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Applied and Environmental Microbiology, February 2001, p. 539-545, Vol. 67, No. 2
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.2.539-545.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Application of Digital Image Analysis and Flow
Cytometry To Enumerate Marine Viruses Stained with SYBR
Gold
Feng
Chen,1,*
Jing-rang
Lu,2
Brian J.
Binder,2
Ying-chun
Liu,2 and
Robert E.
Hodson2
Center of Marine Biotechnology, University of
Maryland Biotechnology Institute, Baltimore, Maryland
21202,1 and Department of Marine
Sciences, University of Georgia, Athens, Georgia
306022
Received 29 June 2000/Accepted 16 November 2000
 |
ABSTRACT |
A novel nucleic acid stain, SYBR Gold, was used to stain marine
viral particles in various types of samples. Viral particles stained
with SYBR Gold yielded bright and stable fluorescent signals that could
be detected by a cooled charge-coupled device camera or by flow
cytometry. The fluorescent signal strength of SYBR Gold-stained viruses
was about twice that of SYBR Green I-stained viruses. Digital images of
SYBR Gold-stained viral particles were processed to enumerate the
concentration of viral particles by using digital image analysis
software. Estimates of viral concentration based on digitized images
were 1.3 times higher than those based on direct counting by
epifluorescence microscopy. Direct epifluorescence counts of SYBR
Gold-stained viral particles were in turn about 1.34 times higher than
those estimated by the transmission electron microscope method.
Bacteriophage lysates stained with SYBR Gold formed a distinct
population in flow cytometric signatures. Flow cytometric analysis
revealed at least four viral subpopulations for a Lake Erie sample and
two subpopulations for a Georgia coastal sample. Flow cytometry-based
viral counts for various types of samples averaged 1.1 times higher
than direct epifluorescence microscopic counts. The potential
application of digital image analysis and flow cytometry for rapid and
accurate measurement of viral abundance in aquatic environments is discussed.
 |
INTRODUCTION |
Since the discovery of highly
abundant viruslike particles (VLPs) in natural seawater (2, 9,
16), marine viruses have been considered one of the major
factors regulating microbial biomass, population, and genetic diversity
in natural environments. In order to understand the potential impact of
marine viruses on other marine microorganisms, the abundance of viral
particles has been estimated in many marine environments (5, 6,
8, 10, 15, 22). The concentration of viral particles generally exceeds that of bacteria by 5- to 10-fold in many of these environments (8, 10, 15, 22). It is now known that viruses are a
dynamic component in the aquatic microbial food web, so protocols for fast and accurate estimates of VLPs in seawater are needed if a
meaningful understanding of these dynamics is to be achieved.
Two major approaches have been used to enumerate marine viruses in
natural seawater: one is based on transmission electron microscopy
(TEM) (2, 16, 22), and the other is based on a
fluorescent-staining method using epifluorescence microscopy (EFM)
(10, 11, 14, 21). Counting viral particles by TEM is
time-consuming and expensive and is not practical for field studies.
Fluorescent dyes, such as DAPI (4',6'-diamidino-2-phenylindole), YoPro-1
{4-[3-methyl-2,3-dihydro-(benzo-1,3- oxazole)-2-methylmethyledene]-1(3'-trimethylammoniumpropyl)-quinoliniumdiiodide}, and SYBR Green I have been used to enumerate VLPs in marine samples (10, 11, 14). Although counts based on
fluorescent-staining methods are highly correlated with those based on
the TEM method, the former usually yields a higher count than the
latter (14, 21). Moreover, the precision of
fluorescence-based counting is much greater than that of the TEM method
(21).
The development of more sensitive nucleic acid stains has greatly
advanced our ability to visualize stained viral particles by EFM. DAPI,
a DNA-specific fluorochrome, was first used to count viral particles
(18). More recently, the nucleic acid stain YoPro-1
was found to provide a brighter fluorescence intensity than DAPI
when staining marine viruses (11). Because the original staining method with YoPro-1 required an optimal 2-day incubation, a modified protocol involving the microwaving of YoPro-1-stained samples was developed to shorten the staining time to a few minutes (24). Most recently, another sensitive nucleic acid stain,
SYBR Green I, has been used for the rapid and accurate enumeration of
viral particles in various marine samples (14). SYBR Green I yielded a brighter fluorescent signal than DAPI when staining viral particles. However, this fluorescence could fade within 30 s
under some conditions, requiring the use of high concentrations of SYBR
Green I and a special antifading mixture (14). After several existing nucleic acid stains, including DAPI,
YoPro-1, and SYBR Green I, were compared simultaneously, the
modified YoPro-1 staining method (23) was recommended
for enumerating viral particles in aquatic environments
(3). The fluorescence intensity of SYBR Green I was
similar to that of YoPro-1, but SYBR Green I faded much
faster than YoPro-1 (3).
Sensitive detection devices and techniques, such as cooled
charge-coupled device (CCD) cameras or flow cytometry (FCM),
make possible more accurate and rapid enumeration of fluorescently stained microbes or VLPs than EFM. FCM has been used for the
enumeration of total bacteria (4, 13, 17),
Synechococcus and Prochlorococcus groups
(4, 7), or a specific group of microbes detected by a
fluorescently labeled probe in marine environments (1). Recently, FCM has been shown to be capable of enumerating marine viruses stained with SYBR Green I (12). In their study,
Marie et al. had to treat samples with deep freezing or heating at
80°C in the presence of detergent to obtain reliable results with
SYBR Green I (12).
SYBR Gold (Molecular Probes, Inc., Eugene, Oreg.) is another sensitive
fluorescent stain for detecting double- or single-stranded DNA or RNA.
According to the manufacturer, this stain is more sensitive than SYBR
Green I and II for staining nucleic acids in gels. In our preliminary
tests, marine viruses stained with SYBR Gold yielded a bright
fluorescent signal that was much more stable than that from SYBR Green
I. In this study, we demonstrate that SYBR Gold can be a good
alternative fluorochrome for rapidly staining and accurately counting
viral particles in various types of aquatic samples. We also examine
the possibility of using digital image analysis (DIA) and FCM for rapid
and precise enumeration of SYBR Gold-stained marine viruses.
 |
MATERIALS AND METHODS |
Sample collection.
Water samples were collected from three
Georgia coastal rivers, the Satilla, the Altamaha, and the Savannah,
during cruises onboard the R/V Bluefin in July 1998. The
salinity of water samples ranged from 0 to 34
. Samples were
collected 1 m below the surface. Two subsamples (50 ml) were taken
at each station and stored in sterile polypropylene centrifuge tubes.
The first subsample was fixed with glutaraldehyde (2.5% final
concentration) for counting total viruses and bacteria, while the
second, unfixed sample was used for isolation and enumeration of
cyanophages that infect marine Synechococcus spp.
All samples were stored in the dark at 4°C until they were used.
Samples from Lake Erie were kindly provided by Steve Wilhelm at the
University of Tennessee, Knoxville.
Cyanophage strains.
The cyanophages P1 and P49
(Myoviridae), which infect the marine
Synechococcus strains WH7803 and WH7805, respectively, were isolated and purified from the water samples collected from Georgia coastal rivers according to published protocols (20).
Staining viruses with SYBR Gold and SYBR Green I.
The
original SYBR Gold stock solution (10,000×) was diluted to a secondary
stock solution (25×) with high-performance liquid chromatography-grade
water. The secondary SYBR Gold stock solution can be stored at 4°C
for up to 1 month according to our preliminary test. To enumerate viral
particles, viral lysates or natural virus communities were stained with
2.5× (final concentration) SYBR Gold solution for 10 min in the dark
and filtered through a 0.02-µm-pore-size Al2O3 Anodisc membrane filter (Whatman Inc.,
Clifton, N.J.), backed by a 0.2-µm-pore-size cellulose membrane
(Gelman Sciences, Ann Arbor, Mich.) at approximately 20 kPa vacuum. The
stained Anodisc filter was mounted on a glass slide with a drop of Slow
Fade (Molecular Probes, Inc.) and a coverslip. When SYBR Gold was
compared with SYBR Green I, two different concentrations (2.5× and
25×) of SYBR stains were tested using the protocol described by Noble
and Fuhrman (14).
In this study, three different methods were used for enumerating
SYBR-stained viral particles: (i) direct count from EFM, (ii) DIA, and
(iii) FCM analysis.
EFM.
Slides were examined under a BX-40 (Olympus America
Inc., Melville, N.Y.) epifluorescence microscope with an ×100
high-resolution U Plan Oil objective lens (N. A. = 1.35 to 0.50).
Viruses and bacteria stained with SYBR Green I or SYBR Gold were
visualized with blue excitation light. To estimate the concentration of
stained viruses, at least 300 viruses were counted.
DIA.
Images from the microscopic viewfield were acquired
with a cooled CCD, SenSys:1400 (1,317 by 1,035 image array; 6.8- by
6.8-µm pixel; 12 bit) (Photometrics, Tucson, Ariz.) and processed
with the Oncor image software package version 2.02 (Oncor, Inc.,
Gaithersburg, Md.) on a Power Macintosh 9500. To enumerate viral
numbers in culture lysates or field samples, 5 to 10 images were
captured for each sample and all the images were processed with
identical image analysis functions, e.g., exposure time, focusing,
thresholding, object identification, and counting. After a digital
image was focused and acquired, it was processed with the Enhance VEC
image function. Objects were then defined with the interactive notch tool. Viruses were counted as a category with the pixel value that
ranged from 5 (minimum) to 12, while bacteria were counted as a
category with the pixel value that ranged from 13 to 100. Alternatively, viruses and bacteria can also be counted manually by
examining the digital images on the computer screen.
FCM.
Virus samples stained with SYBR Gold and SYBR Green I
were analyzed on an EPICS 753 flow cytometer (Coulter Corp., Miami, Fla.) equipped with a 5-W argon ion laser (tuned to 488 nm; 750-mW output) and modified for high sensitivity as described previously (4). SYBR Gold or SYBR Green I fluorescence was measured
above 495 nm; data collection was triggered on this signal. All the samples used for FCM analysis were diluted with TE buffer (10 mM Tris,
1 mM EDTA, pH 7.5). Cyanophage lysates were diluted 1:100 to 1:1,000,
while natural water samples were diluted 1:10.
TEM.
Thirty-five milliliters of viral sample was transferred
into a 36-ml ultracentrifuge tube (Sorvall, Inc., Newtown, Conn.), in
which two carbon- and Formvar-coated electron microscopy grids had been
presettled on a solid platform made of epoxy glue. Viral particles were
then spun onto the grids with an ultracentrifuge (Sorvall
Discovery 100S) with a SURESPIN 630 swinging bucket rotor (Sorvall
Inc.) at 166,800 × g and 4°C for 4 h. The
samples on the grids were then stained with 2% urinate acetate for 1 min. Viral particles were enumerated by TEM (JEOL 100 CXII at 80 kV and
×27,000 magnification), located in The Microscopic Center of The
University of Georgia. More than 200 viral particles were counted for
each sample, and the virus concentration was calculated as described
elsewhere (19).
 |
RESULTS AND DISCUSSION |
Viruses stained with SYBR Gold.
Viral particles in
cyanophage lysates and natural water samples stained brightly
with SYBR Gold. Cyanophages P1 and P49 stained with SYBR Gold
yielded a bright and stable yellow-green fluorescence under EFM and
could be easily detected by a cooled CCD camera (Fig.
1A). When SYBR Gold was tested in
natural samples with salinities ranging from 0 to 34.8
, viral
particles and bacteria in all natural communities yielded bright
yellow-green fluorescence. Due to their larger genomic sizes, SYBR
Gold-stained bacteria usually yielded much brighter fluorescence than
SYBR Gold-stained viruses. Among viruses, the brightness of the SYBR
Gold signal varied, likely due to different genome sizes (20 to 300 kb)
among viral particles (Fig. 1B). Under blue excitation, a majority of
the detrital materials in our samples yielded orange-red
fluorescence that was readily distinguished from the yellow-green
fluorescence of SYBR Gold-stained viruses. Because SYBR Gold
specifically stains nucleic acids, we were able to count viral
particles that were adsorbed onto detrital material.

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FIG. 1.
Digital images of SYBR Gold-stained viruses. Cyanophage
P49 particles (A) and viral and bacterial communities (B) in a Georgia
coastal water sample, July 1998, are shown. v, virus; b, bacteria.
Scale bars, 5 µm.
|
|
In a comparison between SYBR Gold and SYBR Green I, it was found that
the fluorescence of SYBR Gold-stained viruses lasted
longer than that
of SYBR Green I-stained viruses when the standard
concentration (2.5×)
was used for both stains (data not shown).
Without any antifading
solution, the fluorescence of SYBR Gold-stained
viruses was stable for
more than 2 min, while the SYBR Green I
signal faded within 30 s.
In a recent study, SYBR Green I was
found to fade faster than most
other nucleic acid stains (e.g.,
DAPI and Yo-Pro) that have been used
to stain viral particles
in aquatic environments (
3). The
stability of SYBR Gold fluorescence
represents a distinct advantage for
the accurate enumeration of
viruses by EFM with a cooled CCD camera.
Although the fluorescence
of both SYBR Gold- and SYBR Green I-stained
viruses was brighter
and more stable when a higher concentration of
stain (25×) was
used (
14), it was found that under these
conditions many bacterial
cells were overstained, and the resultant
fluorescent halos around
those cells could mask the fluorescence of the
stained
viruses.
Comparison of viral counts by TEM and EFM.
A direct comparison
of 10 natural samples from the Satilla River showed that EFM- and
TEM-based counts were highly correlated (r = 0.975; n = 10) (Fig. 2). However, estimates of
viral abundance based on the EFM method were generally higher (by a
factor of 1.34 on average) than those made by TEM. The results of other studies comparing EFM- and TEM-based viral counts are similar (9,
13, 19). Thus, for example, SYBR Green I-based viral counts were
found to be about 1.28 times higher than those by TEM
(14). It appears, therefore, that TEM-based counts
generally underestimate viral abundance. Several factors might
contribute to lower counts by the TEM method: (i) loss of viral
particles during staining and washing of grids, (ii) high background
due to sedimentation of detrital materials onto grids, and (iii)
nonparallel paths of viral sedimentation during ultracentrifugation
(19). Most of the samples collected from Georgia coastal
rivers contained large amounts of detrital material. High background
due to detritus was believed to result in lower TEM counts in these
samples, but it did not appear to interfere with EFM counts.

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FIG. 2.
Comparison of viral abundance values based on EFM with
SYBR Gold and TEM in 10 natural water samples with salinities ranging
from 0 to 34.8 . The solid line corresponds to a linear regression:
y = 1.34x + 0.66 (r = 0.975; n = 10).
|
|
Enumeration of SYBR Gold-stained viruses by DIA.
When viral
abundance must be determined in many natural samples, a fast and
accurate enumeration method is necessary. One of the major concerns
with the EFM-based method is how to differentiate small bacterial cells
from viral particles. A certain proportion of bacterial cells in
natural aquatic samples can be very small, and therefore, they may be
confused with viruses. In such a case, counting fluorescently stained
viral particles directly by microscopy could be tedious. It was found
that digital images recorded by the cooled CCD camera appeared to show
more viral particles, suggesting that it could detect some weakly
stained viruses that could not be easily detected by human eyes.
Estimates of virus numbers based on EFM were compared with those based
on DIA (Fig. 3). The 12 samples were all
collected from the Savannah and Altamaha River estuary along the
Georgia coast, and their salinities ranged from 0 to 30
. There was a
strong linear correlation between the counts by DIA and those by direct
EFM (r = 0.896; n = 12); however, the DIA counts
were on average 1.31 times higher than the EFM counts. The use of a
cooled CCD camera and DIA allowed us not only to detect the weakly
stained viral particles but also to enumerate hundreds of viral
particles at one time. Digital images of SYBR-stained samples can be
quickly captured by a CCD camera and saved for later processing.
Therefore, a much higher number of viruses can be counted for a given
amount of microscope time.

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FIG. 3.
Relationship of SYBR Gold-stained viruses enumerated by
DIA and direct EFM counting. Twelve samples collected from three
Georgia coastal rivers were used for this analysis. The solid line
indicates a linear regression: y = 1.31x 0.77 (r = 0.896; n = 12).
|
|
Enumeration of SYBR Gold-stained viruses by FCM.
SYBR
Gold-stained cyanophages P1 and P49 (Myoviridae)
formed distinct populations in flow cytometrically measured side
scatter versus green fluorescence (Fig. 4A and B,
respectively). The marine cyanophages used in this experiment are representative of most bacteriophages in natural aquatic environments in terms of size and
morphology (2). In a recent study, viruses which infect Phaeocystis pouchetii were stained with SYBR Green I and
used as a reference strain for FCM analysis (12). However,
most marine viruses infecting microalgae are large polyhedral viruses
(100 to 170 nm in diameter); they are therefore not representative of
natural (bacteriophage-dominated) viral communities. We found that SYBR
Gold can be used to rapidly stain phage isolates whether they have been
fixed with 2.5% glutaraldehyde or not. FCM counts of
cyanophage lysates were highly reproducible, and for phage P49,
they averaged about 1.25 times higher than counts based on EFM (Table
1). Although SYBR Gold-stained phage
lysates were very bright under EFM, difficulty in obtaining a uniform
focal plane for all viral particles could result in the observed
underestimation of the actual number of viruses. The fluorescence
intensities of viruses stained with SYBR Gold and SYBR Green I were
also compared by FCM. The mean fluorescence per P49 virus determined
with SYBR Gold was about two times higher than that with SYBR Green I,
while the standard deviation was significantly lower (Fig.
5). The samples we used in this study had
a wide range of salinities (0 to 34.8
), but we found no significant
impact of salinity on SYBR Gold staining. Finally, SYBR Gold is a much
less expensive nucleic acid stain than SYBR Green I.

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FIG. 4.
Flow cytometric analysis of SYBR Gold-stained
cyanophages P1 (A) and P49 (B). The dots represent individual
particles.
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FIG. 5.
Flow cytometric fluorescence distribution of
cyanophage P49 particles that were stained with SYBR Gold
(shaded) and SYBR Green I (open). Both samples were stained with the
nucleic acid stain at the final concentration of 2.5×. The histograms
are gated as shown in Fig. 4.
|
|
FCM not only allows rapid and automated counts but also provides enough
resolving power to separate different viral populations
in the natural
samples. FCM analysis of a sample from Lake Erie
(Fig.
6A) revealed at least four different
populations of SYBR
Gold-stained particles. Population V-III had
scatter and fluorescence
characteristics similar to those observed for
the cyanophages
P1 and P49. Populations V-I and V-II were much
less abundant and
may represent larger viral particles or some very
small bacteria
in Lake Erie. More than 98% of the SYBR Gold-stained
particles
were removed after the sample was filtered through a
0.02-µm-pore-size
Anodisc filter (Fig.
6B and Table
1). The viral
concentration
at Lake Erie Station 84 obtained by FCM was approximately
1.2
times higher than those obtained by direct EFM counting (Table
1).

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FIG. 6.
Flow cytometric analysis of viral populations from a
Lake Erie sample (A), the same sample filtered through a
0.02-µm-pore-size filter (B), and a Georgia coastal sample (C).
Populations V-I through V-IV are indicated.
|
|
FCM analysis of a seawater sample from the Georgia coast revealed two
distinct populations (Fig.
6C). The dominant population
(V-II) had
scatter and fluorescence characteristics similar to
those observed for
the cyanophages P1 and P49, while the minor
population (V-I)
may represent larger viruses, perhaps those infecting
eukaryotic
microalgae (
12). Viruses in population V-I not only
have
higher side scatter but also have higher fluorescence intensity
than
viruses in population V-II (Fig.
6C). The viral concentration
in
population V-II was about 10-fold higher than that in population
V-I
(Table
1). In an earlier study, two to three viral populations
were
seen in natural marine environments, analogous to the populations
observed here (
12). In that study, the V-II population was
4-
to 10-fold more abundant than the V-I population. A small but
significant portion (14%) of viral population V-II passed through
a
0.02-µm-pore-size filter, while nearly all of population V-I
was
removed. The viral counts in this seawater sample obtained
by FCM were
74 to 88% of those obtained by EFM (Table
1). It
was not clear why FCM
yielded lower counts for this natural seawater
sample. However, we did
notice that under EFM, viral particles
in the natural seawater sample
were not stained as brightly as
in the sample from Lake Erie. This may
be due to the fact that
smaller viruses were more abundant in the
seawater sample than
in the lake sample. In general, marine viruses
with 20- to 100-kb
genomes or with 30- to 60-nm capsid size made up the
majority
of the total virioplankton. The 30- to 60-nm capsid size of
aquatic
virioplankton is slightly smaller than the 60- to 80-nm range
observed for purified marine bacteriophages (
23). Even
with
very sensitive nucleic acid stains, like SYBR Green I or SYBR
Gold, it should be noted that some of the stained viral particles
were
only slightly above the background noise by FCM (Fig.
6).
We therefore
cannot exclude the possibility that some viral particles
fall
below the limits of detection in the FCM configuration used
here.
A recent study found that natural virus communities stained by SYBR
Green I shortly after fixation showed a lower percentage
of viral
counts by FCM than those analyzed by EFM (
12). It
was
suggested that fresh viruses may not be very accessible to some
nucleic acid stains, e.g., SYBR Green I, PicoGreen, SYTOX,
and
TOTO-1 (
12). However, such a hypothesis does not seem
to apply
to bacteriophages or other virus isolates because they can be
stained brightly and usually form a distinguishable FCM pattern.
FCM
analysis of natural viral communities stained with SYBR Green
I require
fixed samples to be deep frozen or heated at 80°C in
the presence of
detergent (
12). Our observations suggested that
heating at
80°C in the presence of detergent often resulted in
nearly 20% lower
counts than in the untreated samples (not shown).
We also noticed that
viral counts based on the SYBR Gold staining
method decreased over time
for the samples that were fixed in
glutaraldehyde and kept at 4°C.
Therefore, it is important to
count viral particles in the fixed
samples shortly after fixation
to obtain accurate estimates of the
viral concentration in natural
environments.
This study focused mainly on developing a rapid technique for counting
viral particles in freshwater and marine environments
using the SYBR
Gold nucleic acid stain. We did not intend to count
bacterial cells,
although bacteria stained with SYBR Gold could
be enumerated by both
the DIA and FCM methods (not shown). We
demonstrated that SYBR Gold is
an alternative dye for rapidly
staining and counting viral particles in
natural aquatic samples.
Viral counts based on DIA or FCM proved to be
more efficient and
accurate for estimating the numbers of viral
particles in natural
environments than direct counting by
EFM.
 |
ACKNOWLEDGMENTS |
We acknowledge support from the following U.S. funding agencies:
the National Science Foundation (OCE-9730602 and OCE-0049098), the
Department of Energy (DE-FG02-97ER62451), and NOAA/Sea Grants Program (NA66RG0282).
We thank Steve Wilhelm at the University of Tennessee for providing the
lake samples and Stephan Jacquet for his suggestions on the manuscript.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Center of Marine
Biotechnology, University of Maryland Biotechnology Institute, 701 East
Pratt St., Suite 236, Baltimore, MD 21202. Phone: (410) 234-8866. Fax:
(410) 234-8896. E-mail: chenf{at}umbi.umd.edu.
Contribution no. 542 from the Center of Marine Biotechnology,
University of Maryland Biotechnology Institute.
 |
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Applied and Environmental Microbiology, February 2001, p. 539-545, Vol. 67, No. 2
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.2.539-545.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
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