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Appl Environ Microbiol, May 1998, p. 1725-1730, Vol. 64, No. 5
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
Comparison of Blue Nucleic Acid Dyes for Flow
Cytometric Enumeration of Bacteria in Aquatic Systems
Philippe
Lebaron,*
Nathalie
Parthuisot, and
Philippe
Catala
Observatoire Océanologique, Centre
National de la recherche Scientifique, Institut National des
Sciences de l'Univers et Université Pierre et Marie Curie,
F-66651 Banyuls-sur-Mer Cedex, France
Received 29 October 1997/Accepted 9 March 1998
 |
ABSTRACT |
Seven blue nucleic acid dyes from Molecular Probes Inc. (SYTO-9,
SYTO-11, SYTO-13, SYTO-16, SYTO-BC, SYBR-I and SYBR-II) were compared
with the DAPI (4',6-diamidino-2-phenylindole) method for flow
cytometric enumeration of live and fixed bacteria in aquatic systems.
It was shown that SYBR-II and SYTO-9 are the most appropriate dyes for
bacterial enumeration in nonsaline waters and can be applied to both
live and dead bacteria. The fluorescence signal/noise ratio was
improved when SYTO-9 was used to stain living bacteria in nonsaline
waters. Inversely, SYBR-II is more appropriate than SYTO dyes for
bacterial enumeration of unfixed and fixed seawater samples.
 |
INTRODUCTION |
Quantification of total bacterial
numbers is a basic and essential task in several areas of microbiology,
including public health, biotechnology, the food, water, and
pharmaceutical industries, and natural environments. During the last
two decades, total direct counting methods that use fluorochrome stains
and epifluorescence microscopy have become increasingly popular because
most naturally occurring communities cannot be enumerated accurately as
CFU by culturing on various agar media (16, 18). Advances in
the field of fluorescent dye technology and flow cytometry now allow the application of this rapid, automated technique to such studies. Flow cytometry has become increasingly popular because it offers the
advantage over microscopy of rapid, easy, and accurate enumeration (6, 12, 14, 15, 19). This increasing popularity is also due
to the recent development of low-cost compact flow cytometers.
The laser-based flow cytometers that are currently commercially
available are equipped with argon lasers. Air-cooled argon lasers are
not tunable, running at only one wavelength, namely 488 nm. For this
reason, an increasing number of blue-light-excited nucleic acid dyes
have been developed. Although some of these dyes have been successfully
applied to natural bacterial communities, comparisons of the
performance of these dyes in different types of aquatic environments
have never been made and should be useful for new investigators.
An expanding list of blue-excitable dyes such as TOTO, TO-PRO, YOYO,
YO-PRO, PicoGreen, SYTO-13, and SYBR Green I (referred to hereafter as
SYBR-I) have been developed for the quantification of microorganisms in
aquatic systems (4, 12, 14, 15). Among these, SYTO-13 and
SYBR-I have been shown to be well suited for the enumeration of
bacterioplankton in natural aquatic ecosystems (4, 15).
Recently, new nucleic acid-specific dyes with different quantum yields
on DNA and RNA have been developed. For instance, the quantum yield of
SYTO-16 for DNA is much higher than those of SYTO-13 and SYTO-11, which
have higher binding affinities for RNA. SYTO-9, which is not
commercially available alone but is provided in the LIVE/DEAD bacterial
viability kit (Molecular Probes Inc., Eugene, Oreg.), yields bright
fluorescence when applied to living bacteria. A new specific bacterial
counting kit from the same company has been marketed based on the use
of the SYTO-BC stain (Molecular Probes Inc.). SYBR-II has been
developed for DNA and RNA staining in gels and has never been compared
to SYBR-I for bacterial enumeration. The SYTO dyes penetrate intact
live cells, while others are generally applied to fixed samples.
Staining procedures that work with live cells are of great interest in situations which require (i) rapid assessment of total bacterial counts
and (ii) total cell enumeration after a first staining step of living
cells with viability or activity dyes. It is also important because
fixation results in cell shrinkage and induces biased light-scattering
measurements and a decrease in fluorescence emission for SYTO dyes
(4).
This study was undertaken (i) to compare the staining efficiencies of
different dyes, including those most recently developed, and (ii) to
estimate total bacterial abundances in live and fixed samples from
different aquatic systems, including fresh and saline waters.
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MATERIALS AND METHODS |
Natural samples.
Bottled mineral waters were purchased in
1-liter plastic bottles. River water samples were collected in the Tech
River (along the Mediterranean coast of France) at three stations
(Pas-du-Loup, Saint-Paul, and Pont d'Elne) in February 1997. Surface
seawater samples were collected with Niskin bottles at three different stations in the Mediterranean Sea near Banyuls-sur-Mer (France) in
January and February 1997. SYTO and SYBR bacterial counts were determined by flow cytometry, and DAPI (4',6-diamidino-2-phenylindole) counts were determined by epifluorescence microscopy. We counted bacteria in fresh samples within 2 h of sampling and in fixed samples within 2 days. Fixed samples were stored at 4°C in the dark.
Cultures.
Salmonella typhimurium CIP 60.62T
(Collection Institut Pasteur, Paris, France) was grown at 37°C on
Trypticase soy agar (TSA) or broth (TSB) medium (bioMérieux). For
growth experiments, 100 ml of fresh TSB medium prewarmed at 37°C was
inoculated with 1% (vol/vol) of an overnight culture (at 37°C under
continuous shaking). Growth was monitored spectrophotometrically at 600 nm, and 30-ml subsamples were taken and fixed at different stages of
the growth curve for RNA analysis (see below). An aliquot of 10 ml was
used for live cell analysis, and two aliquots of 10 ml were fixed as described below.
Fixation.
An aliquot (10 ml) of each sample was fixed for at
least 15 min with 2% (vol/vol) formaldehyde (final concentration) and
stored in the dark at 4°C until analysis. For fluorescent in situ
hybridizations (FISH), a second aliquot (10 ml) was fixed with 3 volumes of 4% paraformaldehyde in phosphate-buffered saline (PBS) (130 mM sodium chloride, 10 mM sodium phosphate buffer [pH 7.2]) and
incubated at 4°C for 4 h. Then, cells were pelleted by
centrifugation in an Eppendorf microcentrifuge (8,000 × g, 2 min), washed with PBS, and resuspended in 1 volume of
PBS and 1 volume of absolute ethanol at a concentration of
108 to 109 cells per ml. The fixed cells were
stored at
20°C.
Whole-cell hybridizations.
The rRNA contents of individual
cells were determined by whole-cell hybridizations using EUB338 and
non-EUB338 (negative control) oligonucleotide probes (20).
Cells were hybridized at 46°C for 2 h in 50 µl of
hybridization buffer (0.9 M sodium chloride, 20 mM Tris-HCl, 100 µg
of polyadenylic acid per ml, 10% of a Denhardt solution [100×;
Sigma], 0.01% sodium dodecyl sulfate [pH 7.2]) containing 1 ng of
probe per µl in a 1.6-ml Eppendorf tube. The hybridization was
stopped by adding 500 µl of cold PBS solution (pH 8.4, 0°C).
Samples were stored on ice (0.5 to 1 h) and in the dark until
analysis. Both electrophoretically purified unlabeled probes and
fluorescence-labeled oligonucleotide probes were obtained from
Eurogentec (Seraing, Belgium). An amino group was attached to the 5'
end of the oligonucleotide in the last stage of synthesis. Labeling was
performed by linking fluorescein isothiocyanate to the 5' end of the
oligonucleotide via a six-carbon spacer arm. Fluorescence was analyzed
by flow cytometry (see below).
Dyes and staining conditions.
SYBR-I, SYBR-II, SYTO-9,
SYTO-11, SYTO-13, and SYTO-16 are high-affinity nucleic acid stains
(Molecular Probes Inc.). The spectral characteristics and quantum
yields on DNA and RNA of these dyes are reported in Table
1. SYTO-9 is not commercially available
alone but is provided in the LIVE/DEAD BacLight bacterial viability kit
(Molecular Probes Inc.). The bacterial counting kit from the same
company is based on the use of a SYTO-BC stain, but no further
information concerning the molecule is provided by the manufacturer.
All dyes were delivered in dimethyl sulfoxide, and commercial stock
solutions were stored at
20°C.
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TABLE 1.
Absorption, fluorescence maxima, and fluorescence quantum
yields for DNA and RNA of the dyes tested in
this studya
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The staining procedures for new dyes were optimized for both dead and
live cells. For SYTO-9, -11, -13, and -16 dyes and SYBR-II,
dye
concentrations and incubation times were optimized on fixed
S. typhimurium cells and on natural waters by testing three
concentrations
(2.5, 5, and 10 µM) and recording the intensities of
cellular
fluorescence at time intervals. Then, for optimization of the
staining solution, the effects of both sodium citrate and potassium
citrate were tested (
14).
For all live and fixed samples and after optimization of staining
procedures, sodium citrate (pH 7.4, 50 mM final concentration)
and
potassium citrate (pH 7.4, 30 mM final concentration) were
added when
staining with SYTO and SYBR dyes, respectively. For
cultures, live and
fixed cells were directly diluted in the saline
solution. SYBR-I and
SYBR-II dyes were added at a final concentration
of 10
4
of the stock solution and incubated for 15 min in the dark. The
optimized staining procedure for SYBR-II was similar to that used
for
SYBR-I. For the counting kit (SYTO-BC dye), the conditions
were those
recommended by the manufacturer.
Evaluations of both DNA and RNA staining efficiency were done for
SYTO-9 and SYBR-II. In this case, optimized staining procedures
were
applied after the fixed cells had been incubated (37°C, 60
min) in
the presence of RNase A (type 1A, Sigma R-4875) at 400
Kunitz units
ml
1 and RNase B (Sigma R-5750) at 500 Kunitz units
ml
1 (
14) or not incubated. Ribonucleases were
rendered free of
DNase (
13). Nonspecific staining was tested
by combining DNA
and RNA digestions. DNA digestion was performed with
DNase I (type
4, Sigma D-5025) at 2,000 Kunitz units ml
1
(37°C, 60 min). Pronase E (Sigma P6911) was used alone or combined
with nucleases at 50 µg ml
1 to test for the possibility
of dye-restricting nucleoproteins
(
12).
Flow cytometry.
All experiments were performed with a
FACS-Calibur flow cytometer (Becton Dickinson) equipped with an
air-cooled laser providing 15 mW at 488 nm and the standard filter
setup. All parameters were collected as logarithmic signals. Green
fluorescence was collected in the FL1 channel (530 ± 15 nm). For
marine samples, the presence of phytoplanktonic cells in natural
samples, mainly Prochlorococcus spp., was checked in the FL3
channel (>630 nm).
For cell enumeration, two procedures were tested because quantification
of the analyzed volume is not available on the FACS-Calibur
flow
cytometer: (i) a 1-ml sample was put in a 12- by 75-mm plastic
tube and
was weighed before and after analysis in order to determine
the
analyzed volume, and (ii) cells were enumerated during a fixed
time
(generally 1 min) at a given flow rate which was calibrated
at the
beginning and end of each analysis session. The second
procedure was
finally used for routine work but both procedures
yielded similar
results. Yellow-green fluorescent microspheres
(0.95-µm-diameter
fluorescent size-standard beads; Polysciences
Inc., Warrington, Pa.)
were systematically added to each sample
as an internal reference. This
internal standard allows the normalization
of cell fluorescences, which
were expressed in bead fluorescence
units (
19). All
microscopic counts were performed by DAPI staining,
as previously
reported, with 47-mm-diameter filters (
10).
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RESULTS AND DISCUSSION |
Staining procedures.
The staining kinetics of SYTO dyes were
determined by flow cytometry of live and fixed S. typhimurium cells from a stationary-phase culture. Three dye
working concentrations (2.5, 5, and 10 µM) were chosen after
preliminary experiments (data not shown). Figure 1 shows the results obtained for fixed
S. typhimurium cells stained with SYTO-9. The green
fluorescence intensity increased rapidly during the first 15 min, and
equilibrium was reached by 30 min. Similar results were obtained for
all SYTO dyes (data not shown). Although staining for 30 min at 2.5 µM was not significantly different from staining at 5 µM, the
reproducibility of results including those from natural samples was
better at the higher concentration. Thus, for further tests with
SYTO-type dyes, the staining concentration was 5 µM and incubations
were performed at room temperature in the dark for 30 min. When applied
to natural samples, the kinetics of staining of SYTO dyes were similar.
Fluorescence of stained cells peaked after 15 min for both SYBR-I and
-II dyes (data not shown). When applied to living cells, equilibrium
was reached after 30 and 40 min for SYBR and SYTO dyes, respectively
(data not shown).

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FIG. 1.
Staining kinetics of fixed S. typhimurium
cells stained with SYTO-9 at three final concentrations: 2.5 µM
(closed squares), 5 µM (circles), and 10 µM (open squares).
Standard deviations were determined with triplicate samples. a.u.,
arbitrary units.
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Both the concentrations and incubation times found for SYTO dyes were
higher than those reported by del Giorgio et al. (
4),
who
worked with lake waters stained with SYTO-13. As stated by
those
authors, we also found that the fluorescence of fixed cells
was lower
than that of live cells; this difference was much greater
for marine
samples (see below). The staining conditions found
for SYBR-I and
SYBR-II dyes were in general agreement with those
reported for SYBR-I
by Marie et al. (
15).
Effects of salts.
The effect of salt addition on the
fluorescence signal was also tested for each dye (Table
2). The addition of 50 mM sodium citrate
improved staining with all SYTO dyes, whereas the fluorescence of SYBR
(I and II)-stained cells was higher when incubated with 30 mM of
potassium citrate. These results are similar to those reported with
SYBR-I for natural seawater samples (15). For all other
experiments, the protocol used for staining cultures and natural
samples consisted of staining with SYTO dyes at 5 µM (final
concentration) in the presence of 30 mM sodium citrate and an
incubation of 30 and 45 min for fixed and live cells, respectively. For
SYBR-I and SYBR-II, cells were stained with a 10
4
concentration of stock solution in the presence of 30 mM potassium citrate and incubated for 15 and 30 min for fixed and unfixed bacteria,
respectively. All incubations were at room temperature in the dark.
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TABLE 2.
Relative fluorescence intensities of fixed bacterial
cells from mineral water and seawater samples with various dyes
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Comparisons of the different dyes.
Table
3 shows comparisons of relative green
fluorescence of fixed bacterial cells from a culture and from mineral,
river, and seawater samples stained with the different dyes. For each water type, the mean fluorescence intensities vary greatly between the
different dyes. For low-salinity samples (culture, mineral, and river
water samples), the fluorescence intensity was high with SYTO-9,
SYTO-16, SYBR-I and SYBR-II, whereas SYTO-13, SYTO-11, and the counting
kit yielded lower signals. The highest mean intensity of green
fluorescence was obtained with SYTO-9. Among SYBR-type dyes, the higher
fluorescence signals were obtained with SYBR-II. Conversely, for marine
samples the fluorescence intensity was higher with SYBR (I and II)
dyes. Surprisingly, the fluorescence intensities of cells stained with
both SYBR-I and SYBR-II dyes revealed little difference, whereas the
quantum yields of the two stains for DNA and RNA are very different
(Table 1). These results suggest that quantum yields should be used
with caution in assessing the apparent DNA and RNA contents of
individual cells.
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TABLE 3.
Relative fluorescence intensities of fixed bacterial
cells from culture, mineral water, river water, and seawater samples
with various dyes
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For all SYTO and SYBR dyes, fixation of the cells before staining
resulted in a decrease in the fluorescence of fixed relative
to unfixed
bacteria. Table
4 shows the effect of
formaldehyde
fixation on the green fluorescence emission of cells
stained with
SYTO-9 and SYBR-II. We noted a strong decrease in the mean
fluorescence
emissions of stained cells after formaldehyde fixation.
The effect
of fixation on stationary-phase cells from a pure culture
was
lower. This decrease resulted in lower fluorescence signal/noise
ratios, which were due to the lower fluorescence signals of stained
bacteria (Fig.
2). Although this lower
fluorescence ratio had
no effect on cell counting in nonsaline samples
because bacteria
remained clearly discriminable, it was more
problematic for marine
samples (Fig.
2). In marine waters, the
discrimination of bacterial
cells was easier with live cells since the
fluorescence distribution
of fixed cells was closer to the origin (Fig.
2). With fixed seawater
samples, the fluorescence noise, which most
likely results from
the presence of fluorescent organic particles
naturally occurring
in seawater, interfered with the cytometric signals
of stained
bacteria. These interferences, which were more important
with
SYTO dyes, were due to a variable overlapping of both signal and
noise fluorescence distributions and resulted in biased estimations
(generally an overestimation) of bacterial counts (data not shown).
The
higher signal/noise ratio was obtained with SYBR-II (Fig.
2).
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TABLE 4.
Relative fluorescence intensities of live and dead
(fixed) S. typhimurium log-phase cells from mineral and
marine waters stained with SYTO-9 and SYBR-II
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FIG. 2.
Fluorescence histograms of bacteria from unfixed and
fixed seawater samples stained with SYBR-I, SYBR-II, SYTO-9, and
SYTO-13.
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This effect of formaldehyde fixation on fluorescence intensity was
reported previously by del Giorgio et al. (
4) for SYTO-13.
Those authors suggested that it could be explained by morphological
changes after fixation and/or by decreased permeability of
formaldehyde-fixed
cells to the dyes. We suggest that the positive
charges of SYTO
(cyanines) and SYBR-type dyes (at neutral pH)
facilitate their
penetration into living cells, which have a membrane
potential,
as opposed to formaldehyde-fixed cells with compromised
membranes.
Permeabilization by formaldehyde fixation was not sufficient
to
allow passive entrance of the dyes. Inversely, when natural samples
and cultures were fixed by heat treatment to permeabilize the
cells,
the fluorescence emission was higher than that of live
cells,
suggesting better permeabilization of membranes to the
dyes (data not
shown). These results suggest that when applied
to natural samples, the
fluorescence intensities of SYTO- and
SYBR-stained bacteria are
improved with live bacteria having polarized
membranes. Moreover, the
presence of cells having damaged membranes
within natural communities
may result in lower fluorescence signals
due to less-efficient
penetration of the dyes, as observed with
formaldehyde-fixed cells.
Comparison of counts.
For nonsaline samples, counts made by
epifluorescence microscopy of DAPI-stained cells were well correlated
with those of live cells stained with SYTO-9 (r2 = 0.99, n = 23) and SYBR-II (r2 = 0.984, n = 23) and counts made by flow cytometry
(Fig. 3). The correlation between counts
obtained with SYTO-9 and DAPI samples was high for both fixed
(r2 = 0.978) and live (r2 = 0.959) cells. A similar strong relationship was found for SYBR-II for
live (r2 = 0.99, n = 23) and
fixed (r2 = 0.985, n = 23)
cells. For unfixed seawater samples, the bacterial counts obtained for
samples stained with SYTO- and SYBR-type dyes were well correlated
(Table 5). However, the correlations
reported between counts made with these dyes and those obtained by DAPI staining and epifluorescence microscopy were slightly lower. These differences may be due to less-accurate enumerations with
epifluorescence microscopy, since natural seawater samples contain many
more particles than mineral waters and pure cultures. The presence of
organic and mineral particles and the small sizes of most marine
bacteria may result in lower bacterial discrimination when cells are
counted by microscopic examination. Moreover, although this is common to both fresh and marine samples, microscopic enumeration is less accurate than flow cytometric enumeration because (i) a low number of
cells is counted (400 to 500), (ii) cells are not always homogeneously distributed on the membrane filter, and (iii) the determination of the
microscope factor (ratio between the surface of the microscopic field
and that of the filters on which cells are distributed) suffers from
some inaccuracies (10).

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FIG. 3.
Relationship between epifluorescence bacterial counts
with DAPI staining and cytometric counts with SYTO-9 and SYBR-II
staining of S. typhimurium cells in culture, mineral, and
river waters (n = 23). The straight line corresponds to
a 1:1 relationship.
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TABLE 5.
Correlations between bacterial counts determined from
unfixed seawater samples (n = 28) stained with
different dyes
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Specificity of the nucleic acid stains SYTO-9 and SYBR-II for
Salmonella.
Initially, we were interested in testing dyes
with high binding affinities for both DNA and RNA to simultaneously
determine both total counts and active cells in natural marine waters.
It has been suggested that a cell containing rRNA in quantities
detectable by 16S rRNA hybridization probably contains the essential
ingredients to be viable (2, 7-9). However, the rRNA
content of most bacteria in oligotrophic environments is often
undetectable by in situ hybridization with rRNA fluorescent probes
without amplification techniques (1, 11, 17). Inversely,
other workers have suggested that DNA, RNA, and proteins are not good
indicators of activity in the environment due to low metabolic activity
and heterogeneous composition (5). The sensitivity of SYTO-9
and SYBR-II to the rRNA content of individual cells of S. typhimurium was estimated by comparing FISH hybridization with
SYTO-9 and SYBR-II staining. Pronase E combined with nucleases had no
effect on the fluorescence signals, suggesting the absence of
dye-restricting nucleoproteins. DNase treatment resulted in an
important background of fluorescence and could not be applied alone or
combined with RNase prior staining. A good correlation
(r2 = 0.89, n = 12) between the
fluorescence values of cells hybridized by FISH techniques and those
obtained by the difference between SYTO-9-stained cells treated and not
treated with RNases was found for growing cells (Fig.
4). The fluorescence signal of S. typhimurium cells stained with SYTO-9 was much higher than that of
cells hybridized with the rRNA fluorescent probe (Fig. 4). A similar
correlation was obtained with SYBR-II (r2 = 0.91, n = 12), but the fluorescence intensity relative
to the RNA content of the cells, as estimated by the difference between SYBR-II-stained cells treated and not treated with RNases, was similar
to that of SYTO-9-stained cells. Although these dyes have very
different quantum yields when they bind to RNA (Table 1), the
fluorescence intensities of stained cells with high RNA contents were
not higher with SYBR-II (data not shown). Thus, the application of
dyes, such as SYTO-9 and SYBR-II, to the discrimination of active
and/or growing cells containing RNA within natural communities remains
unclear since (i) DNase treatment induces an important background of
fluorescence and cannot be applied prior to staining, (ii) the quantum
yield of the dyes may be different when cells rather than
double-stranded RNA and double-stranded DNA in solution are stained,
and (iii) the quantitative relationship between RNA and activity may be
highly species dependent. Alternatively, the use of such dyes without
any nuclease treatment, to discriminate subpopulations having different
nucleic acid contents and membrane polarization within natural
communities, seems promising but requires further experiments.

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FIG. 4.
Evolution of RNA contents of S. typhimurium
cells during successive phases of growth. RNA contents were determined
by whole-cell hybridization (closed circles) and by SYTO-9 staining
(open circles). The insert shows the positions of sampling points on
the growth curve. OD, optical density.
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In this paper, we have presented data that suggest that SYTO-9 and
SYBR-II are the best-suited blue-light-excited fluorescent
dyes for
bacterial enumeration in aquatic systems and that both
can be used to
stain living cells. A major advantage of staining
living cells is that
it prevents cell shrinkage and reduces the
time of staining. However,
SYTO-9 yields higher fluorescence signals
in freshwater samples,
whereas SYBR-II dye is more efficient in
saline waters.
Within the range of SYTO dyes, SYTO-9 is much more efficient than
SYTO-13, SYTO-11, and the counting kit for bacterial enumeration.
However, one limitation to further use of this dye is that it
is not
commercially available at present as a single dye but only
in
combination with another dye in the LIVE/DEAD BacLight kit
from
Molecular Probes Inc. We hope that it will be available soon
as a
single dye, due to its excellent discrimination of bacterial
populations when it is applied to different types of nonsaline
environments. At the moment, SYBR-II is the best candidate for
bacterial cell counting in water samples.
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ACKNOWLEDGMENTS |
This work was funded in part by Chemunex (Maisons-Alfort, France)
and by contract ELOISE PL950439 from the European Community. The
FACS-Calibur flow cytometer was funded by CNRS-INSU and by contract
ELOISE PL950439.
We are grateful to Hendrik Schäfer for language improvements, and
we thank the anonymous reviewers for valuable comments.
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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.
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REFERENCES |
| 1.
|
Alfreider, A.,
J. Pernthaler,
R. Amann,
B. Sattler,
F.-O. Glöckner,
A. Wille, and R. Psenner.
1996.
Community analysis of the bacterial assemblages in the winter cover and pelagic layers of a high mountain lake by in situ hybridization.
Appl. Environ. Microbiol.
62:2138-2144[Abstract].
|
| 2.
|
Boye, M.,
T. Ahl, and S. Molin.
1995.
Application of a strain-specific rRNA oligonucleotide probe targeting Pseudomonas fluorescens Ag1 in a mesocosm study of bacterial release into the environment.
Appl. Environ. Microbiol.
61:1384-1390[Abstract].
|
| 3.
|
Bremer, H., and P. P. Dennis.
1987.
Modulation of chemical composition and other parameters of the cell by growth rate, p. 1527-1542.
In
F. C. Neidhardt, J. L. Ingraham, K. B. Low, B. Magasanik, M. Schaechter, and H. E. Umbarger (ed.), Escherichia coli and Salmonella typhimurium: cellular and molecular biology. American Society for Microbiology, Washington, D.C.
|
| 4.
|
del Giorgio, P. A.,
D. F. Bird,
Y. T. Prairie, and D. Planas.
1996.
Flow cytometric determination of bacterial abundance in lake plankton with the green nucleic acid stain SYTO 13.
Limnol. Oceanogr.
41:783-789.
|
| 5.
|
Jeffrey, W. H.,
R. V. Haven,
M. P. Hoch, and R. B. Coffin.
1996.
Bacterioplankton RNA, DNA, protein content and relationships to rates of thymidine and leucine incorporation.
Aquat. Microb. Ecol.
10:87-95.
|
| 6.
|
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.
|
| 7.
|
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].
|
| 8.
|
Kemp, P. F.,
S. Lee, and J. LaRoche.
1993.
Estimating the growth rate of slowly growing marine bacteria from RNA content.
Appl. Environ. Microbiol.
59:2594-2601[Abstract/Free Full Text].
|
| 9.
|
Kramer, J. G., and F. L. Singleton.
1993.
Measurement of rRNA variations in natural communities of microorganisms on the southeastern U.S. continental shelf.
Appl. Environ. Microbiol.
59:2430-2436[Abstract/Free Full Text].
|
| 10.
|
Lebaron, P.,
M. Troussellier, and P. Got.
1993.
Accuracy and precision of epifluorescence microscopy count for direct estimates of bacterial numbers.
J. Microbiol. Methods
19:89-94.
|
| 11.
|
Lebaron, P.,
P. Catala,
C. Fajon,
F. Joux,
J. Baudart, and L. Bernard.
1997.
A new sensitive, whole-cell hybridization technique for detection of bacteria involving a biotinylated oligonucleotide probe targeting rRNA and tyramide signal amplification.
Appl. Environ. Microbiol.
63:3274-3278[Abstract].
|
| 12.
|
Li, W. K. W.,
J. F. Jellett, and P. M. Dickie.
1995.
DNA distributions in planktonic bacteria stained with TOTO or TO-PRO.
Limnol. Oceanogr.
40:1485-1495.
|
| 13.
|
Maniatis, T.,
E. F. Fritsch, and J. Sambrook.
1982.
In
Molecular cloning: a laboratory manual.
Cold Spring Harbor Laboratory, Cold Spring Harbor, N.Y.
|
| 14.
|
Marie, D.,
D. Vaulot, and F. Partensky.
1996.
Application of the novel nucleic acid dyes YOYO-1, YO-PRO-1, and PicoGreen for flow cytometric analysis of marine prokaryotes.
Appl. Environ. Microbiol.
62:1649-1655[Abstract].
|
| 15.
|
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].
|
| 16.
|
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] |
| 17.
|
Ouverney, C., and J. A. Furhman.
1997.
Increase in fluorescence intensity of 16S rRNA in situ hybridization in natural samples treated with chloramphenicol.
Appl. Environ. Microbiol.
63:2735-2740[Abstract].
|
| 18.
|
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].
|
| 19.
|
Troussellier, M.,
C. Courties, and A. Vaquer.
1993.
Recent applications of flow cytometry in aquatic microbial ecology.
Biol. Cell
78:111-121[Medline].
|
| 20.
|
Wallner, G.,
R. I. Amann, and W. Beisker.
1993.
Optimizing fluorescent in situ hybridization with rRNA-targeted oligonucleotide probes for flow cytometric identification of microorganisms.
Cytometry
14:136-143[Medline].
|
Appl Environ Microbiol, May 1998, p. 1725-1730, Vol. 64, No. 5
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Copyright © 1998, American Society for Microbiology. All rights reserved.
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