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Appl Environ Microbiol, July 1998, p. 2697-2700, Vol. 64, No. 7
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
Effectiveness of SYTOX Green Stain for Bacterial
Viability Assessment
P.
Lebaron,*
P.
Catala, and
N.
Parthuisot
Observatoire Océanologique, Centre
National de la Recherche Scientifique (CNRS-UMR7621), Institut
National des Sciences de l'Univers et Université Paris
VI, F-66651 Banyuls-sur-Mer Cedex, France
Received 23 January 1998/Accepted 19 April 1998
 |
ABSTRACT |
The effectiveness of SYTOX Green nucleic acid stain for measuring
bacterial viability was tested on starved populations of Escherichia coli and Salmonella typhimurium.
This stain underestimates the fraction of dead cells within starved
populations containing cells with damaged nucleic acids or membranes.
Its application to natural samples should be considered with caution.
 |
TEXT |
Viability assessment of bacterial
cells is a major requirement in several areas of microbiology from
environmental research to industrial applications. Flow cytometry
(FCM), used in conjunction with fluorescent viability probes, has great
potential for rapid and accurate quantification of viable and dead
cells (11, 13-15). Fluorescent dyes exist as probes for
different cellular functions (9, 12). Membrane-impermeative
fluorescent probes that can passively diffuse through the cell wall of
a bacterium can act as an indicator of a loss in membrane integrity,
which, in turn, can often act as an indicator of cell viability
(3, 10). Indeed, the loss of membrane integrity results in
membrane permeabilization and thus, in the degradation of nucleic acids
whose maintenance is at least essential to retain viability (4,
17, 18). However, such degradation may occur with a delay after
the loss of membrane integrity which may be dependent on both
environmental conditions and species. Although DNA integrity is not
sufficient to ensure viability of a cell, DNA degradation is sometimes
used to quantify dead cells. However, fluorescent probes used to detect the fraction of dead cells with damaged DNA also have limitations. The
use of DNA probes for assessment of DNA degradation should be
considered with caution since apparent DNA damage can be misinterpreted due to changes in the coiling status of the DNA and/or in the permeability of membranes by these dyes (8).
Recently, SYTOX Green stain (Molecular Probes Inc., Eugene, Oreg.) has
been developed for bacterial viability assessment. SYTOX Green stain is
a high-affinity nucleic acid stain that does not cross the membranes of
live cells and yet easily penetrates cells with compromised plasma
membranes. This dead-cell indicator was recently used for rapid
viability assessment after exposure of cells to disinfectant
(7) or antibiotics (16). This dye was suggested
as a good indicator for viability assessment (16). In this
study, we have tested the efficiency of SYTOX Green dye for flow
cytometric detection of dead cells of Escherichia coli and
Salmonella typhimurium within starved populations.
Strains, cultures, and starvation conditions.
All experiments
were conducted with E. coli ATCC 8739 and S. typhimurium ATCC 43971. Heat treatment was used as a positive control of cells with permeabilized membranes. Heat-treated cells were
obtained by resuspending the cells in 1 ml of phosphate-buffered saline
and placing the tube in boiling water for 10 min. To obtain starved
cultures of these strains, the cells were incubated overnight in
Trypticase soy broth (bioMérieux, Marcy-l'Etoile, France) at
37°C, harvested, washed twice by centrifugation at 5,000 × g for 5 min in sterile MilliQ water, and resuspended in the
same medium. Erlenmeyer flasks (1-liter capacity) containing 400 ml of
filtered water (Milli-Q; 0.22-µm-pore-size filter; Millipore) (pH
7.5) were autoclaved (120°C, 15 min), cooled, inoculated to a cell
density of approximately 107 cells per ml, and incubated in
the dark at 20 ± 0.5°C with gentle stirring. Aliquots of 20 ml
were collected after 0, 8, 15, 22, 32, and 46 days of starvation.
Duplicate flasks were prepared for both strains.
Enumeration of total, culturable, and dead cells.
Subsamples
for total cell enumerations were fixed with 2% formaldehyde and then
stained with SYBR Green I (SYBR-I) DNA stain (Molecular Probes)
(11). The DNA fluorescence of stationary-phase cells which
contained at least one genome was used to create a region in the FL1
histogram. This procedure was used to separate damaged-DNA (DNA
) and
undamaged-DNA (DNA+) subpopulations which appear during starvation.
DNA
cells were determined by cells whose fluorescence was less than
that of cells containing one genome. The lower fluorescence of DNA
cells can be due to (i) damaged DNA but also to (ii) changes in the DNA
coiling status which can result in a lower accessibility of the dye to
the target sites and/or to a lower permeability of membranes by the
dye. For enumeration of culturable cells, 100-µl volumes of serial dilutions (1/10) in phosphate-buffered saline were plated onto nutrient
agar (bioMérieux). The proportion of culturable cells (CFU+) was
defined as the ratio of the number of CFU+ cells to the total number of
cells determined by SYBR-I staining. For enumeration of dead cells, a
stock solution of SYTOX Green stain was prepared in dimethyl sulfoxide
to a final concentration of 5 mM. After optimization of the staining
conditions (data not shown), the cells were stained with 1 µM
SYTOX Green (final concentration) for 30 min at 37°C in the dark.
FCM.
Samples were analyzed with a FACSCalibur flow cytometer
(Becton Dickinson) equipped with an air-cooled laser providing 15 mW at
488 nm and with the standard filter setup. Green fluorescence from
stained cells was collected in the FL1 channel (530 ± 15 nm). The
sheath fluid was filtered water (Milli-Q; 0.22-µm-pore-size filter).
All parameters were collected as logarithmic signals. All bacterial
analyses were performed at a low flow rate setting (12 µl
min
1), and acquisition was done over 1 min. The
calibrated flow rate was controlled daily by measuring the volume
before and after analysis. Samples were run such that the event rate
was below 800 to 1,000 events s
1 to avoid coincidence.
All samples were analyzed immediately after staining. Yellow-green
fluorescent 0.94-µm-diameter microspheres (Polysciences Inc.,
Warrington, Pa.) were added to each sample as an internal fluorescence
standard. Data were plotted as histograms showing the fluorescence
distribution. Triplicate counts were made for each procedure.
Effect of heat treatment on the fluorescence distribution of SYTOX
Green-stained cells.
The fluorescence signal from living cells was
brighter than that obtained from SYTOX Green stain alone without
bacteria (data not shown). When SYTOX Green was applied to live cells,
surface binding of dye resulted in a weak but detectable fluorescence emission (Fig. 1a and c). A marked
enhancement of SYTOX Green fluorescence was observed for heat-treated
cells (Fig. 1b and d).

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FIG. 1.
FL1 histograms of live (a and c) and heat-treated (b and
d) E. coli (a and b) and S. typhimurium (c and d)
cells stained with SYTOX Green.
|
|
Application of SYTOX Green to starved cells.
The viability of
E. coli and S. typhimurium cells was monitored
during prolonged starvation in sterile water (Table
1). After inoculation, the percentages of
viable and culturable cells (CFU+) fell rapidly and were lower than 6%
(E. coli) and 0.1% (S. typhimurium) after 46 days of starvation. As expected, this reduction in viable counts was
matched by a concomitant increase in the number of dead cells as
determined by SYTOX Green staining. Surprisingly, this increase was
followed by a decrease in the number of dead cells. At the same time,
we observed a shift in the fluorescence of a significant fraction of
heat-permeabilized cells stained with SYTOX Green. At the onset of
starvation, the large difference in fluorescence emission intensities
between intact (live) and permeabilized (heat-treated) cells stained
with SYTOX Green facilitates discrimination of both populations (Fig.
2a). This difference decreased during
starvation since the fluorescence of permeabilized cells gradually
decreased in brightness, resulting in an increasing overlap with the
fluorescence distribution of live cells (Fig. 2b). This result suggests
a decrease in the apparent DNA content of the cells. Similar trends
were recorded for E. coli.
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TABLE 1.
Percentages of viable cells, dead cells, and cells with
apparent damaged nucleic acids of E. coli and S. typhimurium populations at different times of starvation in
sterile watera
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FIG. 2.
FL1 histograms of live (closed histogram) and
heat-treated (open histogram) S. typhimurium cells after
SYTOX Green staining at 0 (a) and 46 (b) days of starvation.
|
|
Changes in the nucleic acid content of starved cells.
To
better understand this decrease in the number of dead cells as
determined by SYTOX Green staining, we analyzed the temporal evolution
of the nucleic acid content of starved cells by staining the cells with
SYBR-I nucleic acid dye. The degradation of nucleic acids is sometimes
considered an alternative method for assessing the death of bacterial
cells (5, 17). FCM analysis of the nucleic acid content of
SYBR-I-stained cells revealed important changes in the course of
starvation (Fig. 3). These changes may be
mainly influenced by changes in the DNA content of the cells since the
RNA content of starved cells may be very low (1, 2) and
SYBR-I has a higher binding affinity for DNA than for RNA
(11). After inoculation, stationary-phase cells exhibited a
typical bimodal DNA distribution corresponding to cells containing one
or two genomes (8) (Fig. 3a). After continued starvation, a
subpopulation of cells emitting a lower fluorescence intensity that
corresponded to cells with a lower apparent DNA content (DNA
cells)
appeared. After 46 days of starvation, this subpopulation of cells with
an apparent damaged DNA content represented up to 73.5 and 93.1% of
total counts of E. coli and S. typhimurium
populations, respectively (Table 1). At all sampling times, the sums of
the viable (CFU+) and dead (DNA
and SYTOX Green-stained) cells were always less than 100%, but the results were much more coherent when
dead cells were considered as the fraction of DNA
cells. The
noncomplementarity at a given sampling time between both live and dead
cell counts may be explained by the fact that the apparent degradation
of DNA may occur after the loss of membrane integrity and, thus, with a
certain time lag after the loss of culturability. This result is
congruous with those of other reports (4, 17). As stated
above, this apparent DNA degradation can be due to DNA degradation but
can also be due to changes in the coiling status of DNA. Since an
increasing fraction of heat-permeabilized cells also has a lower
fluorescence intensity after SYTOX Green staining, changes in membrane
permeability cannot explain this increasing fraction of DNA
cells. It
is also interesting that this decrease in the fluorescence signal was
not gradual but corresponded to a rapid shift from one
well-characterized state to another. This DNA
state was not
reversible when the cells were subjected to a 24-h resuscitation step
by adding 1% Trypticase soy broth to the flask after 46 days of
starvation (data not shown). Although the resuscitation conditions
(time and type of nutrients) were perhaps not the most appropriate, the
results suggest that DNA
cells were not viable cells. Inversely, DNA+
cells were responsive to this nutrient supply after 8 h of
incubation with the nutrients.

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FIG. 3.
FCM histograms demonstrating changes which occur in the
DNA fluorescence distribution of S. typhimurium cells at
different times of starvation in sterile water (0, 8, 15, 22, 32, and
46 days).
|
|
Limitations of SYTOX Green staining for viability assessment.
SYTOX Green and SYBR-I are nucleic acid stains with a high
binding affinity for DNA. SYBR-I readily penetrates fixed cells even without membrane permeabilization, while SYTOX Green penetrates cells with permeabilized membranes. If we assume that the apparent DNA
degradation occurs after the loss of membrane integrity, cells with
compromised membranes may contain intact or damaged nucleic acids. The
fraction of DNA
cells with a low fluorescence emission after SYBR-I
staining, corresponding to cells with damaged DNA, increased with
starvation time. Such cells have compromised membranes and should be
stained with SYTOX Green. However, DNA degradation and/or changes in
the topology of the molecule result in a shift of the fluorescence
emission of SYTOX Green-stained cells which overlaps with the weak
fluorescence emission of living cells (16). Thus, the weak
fluorescence of these cells after SYTOX Green staining may correspond
either to permeabilized cells with damaged nucleic acids or to living
cells. Such dead cells with a low fluorescence, whose fraction
increases during starvation, are counted as live cells since they
appear in a fluorescence region corresponding to that of live cells
initially defined with stationary-phase cells. This is why the
number of dead cells, as determined by SYTOX Green staining, decreases
during starvation. Consequently, the percentage of dead cells recorded
after SYTOX Green staining corresponds only to the fraction of cells
with permeabilized membranes and an as-yet-undegraded and/or
topologically modified nucleic acid content.
Recently, it was suggested that SYTOX Green stain is an effective
alternative to conventional methods for measuring bacterial
viability
and antibiotic susceptibility (
16). Our results suggest
that
the use of SYTOX Green stain for detection and evaluation
of viability
in bacteria should be considered with caution and
restricted to
specific applications such as the analysis of antibiotic
susceptibility
of bacteria with undamaged nucleic acids. Although
the physiology of
many bacteria is unknown today, the normal state
for most copiotrophic
bacteria in the aquatic environment is the
starvation mode
(
6). Recently, it was suggested that the percentage
of
nucleoid-containing cells within oligotrophic marine communities
may be
low and often lower than 50% (
5,
18). Thus, the application
of SYTOX Green to determine the fraction of dead cells in the
natural
environment may be of limited use. When SYTOX Green staining
was
applied to marine coastal waters from the Mediterranean Sea,
it was not
possible to discriminate live from dead populations
(data not shown).
Concluding remarks.
The results presented here suggest that
the use of viability dyes such as SYTOX Green stain which target
molecules or sites which are degraded and/or modified during the
starvation process may underestimate the fraction of dead cells, mainly
when discrimination between labeled cells and background signals is
problematic. The use of such dyes to investigate the viability of cells
within natural and complex communities should be considered with
caution.
 |
ACKNOWLEDGMENTS |
This work was funded by contract ELOISE PL950439 from the European
Community. The FACSCalibur flow cytometer was funded by CNRS-INSU-SDV
and by contract ELOISE PL950439.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Laboratoire
ARAGO, BP44, F-66651 Banyuls-sur-Mer Cedex, France. Phone: 33 4 68 88 73 53. Fax: 33 4 68 88 73 95. E-mail:
lebaron{at}arago.obs-banyuls.fr.
 |
REFERENCES |
| 1.
|
Davis, B. D.,
S. M. Luger, and P. C. Tai.
1986.
Role of ribosome degradation in the death of starved Escherichia coli cells.
J. Bacteriol.
166:439-445[Abstract/Free Full Text].
|
| 2.
|
Guindulain, T.,
J. Comas, and J. Vives-Rego.
1997.
Use of nucleic acid dyes SYTO-13, TOTO-1, and YOYO-1 in the study of Escherichia coli and marine prokaryotic populations by flow cytometry.
Appl. Environ. Microbiol.
63:4608-4611[Abstract].
|
| 3.
|
Jepras, R. I.,
J. Carter,
S. C. Pearson,
F. E. Paul, and M. J. Wilkinson.
1995.
Development of a robust flow cytometric assay for determining numbers of viable bacteria.
Appl. Environ. Microbiol.
61:2695-2701.
|
| 4.
|
Joux, F.,
P. Lebaron, and M. Troussellier.
1997.
Succession of cellular states in a Salmonella typhimurium population submitted to starvation in artificial seawater microcosms.
FEMS Microbiol. Ecol.
22:65-76.
|
| 5.
|
Karner, M., and J. A. Fuhrman.
1997.
Determination of active marine bacterioplankton: a comparison of universal 16S rRNA probes, autoradiography, and nucleoid staining.
Appl. Environ. Microbiol.
63:1208-1213[Abstract].
|
| 6.
|
Kjelleberg, S. (ed.).
1993.
Starvation in bacteria.
Plenum Press, New York, N.Y.
|
| 7.
|
Langsrud, S., and G. Sundheim.
1996.
Flow cytometry for rapid assessment of viability after exposure to a quaternary ammonium compound.
J. Appl. Bacteriol.
81:411-418[Medline].
|
| 8.
|
Lebaron, P., and F. Joux.
1994.
Flow cytometry analysis of the cellular DNA content of Salmonella typhimurium and Alteromonas haloplanktis during starvation and recovery in seawater.
Appl. Environ. Microbiol.
60:4345-4350[Abstract/Free Full Text].
|
| 9.
|
Lloyd, D., and A. J. Hayes.
1995.
Vigour, vitality and viability of microorganisms.
FEMS Microbiol.
133:1-7.
|
| 10.
|
Lopez-Amoros, R.,
S. Castel,
J. Comas-Riu, and J. Vives-Rego.
1997.
Assessment of E. coli and Salmonella viability and starvation by confocal laser microscopy and flow cytometry using rhodamine 123, DiBAC4(3), propidium iodide and CTC.
Cytometry
29:1-8[Medline].
|
| 11.
|
Marie, D.,
F. Partensky,
S. Jacquet, and D. Vaulot.
1997.
Enumeration and cell cycle analysis of natural populations of marine picoplankton by flow cytometry using the nucleic acid stain SYBR Green I.
Appl. Environ. Microbiol.
63:186-193[Abstract].
|
| 12.
|
McFeters, G. A.,
F. P. Yu,
B. H. Pyle, and P. S. Stewart.
1995.
Physiological assessment of bacteria using fluorochromes.
J. Microbiol. Methods
21:1-13.
[Medline] |
| 13.
|
Porter, J.,
D. Deere,
R. Pickup, and C. Edwards.
1996.
Fluorescent probes and flow cytometry: new insights into environmental bacteriology.
Cytometry
23:91-96[Medline].
|
| 14.
|
Porter, J.,
J. Diaper,
C. Edwards, and R. Pickup.
1995.
Direct measurements of natural planktonic bacterial community viability by flow cytometry.
Appl. Environ. Microbiol.
61:2783-2786[Abstract].
|
| 15.
|
Porter, J.,
C. Edwards, and R. W. Pickup.
1995.
Rapid assessment of physiological status in Escherichia coli using fluorescent probes.
J. Appl. Bacteriol.
79:399-408[Medline].
|
| 16.
|
Roth, B. L.,
M. Poot,
S. T. Yue, and P. J. Millard.
1997.
Bacterial viability and antibiotic susceptibility testing with SYTOX Green nucleic acid stain.
Appl. Environ. Microbiol.
63:2421-2431[Abstract].
|
| 17.
|
Weichart, D.,
D. McDougald,
D. Jacobs, and S. Kjelleberg.
1997.
In situ analysis of nucleic acids in cold-induced nonculturable Vibrio vulnificus.
Appl. Environ. Microbiol.
63:2754-2758[Abstract].
|
| 18.
|
Zweifel, U. L., and Ä. Hagström.
1995.
Total counts of marine bacteria include a large fraction of non-nucleoid-containing bacteria (ghosts).
Appl. Environ. Microbiol.
61:2180-2185[Abstract].
|
Appl Environ Microbiol, July 1998, p. 2697-2700, Vol. 64, No. 7
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
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