Previous Article | Next Article 
Applied and Environmental Microbiology, January 1999, p. 45-52, Vol. 65, No. 1
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Enumeration of Marine Viruses in Culture and
Natural Samples by Flow Cytometry
Dominique
Marie,1,*
Corina P. D.
Brussaard,2
Runar
Thyrhaug,2
Gunnar
Bratbak,2 and
Daniel
Vaulot1
Station Biologique, CNRS, INSU and
Université Pierre et Marie Curie, 29682 Roscoff cedex,
France,1 and
Department of
Microbiology University of Bergen, N-5020 Bergen,
Norway2
Received 26 May 1998/Accepted 6 October 1998
 |
ABSTRACT |
Flow cytometry (FCM) was successfully used to enumerate viruses in
seawater after staining with the nucleic acid-specific dye SYBR
Green-I. The technique was first optimized by using the Phaeocystis lytic virus PpV-01. Then it was used to analyze
natural samples from different oceanic locations. Virus samples were
fixed with 0.5% glutaraldehyde and deep frozen for delayed analysis. The samples were then diluted in Tris-EDTA buffer and analyzed in the
presence of SYBR Green-I. A duplicate sample was heated at 80°C in
the presence of detergent before analysis. Virus counts obtained by FCM
were highly correlated to, although slightly higher than, those
obtained by epifluorescence microscopy or by transmission electron
microscopy (r = 0.937, n = 14, and
r = 0.96, n = 8, respectively). Analysis of a depth profile from the Mediterranean Sea revealed that
the abundance of viruses displayed the same vertical trend as that of
planktonic cells. FCM permits us to distinguish between at least two
and sometimes three virus populations in natural samples. Because of
its speed and accuracy, FCM should prove very useful for studies of
virus infection in cultures and should allow us to better understand
the structure and dynamics of virus populations in natural waters.
 |
INTRODUCTION |
Quantification of the different
biological components present in an ecosystem is one of the first
tasks of any ecological investigation. Much effort has been devoted to
developing methods for detecting, recognizing, and enumerating
different microorganisms such as protozoa, microalgae, bacteria, and
viruses that thrive in natural waters. Viruses infecting algae and
bacteria are abundant and active components of aquatic ecosystems. The
occurrence of bacteriophages has been known for many years (14,
24, 25), but they have not been really investigated until
recently. In the last decade, a number of studies have pointed out the
ecological importance of viruses in the marine microbial food web
(2, 22) and their potential impact on genetic exchange
between marine organisms (1, 22).
Diverse culturing and microscopic techniques have been used to estimate
the number of viruses in natural waters. The culturing techniques for
algal viruses and bacteriophages include plaque counts and
most-probable-number techniques (6, 8, 29, 31). The
advantage of these assays is that they detect only viruses that are
infective for a specific host. This is, however, also a major
limitation, because the virus susceptibility of the strains used as
assay hosts may be different from the virus susceptibility of the field
strains from the same species (7, 28, 31).
The microscopic techniques include transmission electron microscopy
(TEM) (1, 4, 33) and epifluorescence microscopy (EFM)
combined with fluorescent staining of the viruses (11, 12, 19,
23). For TEM, viruses are harvested directly onto electron
microscopy grids by centrifugation (3) or are concentrated by ultrafiltration and transferred to grids (21, 22).
Analysis by TEM is time-consuming and requires expensive and bulky
equipment, two drawbacks which are not compatible with routine field
studies (1, 5, 21, 33). For EFM, the virus samples are
usually collected on 0.02-µm-pore-size filters, stained with a
DNA-specific fluorescent dye such as DAPI, YO-PRO-1,
YOYO-1, POPO-1, or SYBR Green, and viewed under a standard
epifluorescence microscope. EFM renders virus detection accessible to
field analysis (11, 12, 23, 26), but it is also laborious.
Flow cytometry (FCM) has been routinely used for the analysis of
microorganisms in marine samples for the last decade and is now
commonly accepted as a reference technique in oceanography. Initially
used to discriminate and enumerate the different phytoplanktonic populations (20), it has been more recently applied to the
analysis of the heterotrophic bacterial community (15,
18). The major advantage of FCM resides in the possibility of
rapidly analyzing a large number of cells and providing statistically
significant data. This technique is also amenable to shipboard analysis
(20). The increase in sensitivity of recent flow cytometers
and the introduction of a new generation of nucleic acid-specific
stains like TOTO-1, YOYO-1, PicoGreen, or SYBR Green-I (SYBR-I) have considerably improved the limit of detection of FCM
(15-17).
In this paper, we report the use of FCM to detect marine viruses
stained with the novel nucleic acid stain SYBR-I and compare this
method with TEM and EFM. The method was first optimized with algal virus cultures and then was applied to field samples from different oceanic regions, such as the English Channel, the Equatorial Pacific, and the Mediterranean Sea.
 |
MATERIALS AND METHODS |
Cultures.
The algal-host-virus system used in this study
was Phaeocystis pouchetii AJ01, obtained from the culture
collection at the University of Bergen, Bergen, Norway, and the lytic
virus PpV-01 (130 to 160 nm in diameter), isolated from Raunefjorden,
Western Norway (13). The algal culture was made axenic after
treatment with the antibiotics carbenicillin (0.01 g ml
1;
Sigma Chemical Co.) and cefotaxime (0.01 g ml
1; Sigma).
The virus culture was made axenic after double filtration over
0.2-µm-pore-size Supor 200 filters (Gelman Sciences).
Phaeocystis was grown in f/2 (9), based on aged
seawater, with the modifications that KH2PO4
and NaNO3 were added at 5 and 80 µM respectively. The
temperature of the cultures was maintained at 8.0 ± 0.5°C, and
light was supplied as a light-dark cycle of 16 and 8 h at a photon
flux density of 100 ± 20 µmol m
2
s
1.
For the infection experiment, a culture at an algal concentration of
3.5 × 105 cells ml
1 was split into two
subcultures of 300 ml each (in sterile 1-liter Erlenmeyer flasks). One
of the subcultures was infected with 40 ml of virus lysate, while the
other subculture served as control. Samples for algal cell and virus
counts were taken at regular intervals of generally 2 to 6 h.
After fixation with 0.5% (final) glutaraldehyde (25%, grade I;
Sigma), subsamples were either stored directly at 4°C or quickly
frozen in liquid N2 and stored at
80°C.
Natural seawater samples.
Equatorial Pacific (150°W,
16°S) samples were collected with Niskin bottles during the OLIPAC
cruise onboard the N.O. l'Atalante in November 1994. In the
Mediterranean Sea (18°E, 34°N), vertical profiles were collected
during the MINOS cruise in June 1996 onboard the N.O.
Suroit. Surface seawater samples from the English Channel (Station
Estacade, Roscoff, France) were collected with a bucket in February and
March 1998. Phytoplanktonic cells were enumerated on fresh samples,
onboard for the Mediterranean Sea and Pacific Ocean samples and in the
laboratory for the English Channel samples. For bacterial and viral
enumeration, an aliquot (1.5 ml) was fixed for 15 min with
glutaraldehyde at 0.5 and 0.1% (final concentrations) for the English
Channel and Equatorial Pacific samples, respectively, or with a mixture
of 1% paraformaldehyde and 0.05% glutaraldehyde for the Mediterranean
Sea samples. The samples were then deep frozen in liquid nitrogen and
preserved at
80°C until analysis. Bacteria were counted onboard for
the Mediterranean Sea samples and in the laboratory for the Pacific
Ocean and English Channel samples.
EFM.
During the viral infection experiment with
Phaeocystis, 50 µl of fixed sample (4°C) was diluted
with autoclaved medium filtered onto 0.2-µm-pore-size Anodisc 25 (Whatman) and stained for 5 min with a 0.2-µm-pore-size-filtered
4',6-diamidino-2-phenylindole (DAPI) solution (1:1 [vol/vol] of a
10-µg-ml
1 stock solution [Sigma]). After filtration
of 400 µl of the solution onto a 0.2-µm-pore-size black membrane
filter (Poretics) or a 0.02-µm-pore-size Anodisc 25 filter (Whatman),
viruses were counted immediately on a Olympus BH-2 microscope at
×1,000 with Citifluor (phosphate-buffered saline solution AF 3;
Citifluor Ltd., London, England) as an antifading agent. Filtered
subsamples were also stained with SYBR-I (Molecular Probes Inc.), and
the filters were mounted onto a glass slide with 0.1%
p-phenylenediamine in phosphate-buffered saline-glycerol
(1:1) as described by Noble and Fuhrman (19). The optical
density at 495 nm of the SYBR-I stock solution diluted 1,000-fold in
distilled water (lot 0561-3) was 0.682.
TEM.
A 3-ml sample of the fixed virus samples was
centrifuged onto grids (Ni, 400 mesh) for 30 min at 36,000 rpm in a
Beckman SW 41 swingout rotor (3). The grids were positively
stained with 2% uranyl acetate and viewed in a JEOL 100S transmission
electron microscope at ×20,000 to ×100,000 magnification.
FCM.
All experiments were performed with a FACSort flow
cytometer (Becton Dickinson, San Jose, Calif.) equipped with an
air-cooled laser providing 15 mW at 488 nm and with the standard filter
setup. For photosynthetic-cell enumeration, samples were run for 4 min at a rate of 90 µl min
1 and the discriminator was set
on red fluorescence. Bacterial samples were stained with SYBR-I at a
final concentration of 10
4 of the commercial stock
solution (17). The samples were incubated for 15 min in the
dark, the discriminator was set on green fluorescence, and the samples
were analyzed for 1 min at a rate of 50 µl min
1.
For virus enumeration, dilutions from 1:100 to 1:2,000 for culture
samples and from 1:10 to 1:200 for natural samples were
performed in TE
buffer (10 mM Tris, 1 mM EDTA [pH 7.5]), to avoid
coincidence on the
flow cytometer and to minimize the error due
to low-volume pipetting.
Dilutions were divided into two aliquots
of 500 µl each. One was
incubated for 15 min in the dark in presence
of SYBR-I at a final
concentration of 0.5 × 10
4. The second was
incubated for 10 min at 80°C in presence of SYBR-I
(0.5 × 10
4) and Triton X-100 (0.1%). The latter treatment was
not necessary
for fixed-frozen samples but essential for samples that
were not
frozen (see Results). We chose to use this treatment as a
reference
for virus enumeration. Samples were analyzed by flow
cytometry
for 1 to 4 min at a delivery rate of 50 µl
min
1. The discriminator was set to green fluorescence,
which is proportional
to the nucleic acids-SYBR-I complex, and the
detection threshold
was progressively decreased until viruses could be
detected (see
below), but care was taken to avoid detecting more than
1,000
events per s, a threshold above which coincidence occurs,
resulting
in the underestimation of particle abundance. Parameters were
collected on logarithmic scales and analyzed with the custom-designed
software CYTOWIN (
30; available freely at
http://www.sb-roscoff.fr/Phyto/cyto.html)
that discriminates cell
populations by using combinations of all
recorded
parameters.
 |
RESULTS |
Optimization of the fixation and staining procedures.
Preliminary tests with Phaeocystis virus samples stained
with SYBR-I indicated that FCM could detect a population of fluorescent particles clearly above background but with much lower fluorescence than that usually displayed by bacteria (Fig.
1). For unfrozen Phaeocystis
virus samples fixed with 0.5% glutaraldehyde, dilution in culture
medium (Fig. 1A) or in 0.2-µm-pore-size-filtered seawater (Fig. 1B)
resulted in counts five- to sixfold lower than those obtained after
dilution in TE buffer (Fig. 1C). Samples diluted in culture medium
(Fig. 1A) displayed higher background than those diluted in seawater
(Fig. 1B). FCM analysis of unfrozen samples diluted in TE (Fig. 1C)
still displayed virus counts 3- to 10-fold lower than those obtained by
EFM. Fixation with different concentrations of glutaraldehyde ranging
from 0.1 to 1% had no effect on virus enumeration. Aliquots of the
virus suspension were heated for 10 min at 70°C after fixation with
different concentrations of paraformaldehyde or glutaraldehyde. Virus
counts obtained after this treatment and after staining by SYBR-I were
highly correlated with counts obtained by EFM. Varying the incubation
temperature between 50 and 95°C or adding SYBR-I before or after
heating did not affect the quality of the staining. In contrast,
addition of 0.1% Triton X-100 before heating improved the signal,
inducing a decrease in the coefficient of variation of the viral
population and an increase in the intensity of the green DNA
fluorescence (data not shown). Furthermore, we observed a global
decrease of viral counts (measured by either FCM or TEM) with time for
a suspension fixed with either 0.1 to 0.5% glutaraldehyde or 0.5 to
1% paraformaldehyde and stored at 4°C. We observed an excellent
correlation between FCM and EFM counts for samples that were frozen in
liquid nitrogen after fixation and diluted in TE buffer after thawing
(Fig. 1D). Heating such samples (10 min at 80°C) and incubating them
with detergent (0.1% Triton X-100) did not change the virus counts. This suggested that heating is necessary only for samples that have not
been frozen in liquid N2.

View larger version (30K):
[in this window]
[in a new window]
|
FIG. 1.
FCM analysis of P. pouchetii samples
collected 24 h after the beginning of a viral infection
experiment. Samples were analyzed after fixation with 0.5%
glutaraldehyde and staining with 5 × 10 4 of the
commercial solution of SYBR-I. (Left) Side scatter versus green DNA
fluorescence (SYBR-I). (Right) Monoparametric green DNA fluorescence
distribution of viruses. Each histogram contains 10,000 events. (A to
D) Infected cultures; (E) uninfected culture. Samples were analyzed
either immediately after fixation (A to C) or following freezing in
liquid nitrogen and storage at 80°C (D and E). Samples were diluted
in culture medium (A), 0.2-µm-pore-size-filtered seawater (B), or TE
buffer (C to E).
|
|
At a final concentration of SYBR-I of 10
4 (usually used
for bacteria [
17]), staining was not very stable at
low virus concentrations,
the signal tended to decrease a few seconds
after the beginning
of analysis, and viruses became difficult to
separate from background
noise due to unspecific staining of cellular
debris or particulate
matter. We chose a SYBR-I concentration of
0.5 × 10
4, which gave the best results both for the
analysis of suspensions
containing low concentrations of viruses and
for the homogeneity
of the
staining.
Comparison of different counting techniques.
Detailed
comparisons between FCM, TEM, and EFM enumeration of viruses were
performed during a Phaeocystis infection experiment on
samples fixed with 0.5% glutaraldehyde, frozen in liquid nitrogen, and
stored at
80°C until analysis. The three techniques gave very
similar trends during the experiment (Fig.
2), and counts obtained by FCM were
highly reproducible for the different dilutions analyzed (Table
1; Fig. 3).
Although a good linear relationship was observed between FCM and EFM
and between FCM and TEM (r = 0.97, n = 14, and
r = 0.96, n = 8, respectively), the FCM counts were about 30% higher than those obtained by EFM and differences of up
to 15% were observed with respect to TEM (Table 1; Fig. 3). At 24 h after the beginning of the experiment, the virus concentration increased in the infected culture (Fig. 2). In both infected and uninfected cultures, the level of debris increased with time but no
virus population could be discriminated in the latter cultures (Fig.
1E).

View larger version (20K):
[in this window]
[in a new window]
|
FIG. 2.
Infection experiment of P. pouchetii.
Phaeocystis cells were enumerated by FCM for uninfected (open
triangles) and infected (open circles) cultures. Virus counts were
performed by three different techniques: EFM (solid triangles), TEM
(solid circles), and FCM (solid squares). Virus counts reported for FCM
correspond to the average value of counts obtained on 0.5%
glutaraldehyde-fixed samples, frozen in liquid nitrogen, at different
dilutions and analyzed after incubation at room temperature (Table 1)
or after heating at 80°C in the presence of Triton X-100.
|
|

View larger version (18K):
[in this window]
[in a new window]
|
FIG. 3.
Infection experiment of P. pouchetii.
Comparison between FCM, EFM, and TEM virus counts obtained for samples
collected every 4 h (Fig. 2; Table 1). FCM versus EFM (solid
circles, straight line; EFM = 0.91 × FCM 8.5 × 106, r = 0.97, n = 14). FCM versus TEM
(solid squares, dotted line, FCM = 0.95 × TEM 3.7 × 106, r = 0.96, n = 8). The
dashed line corresponds to a 1:1 relationship.
|
|
To make sure that our EFM counts were not biased, we compared different
EFM filter and dye combinations (black 0.2-µm-pore-size
and white
0.02-µm-pore-size filters; DAPI and SYBR-I) by using
different
dilutions of a
Phaeocystis virus suspension (Table
2).
The EFM counts were identical for the
different filters and dyes
used. They were higher than FCM counts at
low dilutions but were
35% lower at the highest dilutions (Table
2).
In the latter case,
not enough viruses were counted by FCM, leading to
statistically
insignificant results. At low dilutions, the FACSort
began to
display coincidence, resulting in an underestimation of virus
counts, when there were more than 1,000 events per s. It is therefore
critical to adjust the flow rate or sample dilution to remain
below
this level.
View this table:
[in this window]
[in a new window]
|
TABLE 2.
Comparison of virus numbers obtained with different
dilutions of a Phaeocystis virus suspension fixed with 0.5%
glutaraldehyde and immediately frozen in liquid nitrogen and
analyzed by FCM after staining with SYBR-I or by EFM after
staining with DAPI or SYBR-Ia
|
|
Natural seawater samples.
Analysis of natural samples from
three different oceanic regions ranging from mesotrophic to
oligotrophic conditions revealed two populations of SYBR-I-stained
particles that had scatter and DNA fluorescence characteristics similar
to those observed for the Phaeocystis viruses (Fig.
4). In this section, these particles are
referred to as virus particles (V). The V-I and V-II populations differed in their green emission of the nucleic acid-SYBR-I complex (Fig. 4). The virus populations observed in natural samples by FCM
could also be detected by EFM with SYBR-I after filtration onto
0.02-µm-pore-size Anodisc filters. However, the viral counts obtained
by EFM were lower than those obtained by FCM (Table
3), due to the difficulty in clearly
differentiating virus particles from other abundant detritic particles
by microscopy. Virus counts obtained by FCM in the samples from the
Mediterranean Sea and the Equatorial Pacific were about 1.5-fold higher
those obtained by EFM. In contrast, for English Channel samples, which
were analyzed immediately after collection, the EFM and FCM counts
differed by only 10% (Table 3). In the English Channel samples, 80%
of SYBR-I-stainable virus particles passed through 0.2-µm-pore-size filters (Fig. 4C). The filtrate contained 100% of the V-II population, 20% of the V-I population, and no bacteria. Moreover, the V-I group in
the English Channel samples seemed to consist of two subpopulations
(Fig. 4). No virus populations could be detected after filtration
through 0.02-µm-pore-size filters (Fig. 4D).

View larger version (47K):
[in this window]
[in a new window]
|
FIG. 4.
Side scatter versus green fluorescence (SYBR-I) for
surface samples collected in the English Channel and in the Equatorial
Pacific and analyzed by FCM. Samples were run undiluted to enumerate
bacteria (A and E). Then different dilutions were made to analyze
viruses (B and F). Data obtained after filtration of seawater from the
English Channel, through 0.2- or 0.02-µm-pore-size filters, and
stained by SYBR-I are shown (C and D). Only data from a 1:50 dilution
are presented. Proc, Prochlorococcus; B-I, B-II,
B-III, bacteria subpopulations; V-I, V-II, virus subpopulations.
|
|
View this table:
[in this window]
[in a new window]
|
TABLE 3.
Concentration of bacteria and viruses, determined by FCM
and EFM, for surface samples from the English Channel and the
Equatorial Pacific and for samples from a vertical profile
collected in the Mediterranean Sea during the MINOS cruise
(cast 118)a
|
|
Bacterial concentrations in the English Channel, the Mediterranean Sea,
and the Equatorial Pacific were, respectively, 9.1
× 10
5, 3.6 × 10
5, and 6.3 × 10
5 cells ml
1 (Table
3). In the mesotrophic
English Channel, 20 times more
viruses than bacteria and 10-fold more
V-II than V-I viruses were
found. The ratio between viruses and
bacteria was significantly
lower in the more oligotrophic regions
(Mediterranean Sea and
Equatorial Pacific [Table
3]).
The analysis of a depth profile in the Mediterranean Sea (Fig.
5 and
6)
revealed that the abundance of virus particles displayed
the same
vertical trend as that of bacteria and phytoplanktonic
cells. Viral
abundance was minimal near the surface, increased
down to 100 and
120 m, where phytoplanktonic cells were maximal,
and then
decreased with depth (Fig.
6A). The ratio between the
V-I and V-II
populations followed the total number of viruses
(Fig.
6B). The minimum
value for this ratio was obtained at the
surface, and the maximum was
obtained between 100 and 130 m.

View larger version (47K):
[in this window]
[in a new window]
|
FIG. 5.
FCM analysis of seawater samples collected at different
depths on a vertical profile in the Mediterranean Sea (18°E, 34°N)
on 18 June 1996 (MINOS cruise, cast 118). Six representative depths
among 12 sampled are shown. Bacteria (left) were enumerated in
undiluted samples stained with 10 4 SYBR-I. For virus
analysis (middle), samples were diluted 100-fold and stained with
5 × 10 5 SYBR-I. Monoparametric green fluorescence
distributions (right), obtained after computation by CYTOWIN and
corresponding to the virus populations, are also shown.
|
|

View larger version (20K):
[in this window]
[in a new window]
|
FIG. 6.
Vertical distributions of Prochlorococcus
(Proc; solid squares), Synechococcus
(Syn; open circles), picoeukaryotes (Euk; solid triangles),
bacteria (Bact; open triangles), and viruses (solid diamonds) and ratio
between V-II and V-I (stars, dashed line) obtained by FCM for a
vertical profile collected in the Mediterranean Sea (18°E, 34°N) on
18 June 1996 (MINOS cruise, cast 111). Samples were collected in Niskin
bottles from 200 m up to the surface. Phytoplanktonic cells and
bacteria were enumerated onboard. Prochlorococcus was
undetectable from the surface down to 80 m because of its weak red
chlorophyll fluorescence. Viruses were analyzed on
paraformaldehyde-preserved samples, and the numbers result from the
average of counts obtained on samples diluted 1:100 and 1:200 in TE
buffer. (A) Logarithmic scale. (B) Linear scale.
|
|
 |
DISCUSSION |
In the past, virus in natural marine samples were detected and
enumerated by TEM (see, e.g., reference 22). More
recently EFM and nucleic acid-specific fluorescent stains, such as DAPI and YO-PRO-1, have been shown to result in more accurate and more easily performed enumeration (12, 32). In the present study, we have gone one step further, by combining SYBR-I staining with detection by a sensitive and widely available method, FCM. This constitutes a real improvement for the study of viral communities, especially because this method is less time-consuming and less operator dependent than other counting techniques such as TEM and EFM
(FCM typically allows around 200 samples per day to be processed during
a typical cruise, i.e., about 5 to 10 times as many as by EFM).
Nevertheless, TEM and EFM can provide complementary information, such
as the detection of viruses that are attached to or internalized into
host cells or to differentiate different morphotypes. As with EFM or
TEM, FCM analysis of viruses can be performed on glutaraldehyde- or
paraformaldehyde-fixed samples permitting delayed analysis. A good
correlation was obtained between TEM, EFM, and FCM virus counts (Fig.
3), but viral counts by FCM were generally higher. FCM counts appeared
highly reproducible (Table 1), and this technique allows the
enumeration of viruses in solution at concentrations too low to be
counted by the other methods (Table 2).
Samples analyzed by FCM shortly after fixation showed a low percentage
of stained viruses compared to those analyzed by the microscopic
techniques. However, heating such samples to 95°C in the presence of
detergent or freezing in liquid nitrogen resulted in viral counts
comparable to TEM or EFM counts. Our observations suggest that fresh
viruses may have a structure that makes the nucleic acids not
immediately accessible to SYBR-I or to the other nucleic acid-specific
dyes that we also tested, such as PicoGreen, SYTOX, and the intercalary
cyanine dye TOTO-1 (data not shown). Detergent or heat treatment may
denature the viral capsid, allowing the stain to penetrate. For both
paraformaldehyde- and glutaraldehyde-fixed samples, we observed a
decreased in virus number over time when the samples were kept at
4°C. This decline of virus concentration at 4°C could be due to
aggregate formation or to virus degradation by nucleases, as observed
for bacterial samples in seawater (10).
Viruses constitute the most abundant group of nucleic acid-containing
particles in the ocean (7), and estimates based on TEM range
from 105 to 108 ml
1 (1, 2,
5, 11, 12, 22, 27). In pond water (19) or in estuarine
environments (21), viral abundance reach 106 to
107 ml
1 and exceed the bacterial abundance by
fivefold, while in oligotrophic waters viral and bacterial abundance
have been reported to be quite similar from 2.0 to 4.0 × 105 per ml. Other authors found that virus concentrations
exceeded the bacterial abundance by 10-fold in Norwegian Fjords, with
bacterial counts between 1.0 × 105 and 4.0 × 105 cell ml
1 (5). In the present
work, bacterial abundance measured in three different oceanic areas
agreed with the literature values, while viral concentrations were
about 10-fold higher than bacterial concentrations, ranging from
0.2 × 107 ml
1 in the oligotrophic
waters of the Equatorial Pacific or the Mediterranean Sea to 1.8 × 107 ml
1 in coastal waters of the English Channel.
Bergh et al. (1) observed that viruses in seawater samples
appear to be free. They identified four different classes of viruses in
terms of their size and found that marine samples are dominated by the
smallest class (30 to 60 nm). Our FCM data suggest that at least two
virus populations (V-I and V-II) are ubiquitous in oceanic samples from
very different environments. A total of 20% of the V-I group, which
displays the highest SYBR-I fluorescence intensity, and 100% of the
V-II viruses could pass through 0.2-µm-pore-size filters (Fig. 4C),
suggesting that V-I viruses are larger. The V-I population displays the
same relative green fluorescence intensity after staining with SYBR-I
than do viruses affecting eukaryotic algal cells such as P. pouchetii (analyzed in the present study) or Micromonas
pusilla (data not shown). Furthermore, the V-II population is
4- to 10-fold more abundant than the V-I population, a ratio
commensurate with the heterotroph/phytoplankton ratio, which
ranged from 3 to 20 (n = 70) in natural samples
from the Mediterranean Sea. This suggests that V-I viruses could be
infectious to phytoplanktonic (in particular eukaryotic) cells while
V-II viruses could be related to the more numerous heterotrophic
bacteria. It is noteworthy that in the Mediterranean Sea depth profile
the V-I/V-II ratio peaked at the depth where phytoplanktonic cells were
most abundant (Fig. 6B). Although these hypotheses require much more
detailed work for confirmation, which is clearly beyond the scope of
this study, they underline that, in the future, FCM could be one of the
major techniques used for the analysis of viruses and will contribute
to the knowledge of the distribution and dynamic of viruses in oceanic environments.
 |
ACKNOWLEDGMENTS |
This work was supported by grants from the European Community
(MAST CT95-0016-MEDEA; MAS3-CT96-5033[DG12-ASAL], TMR program), from
JGOFS-France (EPOPE, MINOS, and PROSOPE programs), and by The Research
Council of Norway (project 121425/420). The FACSort flow cytometer was
funded in part by CNRS-INSU and the Région Bretagne.
The electron microscopic work was done at the Laboratory for Electron
Microscopy University of Bergen. We thank Sandrine Boulben for her
technical assistance and Jed Fuhrman for an early discussion on the
interest of detecting viruses by FCM.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Station
Biologique, Place Georges Tessier, BP 74, F-29680 Roscoff, France.
Phone: 33 (2) 98 29 23 14. Fax: 33 (2) 98 29 23 24. E-mail:
marie{at}sb-roscoff.fr.
 |
REFERENCES |
| 1.
|
Bergh, Ø.,
K. Y. Børsheim,
G. Bratbak, and M. Heldal.
1989.
High abundance of viruses found in aquatic environments.
Nature
340:467-468[Medline].
|
| 2.
|
Bratbak, G.,
M. Heldal,
S. Norland, and T. F. Thingstad.
1990.
Viruses as partners in spring bloom microbial trophodynamics.
Appl. Environ. Microbiol.
56:1400-1405[Abstract/Free Full Text].
|
| 3.
|
Bratbak, G., and M. Heldal.
1993.
Total count of viruses in aquatic environments, p. 135-138.
In
P. F. Kemp, B. F. Sherr, E. B. Sherr, and J. J. Cole (ed.), Current methods in aquatic microbial ecology. Lewis Publishers, London, England.
|
| 4.
|
Bratbak, G.,
J. K. Egge, and M. Heldal.
1993.
Viral mortality of the marine alga Emiliania huxleyi (Haptophyceae) and termination of algal blooms.
Mar. Ecol. Prog. Ser.
93:39-48.
|
| 5.
|
Børsheim, K. Y.,
G. Bradbak, and M. Heldal.
1990.
Enumeration and biomass estimation of planktonic bacteria and viruses by transmission electron microscopy.
Appl. Environ. Microbiol.
56:352-356[Abstract/Free Full Text].
|
| 6.
|
Børsheim, K. Y.
1993.
Native marine bacteriophages.
FEMS Microb. Ecol.
102:141-159.
|
| 7.
|
Cottrell, M. T., and C. A. Suttle.
1991.
Wide-spread occurrence and clonal variation in viruses which cause lysis of a cosmopolitan eukaryotic marine phytoplankter, Micromonas pusilla.
Mar. Ecol. Prog. Ser.
78:1-9.
|
| 8.
|
Cottrell, M. T., and C. A. Suttle.
1995.
Dynamics of a lytic virus infecting the photosynthetic marine picoflagellate Micromonas pusilla.
Limnol. Oceanogr.
40:730-739.
|
| 9.
|
Guillard, R. R. L.
1975.
Culture of phytoplankton for feeding marine invertebrates, p. 29-60.
In
W. L. Smith, and M. H. Chanley (ed.), Culture of marine invertebrate animals. Plenum Press, New York, N.Y.
|
| 10.
|
Gundersen, K.,
G. Bratbak, and M. Heldal.
1996.
Factors influencing the loss of bacteria in preserved seawater samples.
Mar. Ecol. Prog. Ser.
137:305-310.
|
| 11.
|
Hara, S.,
K. Terauchi, and I. Koike.
1991.
Abundance of viruses in marine waters: assessment by epifluorescence and transmission electron microscopy.
Appl. Environ. Microbiol.
57:2731-2734[Abstract/Free Full Text].
|
| 12.
|
Hennes, K. P., and C. A. Suttle.
1995.
Direct counts of viruses in natural waters and laboratory cultures by epifluorescence microscopy.
Limnol. Oceanogr.
40:1050-1055.
|
| 13.
|
Jacobsen, A.,
G. Bratbak, and M. Heldal.
1996.
Isolation and characterization of a virus infecting Phaeocystis pouchetii (Prymnesiophyceae).
J. Phycol.
32:923-927.
|
| 14.
|
Kriss, A. E., and E. A. Rukina.
1947.
Bacteriophages in the sea.
Dokl. Akad. Nauk SSSR
57:833-836.
|
| 15.
|
Li, W. K. W.,
J. F. Jellett, and P. M. Dickie.
1995.
DNA distribution in planktonic bacteria stained with TOTO and TO-PRO.
Limnol. Oceanogr.
40:1485-1495.
|
| 16.
|
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].
|
| 17.
|
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].
|
| 18.
|
Monger, B. C., and M. R. Landry.
1993.
Flow cytometric analysis of marine bacteria with Hoechst 33342.
Appl. Environ. Microbiol.
59:905-911[Abstract/Free Full Text].
|
| 19.
|
Noble, R. T., and J. A. Fuhrman.
1998.
Use of SYBR Green I for rapid epifluorescence counts of marine viruses and bacteria.
Aquat. Microb. Ecol.
14:113-118.
|
| 20.
|
Olson, R. J.,
D. Vaulot, and S. W. Chisholm.
1985.
Marine phytoplankton distributions measured using shipboard flow cytometry.
Deep-Sea Res.
32:1273-1280.
|
| 21.
|
Paul, J. H.,
S. C. Jiang, and J. B. Rose.
1991.
Concentration of viruses and dissolved DNA from aquatic environments by vortex flow filtration.
Appl. Environ. Microbiol.
57:2197-2204[Abstract/Free Full Text].
|
| 22.
|
Proctor, L. M., and J. A. Fuhrman.
1990.
Viral mortality of marine bacteria and cyanobacteria.
Nature (London)
343:60-62.
|
| 23.
|
Proctor, L. M., and J. A. Fuhrman.
1992.
Mortality of marine bacteria in response to enrichments of the virus size fraction from seawater.
Mar. Ecol. Prog. Ser.
87:283-293.
|
| 24.
|
Spencer, R.
1955.
A marine bacteriophage.
Nature (London)
175:690.
|
| 25.
|
Spencer, R.
1960.
Indigenous marine bacteriophages.
J. Bacteriol.
79:614[Free Full Text].
|
| 26.
|
Suttle, C. A.,
A. M. Chan, and M. T. Cottrell.
1990.
Infection of phytoplankton by viruses and reduction of primary productivity.
Nature
347:467-469.
|
| 27.
|
Suttle, C. A.,
A. M. Chan, and M. T. Cottrell.
1991.
Use of ultrafiltration to isolate viruses from seawater which are pathogens of marine phytoplankton.
Appl. Environ. Microbiol.
57:721-726[Abstract/Free Full Text].
|
| 28.
|
Suttle, C. A., and A. M. Chan.
1993.
Marine cyanophages infecting oceanic and coastal strains of Synechococcus: abundance, morphology, cross-infectivity and growth characteristics.
Mar. Ecol. Prog. Ser.
92:99-109.
|
| 29.
|
Suttle, C. A., and A. M. Chan.
1995.
Viruses infecting the marine Prymnesiophyte Chrysochromulina spp.: isolation, preliminary characterization and natural abundance.
Mar. Ecol. Prog. Ser.
118:275-282.
|
| 30.
|
Vaulot, D.
1989.
CYTOPC: processing software for flow cytometric data.
Signal Noise
2:8.
|
| 31.
|
Waterbury, J. B., and F. W. Valois.
1993.
Resistance to co-occurring phages enables marine Synechococcus communities to coexist with cyanophages abundant in seawater.
Appl. Environ. Microbiol.
59:3393-3399[Abstract/Free Full Text].
|
| 32.
|
Weinbauer, M. E., and C. A. Suttle.
1997.
Comparison of epifluorescence and transmission electron microscopy for counting viruses in natural marine waters.
Aquat. Microb. Ecol.
13:225-232.
|
| 33.
|
Wommack, K. E.,
R. T. Hill,
M. Kellel,
E. Russek-Cohen, and R. A. Colwell.
1992.
Distribution of viruses in the Chesapeake Bay.
Appl. Environ. Microbiol.
58:2965-2970[Abstract/Free Full Text].
|
Applied and Environmental Microbiology, January 1999, p. 45-52, Vol. 65, No. 1
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
This article has been cited by other articles:
-
Frada, M., Probert, I., Allen, M. J., Wilson, W. H., de Vargas, C.
(2008). From the Cover: The "Cheshire Cat" escape strategy of the coccolithophore Emiliania huxleyi in response to viral infection. Proc. Natl. Acad. Sci. USA
105: 15944-15949
[Abstract]
[Full Text]
-
Llewellyn, C. A., Tarran, G. A., Galliene, C. P., Cummings, D. G., De Menezes, A., Rees, A. P., Dixon, J. L., Widdicombe, C. E., Fileman, E. S., Wilson, W. H.
(2008). Microbial dynamics during the decline of a spring diatom bloom in the Northeast Atlantic. J PLANKTON RES
30: 261-273
[Abstract]
[Full Text]
-
Parada, V., Sintes, E., van Aken, H. M., Weinbauer, M. G., Herndl, G. J.
(2007). Viral Abundance, Decay, and Diversity in the Meso- and Bathypelagic Waters of the North Atlantic. Appl. Environ. Microbiol.
73: 4429-4438
[Abstract]
[Full Text]
-
Lohr, J., Munn, C. B., Wilson, W. H.
(2007). Characterization of a Latent Virus-Like Infection of Symbiotic Zooxanthellae. Appl. Environ. Microbiol.
73: 2976-2981
[Abstract]
[Full Text]
-
Pan, L. A., Zhang, J., Zhang, L. H.
(2007). Picophytoplankton, nanophytoplankton, heterotrohpic bacteria and viruses in the Changjiang Estuary and adjacent coastal waters. J PLANKTON RES
29: 187-197
[Abstract]
[Full Text]
-
Martinez-Martinez, J., Norland, S., Thingstad, T. F., Schroeder, D. C., Bratbak, G., Wilson, W. H., Larsen, A.
(2006). Variability in microbial population dynamics between similarly perturbed mesocosms. J PLANKTON RES
28: 783-791
[Abstract]
[Full Text]
-
Sandaa, R.-A., Larsen, A.
(2006). Seasonal Variations in Virus-Host Populations in Norwegian Coastal Waters: Focusing on the Cyanophage Community Infecting Marine Synechococcus spp.. Appl. Environ. Microbiol.
72: 4610-4618
[Abstract]
[Full Text]
-
Wen, K., Ortmann, A. C., Suttle, C. A.
(2004). Accurate Estimation of Viral Abundance by Epifluorescence Microscopy. Appl. Environ. Microbiol.
70: 3862-3867
[Abstract]
[Full Text]
-
Brussaard, C. P. D., Short, S. M., Frederickson, C. M., Suttle, C. A.
(2004). Isolation and Phylogenetic Analysis of Novel Viruses Infecting the Phytoplankton Phaeocystis globosa (Prymnesiophyceae). Appl. Environ. Microbiol.
70: 3700-3705
[Abstract]
[Full Text]
-
Brussaard, C. P. D.
(2004). Optimization of Procedures for Counting Viruses by Flow Cytometry. Appl. Environ. Microbiol.
70: 1506-1513
[Abstract]
[Full Text]
-
Schroeder, D. C., Oke, J., Hall, M., Malin, G., Wilson, W. H.
(2003). Virus Succession Observed during an Emiliania huxleyi Bloom. Appl. Environ. Microbiol.
69: 2484-2490
[Abstract]
[Full Text]
-
Yoch, D. C.
(2002). Dimethylsulfoniopropionate: Its Sources, Role in the Marine Food Web, and Biological Degradation to Dimethylsulfide. Appl. Environ. Microbiol.
68: 5804-5815
[Full Text]
-
Ley, V., Higgins, J., Fayer, R.
(2002). Bovine Enteroviruses as Indicators of Fecal Contamination. Appl. Environ. Microbiol.
68: 3455-3461
[Abstract]
[Full Text]
-
Danovaro, R., Dell'Anno, A., Trucco, A., Serresi, M., Vanucci, S.
(2001). Determination of Virus Abundance in Marine Sediments. Appl. Environ. Microbiol.
67: 1384-1387
[Abstract]
[Full Text]
-
Chen, F., Lu, J.-r., Binder, B. J., Liu, Y.-c., Hodson, R. E.
(2001). Application of Digital Image Analysis and Flow Cytometry To Enumerate Marine Viruses Stained with SYBR Gold. Appl. Environ. Microbiol.
67: 539-545
[Abstract]
[Full Text]
-
Bettarel, Y., Sime-Ngando, T., Amblard, C., Laveran, H.
(2000). A Comparison of Methods for Counting Viruses in Aquatic Systems. Appl. Environ. Microbiol.
66: 2283-2289
[Abstract]
[Full Text]
-
Wommack, K. E., Colwell, R. R.
(2000). Virioplankton: Viruses in Aquatic Ecosystems. Microbiol. Mol. Biol. Rev.
64: 69-114
[Abstract]
[Full Text]
-
Gasol, J. M., Zweifel, U. L., Peters, F., Fuhrman, J. A., Hagström, A.
(1999). Significance of Size and Nucleic Acid Content Heterogeneity as Measured by Flow Cytometry in Natural Planktonic Bacteria. Appl. Environ. Microbiol.
65: 4475-4483
[Abstract]
[Full Text]