesis, C
6H
12O
6
3 CH
3COOH.
S. silvacetica,
M. thermoacetica,
A. woodii, and
T. kivui also
consumed low amounts of O
2 (Table
1 and data not shown). As
with
C. magnum, the presence of low amounts of O
2 did not alter
the ratios of acetate produced to glucose consumed for
S. silvacetica and
M. thermoacetica. Acetate-to-biomass ratios can be used
to evaluate the bioenergetics and growth efficiencies of acetogens
(
4). In general, the amount of acetate production that was required
for growth increased when the headspaces of cultures was supplemented
with O
2 (Table
1), indicating that maintenance energy requirements
increased in response to oxidative stress.

Enzyme activities possibly associated with aerotolerance.
Cell extracts of
S. silvacetica,
M. thermoacetica, and
C. magnum contained various levels of peroxidase (which consumes H
2O
2)
and NADH oxidase (which consumes O
2) activities; catalase (which
consumes H
2O
2) and superoxide dismutase (which consumes O
2·-)
activities were not detected (Table
2).

Concluding remarks.
The capacity of so-called strict anaerobes to tolerate and consume
trace levels of O
2 was first demonstrated for sulfate-reducing
bacteria (
16). Since acetogens occur in, and can be easily isolated
from, habitats that are subject to transient fluxes of O
2, it
is not surprising that acetogens have the ability to consume
low amounts of O
2 and to grow in medium supplemented with low
concentrations of O
2. In addition to the acetogens evaluated
in the present study,
Clostridium glycolicum RD-1, an abundant
culturable acetogen that inhabits the sea grass root, also displays
tolerance to O
2 (
13).
C. glycolicum RD-1 can tolerate up to
6% (vol/vol) O
2 in the headspace of cultures and undergoes a
metabolic shift towards classic ethanol and lactate fermentations
when challenged with oxic conditions (
13). It has recently been
reported that methanogens and acetogens that inhabit the termite
gut can likewise tolerate and consume traces of O
2 (
14; H. Boga
and A. Brune, Abstr. Annu. Meet. Verein. Allgem. Angewand. Mikrobiol.,
Biospectrum, Abstr. 15. P. 11. 33, p. 143, 2000).
The occurrence of NADH oxidase activity in cell extracts indicates that the acetogens tested can catalytically consume O2. O2 can yield H2O2 and O2·- within cells, and several enzymes are known to rid cells of these toxic products. Peroxidase activity was low but detectable. The absence of catalase and superoxide dismutase in acetogens was not entirely unexpected, since these enzymes produce O2. Rubrerythrin (which consumes H2O2) and rubredoxin oxidoreductase (which consumes O2·-) are alternative oxidative-stress defense proteins in the sulfate reducer Desulfovibrio vulgaris and do not produce O2 (15). Genes for similar proteins have been identified in M. thermoacetica (5). A full understanding of the biochemical processes that are responsible for the aerotolerance of acetogens will require additional investigations.

ACKNOWLEDGMENTS
We thank Carola Matthies for helpful discussions and evaluation
of the manuscript.
Support for this study was provided by the German Ministry of Education, Science, Research, and Technology (PT BEO 51-0339476C).

FOOTNOTES
* Corresponding author. Mailing address: Department of Ecological Microbiology, BITOEK, University of Bayreuth, 95440 Bayreuth, Germany. Phone: 49-0-921-555-640. Fax: 49-0-921-555-793. E-mail:
harold.drake{at}bitoek.uni-bayreuth.de.


REFERENCES
1
- Beauchamp, C., and I. Fridovich. 1971. Superoxide dismutase: improved assays and an assay applicable to acrylamide gels. Anal. Biochem. 44:276-287.[CrossRef][Medline]
2
- Beers, R. F., Jr., and I. W. Sizers. 1952. A spectrophotometric method for measuring the breakdown of hydrogen peroxide by catalase. J. Biol. Chem. 195:133.[Free Full Text]
3
- Bradford, M. M. 1976. A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. Anal. Biochem. 72:248-254.[CrossRef][Medline]
4
- Daniel, S. L., T. Hsu, S. I. Dean, and H. L. Drake. 1990. Characterization of the H2- and CO-dependent chemolithotrophic potentials of the acetogens Clostridium thermoaceticum and Acetogenium kivui. J. Bacteriol. 172:4464-4471.[Abstract/Free Full Text]
5
- Das, A., E. D. Coulter, D. M. Kurtz, Jr., and L. G. Ljungdahl. 2001. Five-gene cluster in Clostridium thermoaceticum consisting of two divergent operons encoding rubredoxin oxidoreductase-rubredoxin and rubrerythrintype A flavoproteinhigh-molecular-weight rubredoxin. J. Bacteriol. 183:1560-1567.[Abstract/Free Full Text]
6
- Drake, H. L. 1994. Acetogenesis, acetogenic bacteria, and the acetyl-CoA Wood/Ljungdahl pathway: past and current perspectives, p. 3-60. In H. L. Drake (ed.), Acetogenesis. Chapman and Hall, Inc., New York, N.Y.
7
- Drake, H. L., K. Küsel, and C. Matthies. Ecological consequences of the phylogenetic and physiological diversities of acetogens. Antonie Leeuwenhoek, in press.
8
- Gößner, A. S., R. Devereux, N. Ohnemüller, G. Acker, E. Stackebrandt, and H. L. Drake. 1999. Thermicanus aegyptius gen. nov., sp. nov., isolated from oxic soil, a fermentative microaerophile that grows commensally with the thermophilic acetogen Moorella thermoacetica. Appl. Environ. Microbiol. 65:5124-5133.[Abstract/Free Full Text]
9
- Kuhner, C. H., C. Frank, A. Grießhammer, M. Schmittroth, G. Acker, A. Gößner, and H. L. Drake. 1997. Sporomusa silvacetica sp. nov., an acetogenic bacterium isolated from aggregated forest soil. Int. J. Syst. Bacteriol. 47:352-358.[Abstract/Free Full Text]
10
- Kuhner, C. H., C. Matthies, G. Acker, M. Schmittroth, A. S. Gößner, and H. L. Drake. 2000. Clostridium akagii sp. nov. and Clostridium acidisoli sp. nov.: acid-tolerant, N2-fixing clostridia isolated from acidic forest soil and litter. Int. J. Syst. Evol. Microbiol. 50:873-881.[Abstract]
11
- Küsel, K., and H. L. Drake. 1995. Effects of environmental parameters on the formation and turnover of acetate by forest soils. Appl. Environ. Microbiol. 61:3667-3675.[Abstract]
12
- Küsel, K., H. C. Pinkart, H. L. Drake, and R. Devereux. 1999. Acetogenic and sulfate-reducing bacteria inhabiting the rhizoplane and deep cortex cells of the sea grass Halodule wrightii. Appl. Environ. Microbiol. 65:5117-5123.[Abstract/Free Full Text]
13
- Küsel, K., A. Karnholz, T. Trinkwalter, R. Devereux, G. Acker, and H. L. Drake. 2001. Physiological ecology of Clostridium glycolicum RD-1, an aerotolerant acetogen isolated from sea grass roots. Appl. Environ. Microbiol. 67:4734-4741.[Abstract/Free Full Text]
14
- Leadbetter, J. R., and J. A. Breznak. 1996. Physiological ecology of Methanobrevibacter cuticularis sp. nov. and Methanobrevibacter curvatus sp. nov., isolated from the hindgut of the termite Reticulitermes flavipes. Appl. Environ. Microbiol. 62:3620-3631.[Abstract]
15
- Lumppio, H. L., N. V. Shenvi, A. O. Summers, G. Voordouw, and D. M. Kurtz, Jr. 2001. Rubrerythrin and rubredoxin oxidoreductase in Desulfovibrio vulgaris: a novel oxidative stress protection system. J. Bacteriol. 183:101-108.[Abstract/Free Full Text]
16
- Marschall, C., P. Frenzel, and H. Cypionka. 1993. Influence of oxygen on sulfate reduction and growth of sulfate-reducing bacteria. Arch. Microbiol. 159:168-173.[CrossRef]
17
- Matthies, C., A. Freiberger, and H. L. Drake. 1993. Fumarate dissimilation and differential reductant flow by Clostridium formicoaceticum and Clostridium aceticum. Arch. Microbiol. 160:273-278.[CrossRef]
18
- Stanton, T. B., and N. S. Jensen. 1993. Purification and characterization of NADH oxidase from Serpulina (Treponema) hyodysenteriae. J. Bacteriol. 175:2980-2987.[Abstract/Free Full Text]
19
- Stellmach, B., W. Gottschick, F. Battermann, and K. Zabel. 1988. Bestimmungsmethoden enzyme, p. 222-223. Steinkopff Verlag, Darmstadt, Germany.
20
- Tholen, A., and A. Brune. 1999. Localization and in situ activities of homoacetogenic bacteria in the highly compartmentalized hindgut of soil-feeding higher termites (Cubitermes spp.). Appl. Environ. Microbiol. 65:4497-4505.[Abstract/Free Full Text]
21
- Wagner, C., A. Grießhammer, and H. L. Drake. 1996. Acetogenic capacities and the anaerobic turnover of carbon in a Kansas prairie soil. Appl. Environ. Microbiol. 62:494-500.[Abstract]
22
- Wood, H. G., and L. G. Ljungdahl. 1991. Autotrophic character of acetogenic bacteria, p. 201-250. In J. M. Shively and L. L. Barton (ed.), Variations in autotrophic life. Academic Press, San Diego, Calif.
Applied and Environmental Microbiology, February 2002, p. 1005-1009, Vol. 68, No. 2
0099-2240/02/$04.00+0 DOI: 10.1128/AEM.68.2.1005-1009.2002
Copyright © 2002, American Society for Microbiology. All Rights Reserved.
This article has been cited by other articles:
-
Balk, M., van Gelder, T., Weelink, S. A., Stams, A. J. M.
(2008). (Per)chlorate Reduction by the Thermophilic Bacterium Moorella perchloratireducens sp. nov., Isolated from Underground Gas Storage. Appl. Environ. Microbiol.
74: 403-409
[Abstract]
[Full Text]
-
Kawasaki, S., Mimura, T., Satoh, T., Takeda, K., Niimura, Y.
(2006). Response of the Microaerophilic Bifidobacterium Species, B. boum and B. thermophilum, to Oxygen. Appl. Environ. Microbiol.
72: 6854-6858
[Abstract]
[Full Text]
-
Gossner, A. S., Kusel, K., Schulz, D., Trenz, S., Acker, G., Lovell, C. R., Drake, H. L.
(2006). Trophic interaction of the aerotolerant anaerobe Clostridium intestinale and the acetogen Sporomusa rhizae sp. nov. isolated from roots of the black needlerush Juncus roemerianus.. Microbiology
152: 1209-1219
[Abstract]
[Full Text]
-
Kawasaki, S., Watamura, Y., Ono, M., Watanabe, T., Takeda, K., Niimura, Y.
(2005). Adaptive Responses to Oxygen Stress in Obligatory Anaerobes Clostridium acetobutylicum and Clostridium aminovalericum. Appl. Environ. Microbiol.
71: 8442-8450
[Abstract]
[Full Text]
-
Das, A., Silaghi-Dumitrescu, R., Ljungdahl, L. G., Kurtz, D. M. Jr.
(2005). Cytochrome bd Oxidase, Oxidative Stress, and Dioxygen Tolerance of the Strictly Anaerobic Bacterium Moorella thermoacetica. J. Bacteriol.
187: 2020-2029
[Abstract]
[Full Text]
-
Matsui, G. Y., Ringelberg, D. B., Lovell, C. R.
(2004). Sulfate-Reducing Bacteria in Tubes Constructed by the Marine Infaunal Polychaete Diopatra cuprea. Appl. Environ. Microbiol.
70: 7053-7065
[Abstract]
[Full Text]
-
Kato, S., Haruta, S., Cui, Z. J., Ishii, M., Yokota, A., Igarashi, Y.
(2004). Clostridium straminisolvens sp. nov., a moderately thermophilic, aerotolerant and cellulolytic bacterium isolated from a cellulose-degrading bacterial community. Int. J. Syst. Evol. Microbiol.
54: 2043-2047
[Abstract]
[Full Text]
-
Graber, J. R., Breznak, J. A.
(2004). Physiology and Nutrition of Treponema primitia, an H2/ CO2-Acetogenic Spirochete from Termite Hindguts. Appl. Environ. Microbiol.
70: 1307-1314
[Abstract]
[Full Text]
-
Parshina, S. N., Kleerebezem, R., Sanz, J. L., Lettinga, G., Nozhevnikova, A. N., Kostrikina, N. A., Lysenko, A. M., Stams, A. J. M.
(2003). Soehngenia saccharolytica gen. nov., sp. nov. and Clostridium amygdalinum sp. nov., two novel anaerobic, benzaldehyde-converting bacteria. Int. J. Syst. Evol. Microbiol.
53: 1791-1799
[Abstract]
[Full Text]
-
Boga, H. I., Ludwig, W., Brune, A.
(2003). Sporomusa aerivorans sp. nov., an oxygen-reducing homoacetogenic bacterium from the gut of a soil-feeding termite. Int. J. Syst. Evol. Microbiol.
53: 1397-1404
[Abstract]
[Full Text]
-
Boga, H. I., Brune, A.
(2003). Hydrogen-Dependent Oxygen Reduction by Homoacetogenic Bacteria Isolated from Termite Guts. Appl. Environ. Microbiol.
69: 779-786
[Abstract]
[Full Text]
-
Leaphart, A. B., Friez, M. J., Lovell, C. R.
(2002). Formyltetrahydrofolate Synthetase Sequences from Salt Marsh Plant Roots Reveal a Diversity of Acetogenic Bacteria and Other Bacterial Functional Groups. Appl. Environ. Microbiol.
69: 693-696
[Abstract]
[Full Text]