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Applied and Environmental Microbiology, April 2004, p. 2525-2528, Vol. 70, No. 4
0099-2240/04/$08.00+0 DOI: 10.1128/AEM.70.4.2525-2528.2004
Copyright © 2004, American Society for Microbiology. All Rights Reserved.
Geobacter sulfurreducens Can Grow with Oxygen as a Terminal Electron Acceptor
W. C. Lin, M. V. Coppi, and D. R. Lovley*
Department of Microbiology, University of Massachusetts, Amherst, Massachusetts 01003
Received 21 October 2003/
Accepted 31 December 2003

ABSTRACT
Geobacter sulfurreducens, previously classified as a strict
anaerobe, tolerated exposure to atmospheric oxygen for at least
24 h and grew with oxygen as the sole electron acceptor at concentrations
of 10% or less in the headspace. These results help explain
how
Geobacter species may survive in oxic subsurface environments,
being poised to rapidly take advantage of the development of
anoxic conditions.

INTRODUCTION
Geobacter species have previously been considered strict anaerobes
(
4,
18,
19). However, when organic electron donors are introduced
into previously oxic subsurface sediments in order to stimulate
anaerobic dissimilatory metal reduction,
Geobacter species rapidly
become the predominant Fe(III)-reducing microorganisms in a
diversity of subsurface sediments (
2,
13,
29). Thus, it appears
that there is a reservoir of
Geobacter species in oxic aquifers.
The ability of strict anaerobes to survive under oxic conditions is not unprecedented. Many anaerobes contain enzymes, such as superoxide reductase (14), superoxide dismutase (23), and NADH oxidase (32), which permit them to tolerate oxygen exposure. Some organisms generally regarded as anaerobes also have the ability to lower the oxygen concentration in their surroundings. For example, homoacetogenic bacteria isolated from termite guts oxidized hydrogen with the reduction of oxygen and thereby established favorable conditions for growth (3). Desulfovibrio species, which, like Geobacter species, are
-Proteobacteria, can survive oxygen exposure (1, 11) and express oxidative-stress enzymes such as superoxide dismutases (10, 12), superoxide reductases (28), and ruberythrin or rubredoxin oxidoreductase (21). Desulfovibrio species also contain enzymes that can reduce oxygen (5, 16, 23) and, in some cases, conserve energy from oxygen reduction (8, 9). However, no examples of sustained growth by Desulfovibrio species with oxygen as the electron acceptor have been documented.
The sequence of the Geobacter sulfurreducens genome has revealed many previously unsuspected metabolic capabilities of this organism (6, 17, 22). Genes predicted to code for proteins involved in response to oxidative stress, such as rubredoxins, A-type flavodoxins, catalase, superoxide dismutase, and superoxide reductase, are readily apparent (22) and perhaps not unexpected. More surprising is the presence of genes appearing to encode a terminal cytochrome c oxidase, suggesting that G. sulfurreducens might have the ability to utilize oxygen as a terminal electron acceptor (22).

Survival in atmospheric oxygen.
In order to determine the ability of
G. sulfurreducens to tolerate
oxygen exposure, mid-log-phase cultures were grown at 30°C
under N
2 in a 3-(N-morpholino)propanesulfonic acid (MOPS)-buffered
(20 mM, pH 7.0) variation of the previously described acetate-fumarate
medium (
7). The cells were then diluted 10-fold into the aerobically
prepared MOPS-acetate-fumarate medium and shaken under air.
Following exposure to air for various periods of time, the cells
were diluted another 10-fold into an anoxic MOPS-acetate-fumarate
medium that was supplemented with 1 mM cysteine and 0.5% yeast
extract and were incubated at 30°C. Exposure to atmospheric
oxygen resulted in only a slight increase in the lag phase prior
to the onset of anaerobic growth (Fig.
1). Furthermore, the
length of the lag phase was not significantly affected by the
duration of the exposure to air. These results demonstrate that
G. sulfurreducens is aerotolerant.

Growth with oxygen as the sole electron acceptor.
In order to determine whether
G. sulfurreducens is able to grow
with oxygen as the sole electron acceptor,
G. sulfurreducens was grown in a modification of the previously described anoxic,
bicarbonate-buffered medium (
7) with excess acetate (15 mM)
as the electron donor and limiting fumarate (20 mM) as the electron
acceptor. Cysteine and resazurin were omitted from the medium.
The atmosphere overlying the medium was He-CO
2 (80:20). Cultures
were grown in 1.1-liter bottles in a manner similar to the method
described by Dilling and Cypionka (
9), with 200 ml of medium
at 30°C with shaking at 45 rpm. Acetate and fumarate concentrations
were measured with a liquid chromatograph (model SPD-10A; Shimadzu,
Kyoto, Japan) equipped with a 100- by 7.8-mm Aminex Fast Acid
column (Bio-Rad, Hercules, Calif.) with an 8 mM H
2SO
4 mobile
phase at a flow rate of 0.5 ml/min. Oxygen concentration in
the headspace was measured with a Hewlett-Packard series HP6890
gas chromatograph equipped with a thermal conductivity detector
(Agilent Technologies, Inc., Albany, N.Y.) and a Carboxen 1010
PLOT capillary column (Supelco, Bellefonte, Pa.). The temperatures
of the detector, injector, and column were 230, 230, and 40°C,
respectively. Cell number was determined with acridine orange
staining and epifluorescence microscopy, as previously described
(
20). When a 2% inoculum of mid-log-phase cells grown in anoxic
acetate-fumarate medium was added to fresh anoxic medium, the
cells consumed acetate and grew to an absorbance of ca. 0.3
within 2 days (Fig.
2A). At this point, all of the fumarate
in the medium had been consumed, and no further growth was observed
unless the medium was amended with additional fumarate (data
not shown). When oxygen was added to the headspace at an initial
concentration of 5 or 10%,
G. sulfurreducens grew, as was indicated
by an increase in absorbance (Fig.
2A) and a net increase of
1.93
x 10
8 and 2.82
x 10
8 cells/ml, respectively. Cell growth
was accompanied by the concurrent consumption of acetate and
oxygen (Fig.
2). If the concentration of oxygen was increased
to 15 or 20%, oxygen consumption stopped within a day and cell
growth was less than that with 5% oxygen, suggesting that aerobic
growth could not be sustained at these higher oxygen levels.
In order to determine if sustained growth on acetate and oxygen
was possible, cells were initially grown on acetate with 5 mM
fumarate as the electron acceptor; this was followed by oxygen
addition after fumarate was depleted. Growth on acetate and
oxygen continued for 10 days with multiple additions of 5% oxygen
and 15 mM acetate (Fig.
3). When 10% oxygen was added, growth
stopped after the second addition. However, growth could be
sustained after an initial addition of 10% oxygen if 5% oxygen
was used for subsequent additions (data not shown).
Growth on oxygen required that the cells be pregrown on fumarate.
There was no growth when either anaerobically grown cells or
cells that had been grown with 5 or 10% oxygen were inoculated
directly into fresh medium with 5%, 10%, or atmospheric oxygen,
even when the medium was supplemented with organic acids that
were present in the fumarate-grown cultures, such as succinate
and malate.
The stoichiometry of oxygen to acetate consumption was 2.4 ± 0.8 (mean ± standard deviation from four replicate experiments, as determined from the results shown in Fig. 2 and 3) for the cultures grown with an initial oxygen concentration of 5%, and there was no growth on oxygen in acetate-depleted cultures. These results suggest that acetate was oxidized to carbon dioxide, with oxygen serving as the sole electron acceptor according to the reaction CH3COOH + 2O2
2CO2 + 2H2O. In comparison, the stoichiometry of fumarate-to-acetate consumption for the initial growth on fumarate was 3.8 ± 0.6, which also corresponded well with the predicted reaction, where acetate is oxidized to CO2, with fumarate serving as the sole electron acceptor: 4COOHCHCHCOOH + CH3COOH + 2H2O
4COOHCH2CH2COOH + 2CO2.The levels of growth (measured as the increase in cell number per millimole of acetate consumed) were similar in the presence of oxygen and in the presence of fumarate. Growth on fumarate alone yielded 5.7 x 107 cells per mmol of acetate, while growth on 5 and 10% oxygen yielded 5.9 x 107 and 6.3 x 107 cells per mmol of acetate, respectively.

Implications.
The finding that
G. sulfurreducens can survive exposure to atmospheric
oxygen and readily grows at low oxygen concentrations has important
implications for the growth and survival of
Geobacter species
in subsurface environments. In water-saturated soils and aquatic
sediments, Fe(III) is likely to be most abundant near the oxic-anoxic
interface, where the oxidation of Fe(II) can regenerate Fe(III)
produced from microbial Fe(III) reduction (
30). Thus, oxygen
intrusions into the zone of Fe(III) reduction may be common,
especially in sediments with substantial bioturbation or other
physical disturbances. In shallow aquifers, an environment where
Fe(III) reduction is often an important terminal electron-accepting
process, periods of high surface recharge can result in the
introduction of dissolved oxygen into previously anoxic zones
(
31). Microorganisms carrying out anaerobic respiration in the
interior anoxic zone of soil aggregates (
24,
25,
26,
27) in
otherwise oxic soils are also likely to face periodic oxygen
exposure. The ability to tolerate exposure to high levels of
oxygen and to grow at low oxygen levels may permit
G. sulfurreducens to thrive in these environments. It is well documented that
once oxygen is consumed in subsurface environments,
Geobacter species can rapidly become the predominant Fe(III)-reducing
microorganisms (
2,
13,
29).
In summary, the results presented here demonstrate that G. sulfurreducens should no longer be classified as a strict anaerobe. Given the potential importance of the survival and growth of Geobacter species in oxic environments, further investigations into the mechanisms by which G. sulfurreducens survives oxidative stress and grows on oxygen are warranted.

ACKNOWLEDGMENTS
This research was supported by the Microbial Genome, Biological
and Environmental Research, Office of Science, Department of
Energy (DE-FG02-01ER63145), and Genomes to Life (DE-FC02-02ER63446)
programs.
We thank Evgenya Shelobolina for her valuable assistance.

FOOTNOTES
* Corresponding author. Mailing address: Department of Microbiology, University of Massachusetts, 203 Morrill Science Center IV, Amherst, MA 01003. Phone: (413) 545-9651. Fax: (413) 545-1578. E-mail:
dlovley{at}microbio.umass.edu.


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Applied and Environmental Microbiology, April 2004, p. 2525-2528, Vol. 70, No. 4
0099-2240/04/$08.00+0 DOI: 10.1128/AEM.70.4.2525-2528.2004
Copyright © 2004, American Society for Microbiology. All Rights Reserved.
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