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Applied and Environmental Microbiology, November 1998, p. 4238-4245, Vol. 64, No. 11
Laboratoire de Microbiologie de
l'Environnement, Université de Caen, 14032 Caen Cedex, France
Received 9 April 1998/Accepted 19 August 1998
The ability of Enterococcus faecalis to metabolically
adapt to an oligotrophic environment has been analyzed. E. faecalis is able to survive for prolonged periods under
conditions of complete starvation established by incubation in tap
water. During incubation in this microcosm, cells developed a rippled
cell surface with irregular shapes. Exponentially growing cells
survived to the same extent as cells starved for glucose prior to
exposure to the multiple nutrient deficient stress. Chloramphenicol
treatment during incubation in tap water led to a rapid decline in
plate counts for exponentially growing cells but showed progressively reduced influence on stationary-phase cells harvested after different times of glucose starvation. During incubation in the oligotrophic environment, cells from the exponential-growth phase and
early-stationary phase became progressively more resistant to other
environmental stresses (heat [62°C], acid [pH 3.3], UV254
nm light [180 J/m2], and sodium hypochlorite
[0.05%]) until they reached a maximum of survival characteristic for
each treatment. In contrast, cells starved of glucose for 24 h did
not become more resistant to the different treatments during incubation
in tap water. Our combined data suggest that energy starvation induces
a response similar to that triggered by oligotrophy. Analysis of
protein synthesis by two-dimensional gel electrophoresis revealed the
enhanced synthesis of 51 proteins which were induced in the
oligotrophic environment. A comparison of these oligotrophy-inducible
proteins with the 42 glucose starvation-induced polypeptides (J. C. Giard, A. Hartke, S. Flahaut, P. Boutibonnes, and Y. Auffray, Res.
Microbiol. 148:27-35, 1997) showed that 16 are common between the two
different starvation conditions. These proteins and the corresponding
genes seem to play a key role in the observed phenomena of long-term
survival and development of general stress resistance of starved
cultures of E. faecalis.
The natural habitat of enteric
bacteria is the intestine of humans and animals. When discharged into a
natural aquatic system, these allochthonous microorganisms need to
adapt for survival in this hostile environment. Water systems are
characterized by their oligotrophic nature (18, 19), and
nutrient starvation seems to be one of the abiotic factors that
negatively affects survival (2).
Recent advances in studying the physiological response of
nondifferentiating bacteria following starvation of different
individual nutrients has led to an understanding that such bacteria
undergo a concerted rapid change in the pattern of gene expression
(13). The metabolic reprogramming leads to a cellular state
of enhanced resistance, compared to that in exponentially growing
cells, to a great number of various stress conditions (see references
9 and 10 and references therein).
Fecal streptococci are considered to be good indicators of fecal
contamination since they are present in the feces of humans and
warm-blooded animals. Despite this fact, fecal streptococci have
received, relative to fecal coliforms and in particular
Escherichia coli, only minor attention from researchers
studying the destiny of allochthonous bacteria after their release into
aquatic systems. Compared to other streptococci, Enterococcus
faecalis is considered to survive longer in the aquatic
environment (2) and hence should be the most suitable
indicator of fecal contamination in water. Furthermore, this
gram-positive, nonsporulant bacterium is known as an opportunistic
pathogen that causes urinary tract infection and is responsible for the
majority of cases of subacute bacterial endocarditis. Because of the
increasing importance of the health risks associated with exposure to
contaminated water and of hospital-acquired infections, which are due
to an alarming increase in resistance to various antibiotics, we have
initiated studies to increase our fundamental understanding and
knowledge of E. faecalis survival strategies after its
release into hostile environments (3, 6-10, 15, 16, 23).
We have recently determined the starvation stress response to glucose
of E. faecalis. During the first 24 h of the energy starvation period at least 42 proteins with time-dependent
sequential synthesis were induced (10). The
carbohydrate-starved cells showed enhanced resistance to lethal heat,
oxidative, acid, ethanol (9), and NaOCl (16)
stresses, compared to the growing cells, indicating that energy
starvation in E. faecalis triggers development of a
generally resistant phenotype. The time necessary to reach maximal
resistance in the stationary phase was shown to be characteristic for
each stress condition.
As stated above, starvation of only one nutrient is rarely encountered
by fecal bacteria after release by the host. The objective of this
study was to determine whether E. faecalis develops general stress resistance in an aquatic environment characterized by its oligotrophic nature. Furthermore, we were interested in whether the
response triggered by oligotrophy overlaps with that induced in rich
medium after the exhaustion of the energy source glucose. Therefore,
exponentially growing and preadapted glucose-starved cells of E. faecalis were introduced into tap water, and survival rates as
well as the development of resistance to different treatments were
determined. Furthermore, to gain insight into the adaptation process of
this fecal bacterium to an aquatic environment at the molecular level,
we have analyzed changes in protein metabolism by two-dimensional gel electrophoresis.
Bacterial strain, culture conditions, and introduction into the
oligotrophic microcosm.
This study was performed with E. faecalis JH2-2 obtained from the parental strain JH2
(12). Cultures were grown without shaking at 37°C in 20-ml
glass tubes containing 10 ml of semisynthetic medium (Bacto-Folic AOAC
Medium; Difco, Detroit, Mich.) supplemented with 0.15% glucose. Under
these conditions cultures entered stationary phase at an optical
density of 600 nm (OD600) of 1.1, a value which corresponds
to approximately 3 × 108 CFU/ml. Cells from the
exponential-growth phase were harvested at an OD600 of 0.5. Prior to introduction into tap water, the cultures were harvested by
centrifugation and washed twice in an equal volume of sterile 0.9%
NaCl at room temperature. Finally, the pellets were suspended in tap
water (obtained from the distribution system of the city of Caen,
France) to a final concentration of approximately 108
CFU/ml and incubated at 16°C without shaking in the presence or
absence of chloramphenicol (100 µg/ml). Prior to its use, tap water
was filtered through a 0.2-µm (pore size) cellulose filter (Millipore
Corp., Bedford, Mass.) and autoclaved for 15 min at 121°C.
Challenge conditions and cell count.
For heat, acid, and
NaOCl challenges the cells were harvested by centrifugation and
resuspended in semisynthetic medium either prewarmed to 62°C or
adjusted to pH 3.3 by HCl or containing 0.05% (vol/vol) NaOCl (Sigma
Chemical Co., St. Louis, Mo.). Free and total chlorine were determined
colorimetrically by the dialkyl-p-phenylenediamine method
(Merck, Darmstadt, Germany). Cultures incubated in the microcosms were
irradiated with UV254 nm light in a standard petri dish
without any pretreatment. Control cultures were harvested prior to
irradiation by centrifugation and resuspended in 10 ml of 0.9% NaCl
before transfer to a petri dish. In all cases, UV irradiation was
performed at a dose rate of 150 J/m2.
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
Survival of Enterococcus faecalis in an
Oligotrophic Microcosm: Changes in Morphology, Development of General
Stress Resistance, and Analysis of Protein Synthesis
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ABSTRACT
Top
Abstract
Introduction
Materials & Methods
Results
Discussion
References
![]()
INTRODUCTION
Top
Abstract
Introduction
Materials & Methods
Results
Discussion
References
![]()
MATERIALS AND METHODS
Top
Abstract
Introduction
Materials & Methods
Results
Discussion
References
Electron microscopy. E. faecalis cells were fixed by the addition of glutaraldehyde to a final concentration of 2% (wt/vol) in 0.1 M sodium cacodylate buffer (pH 6.8) (SCB). After this first fixation the cells were rinsed with 0.1 M SCB and fixed for 1 h in 1% (wt/vol) osmium tetroxide in 0.1 M SCB. The samples were then washed twice with 0.1 M SCB, dehydrated with acetone, critical-point dried by the CO2 method of Anderson (1), and coated with gold. Cells were examined and photographed with a JEOL-JSM 6400F field emission scanning electron microscope operating at 5 kV.
Labeling of proteins and two-dimensional gel
electrophoresis.
Culture conditions were as described above.
Culture aliquots of 1 ml were pulse-labeled with 250 µCi of
[35S]methionine-[35S]cysteine protein
labeling mix (1,000 Ci/mmol; New England Nuclear). Exponential-growth-phase cells were labeled for 40 min at 37°C (between OD600 0.25 and 0.5) in semisynthetic medium.
Labeling of cultures in tap water was done by the addition of
radiolabel at the onset of oligotrophy, and the cell suspensions were
incubated for different times at 16°C. Cells were harvested by
centrifugation and resuspended in 500 µl of lysozyme buffer (25 mM
Tris-base [pH 7.0; Millipore] containing 10 µg of lysozyme
[Sigma] per ml, 1 mM phenylmethylsulfonyl fluoride [Sigma], 100 µg of chloramphenicol per ml, and 0.5 M sucrose). Control cultures
from the exponential-growth phase were treated in the same manner
except that the cells were washed twice in cold 0.9% NaCl before
suspension in the lysozyme buffer. After 5 min at 37°C, cells were
harvested by centrifugation, and lysis was performed by the addition of
200 µl of buffer I (0.3% sodium dodecyl sulfate, 200 mM
dithiothreitol [Merck], 28 mM Tris-HCl [Millipore], and 22 mM
Tris-base). After 5 min at 100°C, samples were chilled on ice, and 24 µl of buffer II (24 mM Tris-base, 476 mM Tris-HCl, 50 mM
MgCl2, 1 mg of DNase I [Sigma] per ml, and 0.25 mg of
RNase A [Sigma] per ml) was added. The reaction was stopped after 15 min at 4°C by the addition of 4 volumes of ice-cold acetone, and
precipitation of proteins was allowed to continue for 20 min on ice.
Proteins were collected by centrifugation at 15,000 rpm for 15 min and
were suspended in 40 µl of buffer III (540 mg of urea per ml, 10 mg
of dithiothreitol per ml, 2% [vol/vol] Ampholytes [pH 4 to 8;
Millipore], and 0.52% Triton-X 100). High-resolution two-dimensional
electrophoresis was performed according to the method of O'Farrell
(21) with modifications as described previously
(17) and using the Multiphor II system (Pharmacia Biotech,
Uppsala, Sweden) for the first dimension and the Investigator-2D
electrophoresis system (Millipore) for the second dimension. Labeled
proteins were visualized by autoradiography after 4 to 12 weeks at
80°C by exposure on Hyperfilm-MP (Amersham International). Analysis
of the autoradiograms was performed by visual inspection.
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RESULTS |
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Survival of E. faecalis in an oligotrophic microcosm. The survival of E. faecalis in tap water at 16°C is shown in Fig. 1. During the 85 days of incubation no significant differences were seen between growing cells and those harvested at the onset of glucose starvation or after 3 and 24 h in the stationary phase. In all cases 10 to 30% of cells were culturable.
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Morphological changes of E. faecalis upon residence in the nutrient-poor microcosm. Scanning electron micrographs revealed that cells incubated for 24 h under oligotrophic conditions showed no obvious difference from growing cultures (Fig. 2). The cells had a smooth and spherical appearance and were organized mainly in chains. However, the cells developed a rippled cell surface with irregular shapes and significant alterations within 3 to 7 weeks of starvation. At these longer incubation times, cells were mainly organized as pairs; only rarely were longer chains detected. Some cells had collapsed envelopes, and other cells showed breaks in the septal regions and had surface tears (Fig. 2).
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Development of multiresistance of E. faecalis during
incubation in tap water.
The former experiments showed that
E. faecalis was able to survive for long periods under
oligotrophic conditions and that survival was independent of the
physiological state of the cells prior to the transfer to the
microcosms (Fig. 1). One phenomenon induced by starvation is that
microorganisms develop general stress resistance (13). Our
previous results showed that glucose starvation triggers resistance to
a number of environmental stresses in E. faecalis, e.g.,
heat (62°C), lactic acid (pH 3.2), H2O2 (20 mM), ethanol (17% [vol/vol]) (9), and NaOCl
(10
2% [vol/vol]) (16). We were therefore
interested in determining whether E. faecalis could evolve
into a more resistant state under conditions that were closer to
situations encountered by allochthonous bacteria in the environment.
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Analysis of modifications in protein pattern during incubation in tap water by two-dimensional gel electrophoresis. The most spectacular development into a multiresistant cellular state during incubation in tap water was evident in cells harvested from the exponential-growth phase. In contrast, the resistance of cultures which experienced glucose starvation for 24 h prior to incubation in the oligotrophic environment was not further enhanced. We therefore began to analyze the changes in protein synthesis in naive cells (i.e., those harvested from the exponential-growth phase) during the incubation in the oligotrophic environment.
The autoradiograms obtained with cultures starved in water for different periods are shown in Fig. 4. The first 24 h of incubation in the microcosm was characterized by a shutdown of synthesis of the majority of polypeptides that are normally expressed in growing cultures. Only 40 to 50 proteins were present in the autoradiograms, with the majority at the lower limit of detection and thus not visible on the photographs. However, some protein spots, especially those in the low-molecular-weight range, were more intense and are indicated by arrows. Interestingly, a proportion of these have been identified in a previous work as glucose starvation-inducible proteins (Gls proteins) (10) and thus are indicated with a "G" in the autoradiograms. Whereas polypeptides G24 and G36 were still at the limit of detection, G41 was clearly induced over the level of synthesis in control cells, and G37 and G40 were new polypeptides not present in the growing cultures. Five other proteins not yet identified as stress proteins in E. faecalis JH2-2 (10, 16) were among the polypeptides synthesized during the first day of incubation under the oligotrophic conditions. They are indicated by the character "O." Some of these were also present in growing cells (O14, O29, and O36), but they showed relatively enhanced synthesis in cultures incubated for 24 h in tap water. Others (O21 and O28) seem to be specifically induced under these conditions. One protein (indicated by an intense spot to the right of O29 in the autoradiogram) seems to be different from the others because its spot intensity is comparable to that in the control cells and does not change during the 4-week incubation period in the microcosm (compare Fig. 4A to D).
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DISCUSSION |
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In many studies the bacterial starvation stress response has been analyzed in defined in vitro systems where only one growth factor (in most this is the carbon and/or energy source) was lacking. It has been shown that these one-nutrient-starved bacteria developed a general stress resistance leading to enhanced tolerance to different, otherwise hostile environmental conditions (9, 11, 13). However, only a few investigators (20, 27) have addressed the question of whether this phenomenon also takes place with bacteria under environmental conditions where microorganisms are frequently confronted with multiple starvations. This is particularly true for enteric microorganisms [and even more for (poly)auxotrophs with complex nutritional requirements, e.g., E. faecalis], which are released directly or through wastewater into rivers and coastal areas. In the aquatic ecosystem, the survival of these organisms is affected by complex environmental stresses and killing agents that trigger cellular responses that are still poorly understood. Water systems are characterized by their oligotrophic nature, and this seems to be one of the factors that reduces the culturability of allochthonous coprotrophic bacteria (19).
We have found that E. faecalis survived well in our microcosm, as even after prolonged periods of incubation 10 to 30% could still be cultivated. Byrd et al. (4) measured the survival of several bacteria, including E. faecalis, in a drinking water system and found a rapid decrease of culturability in the first days of incubation. However, the cell density (ca. 106 CFU/ml) and incubation conditions they used were different from those used here.
Recently, it has been shown that nonculturable cells exist and exhibit various degrees of metabolic activity (24, 25). Therefore, the somewhat lower plating efficiency of cells after long-term incubation in tap water may be the result of cellular death, of a transition into a "viable but nonculturable" state, or both. However, if cellular death was mainly responsible for the decrease in CFU counts, this was not accompanied during the first weeks of incubation by significant cell lysis. This result indicates that the potential to adapt and survive in the oligotrophic environment seems not to be due to a significant cannibalism of living over dead cells but may be the result of mobilization of endogenous reserves.
The electron microscopic analysis furthermore revealed that the cells do not significantly shrink during incubation in the nutrient-poor microcosm. This finding is in contrast to the starvation response of gram-negative bacteria. During starvation E. coli become more coccoid, accompanied by a decrease in cell size (14). The shrinking process upon starvation is even more pronounced in marine Vibrio spp., where ultramicrocells as small as 0.03 µm3 can be formed (18). Furthermore, a decrease in cell length upon prolonged incubation of exponentially growing Pseudomonas fluorescens R2fRpr cells introduced into two different soils has been reported (27).
As stated above, starved cells are generally considered to be in a more resistant state than their growing counterparts. However, we have not observed a significant difference between growing and preadapted glucose-starved cultures in survival oligotrophic stress. The survival of the 3- and 24-h glucose-starved cells was independent of protein synthesis during their incubation in tap water. In contrast, the persistence in the oligotrophic environment of their growing counterparts and also, but to a lesser extent, of cells from the onset of glucose starvation was dependent on an active protein metabolism. Thus, the system(s) responsible for long-term survival under oligotrophic conditions seems to be already present in cultures starved of glucose for 3 and 24 h prior to transfer into tap water. In contrast, growing cultures and cells from the onset of glucose starvation were not preconditioned to survive in the oligotrophic environment. However, they can adapt to survive this complex starvation stress by synthesizing specific proteins during incubation in the microcosm that may already be present in preadapted glucose-starved cells. These results suggests a close relationship between the stress responses triggered by glucose starvation and oligotrophy. It is noteworthy that we have obtained a very similar result in seawater (10a), showing that the observed long-term survival and dependence on protein synthesis was not specific for tap water but may reflect a more global adaptation to aquatic environments.
The suggestion of an overlap of the two different starvation responses was furthermore supported by the analysis of the evolution of resistance to heat, acid, NaOCl, and UV irradiation. Cultures which have experienced glucose starvation for 24 h prior to incubation in the oligotrophic environment do not undergo a further increase in resistance. In contrast, cells harvested from the exponential-growth phase, which were initially more sensitive to these stresses, developed resistance progressively during incubation in tap water. This shows that complete starvation does not have a synergistic effect on the multiresistance induced by energy starvation, confirming the suggestion of a molecular link between the two starvation responses in E. faecalis.
Comparable results have been obtained with P. fluorescens (27). Cells inoculated into soils mounted a general stress resistance, and preadaptation to carbon starvation of inoculant cells leads to no further enhancement of the general resistance following incubation in soil. In that study it was suggested that carbon starvation could largely induce a response similar to that triggered by the residence of inoculant cells in soil, but no molecular analysis to strengthen this suggestion was presented.
We have conducted these molecular studies by analyzing changes in protein synthesis during incubation in the oligotrophic microcosm. Incubation of E. faecalis cells in tap water leads to an enhanced synthesis of at least 51 proteins. These polypeptides showed different kinetics of induction, indicating that adaptation to oligotrophy is a highly ordered process. Interestingly, the majority of proteins induced early during incubation in tap water were of low molecular weight. Oligotrophy provoked a shutdown in synthesis of higher-molecular-weight polypeptides at the beginning of the incubation period, and synthesis restarted only after longer incubation times. It is premature to speculate whether some of the early low-molecular-weight proteins play a key role in the adaptation process which enables the cellular protein synthesis machinery to finally regain metabolism of the higher-molecular-weight proteins. However, our experimental conditions did not permit us to determine whether polypeptides which become detectable only after prolonged incubation times in tap water are subject to a delayed switching-on of expression or have lower rates of synthesis relative to those detected earlier.
At least 42 polypeptides were induced in E. faecalis after entrance into the stationary phase provoked by glucose exhaustion (10). Comparison with the proteins induced by oligotrophy revealed an overlap of 16 polypeptides. This finding shows that glucose and multiple nutrient starvation trigger similar responses. Until now only one of these polypeptides, the protein Gls24, has been analyzed at the molecular level (10). The corresponding gene showed homology to a hypothetical open reading frame of Lactococcus lactis (5), and the E. faecalis protein seems to be implicated in morphological changes in the stationary phase (8a).
The other polypeptides induced in tap water may be implicated in the starvation response to other nutrients, i.e., phosphorous, nitrogen, or amino acids. Furthermore, due to the difference in incubation temperatures used to analyze glucose and complete starvation (37 and 16°C, respectively), it is possible that some proteins belong to the cold-shock regulon. Induction of cold-shock proteins in E. faecalis JH2-2 at 8°C has recently been demonstrated (23).
Because carbon and complete starvation trigger similar physiological responses, it seems reasonable to assume that the overlapping polypeptides are responsible at the molecular level for the observed phenomena of long-term survival and the development of general resistance. Interestingly, four of these general starvation proteins have also been identified as CdCl2 inducible. Work is in progress in our laboratory to identify these proteins and their corresponding genes by reverse genetics.
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ACKNOWLEDGMENTS |
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The expert technical assistance of Annick Blandin and Beatrice Cheval was greatly appreciated. We thank Sylviane Lemarinier for the electron microscopic studies and T. N. Ledger for the help with the English.
This work was supported with financial aid from the Agence de l'Eau Seine Normandie.
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FOOTNOTES |
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* Corresponding author. Mailing address: Laboratoire de Microbiologie de l'Environnement, Université de Caen, Esplanade de la Paix, 14032 Caen Cedex, France. Phone: 02-31-56-54-04. Fax: 02-31-56-53-11. E-mail: hartke{at}ibba.unicaen.fr.
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