Fluorescent in situ hybridization (FISH) using rRNA-specific
oligonucleotide probes has emerged as a popular technique
for identifying individual microbial cells. In natural samples,
however, the signal derived from fluor-labeled oligonucleotide probes
often is undetectable above background fluorescence in many cells.
To circumvent this difficulty, we applied fluorochrome-labeled
polyribonucleotide probes to identify and enumerate marine planktonic
archaea and bacteria. The approach greatly enhanced the sensitivity and
applicability of FISH with seawater samples, allowing confident
identification and enumeration of planktonic cells to ocean depths of
3,400 m. Quantitative whole-cell hybridization experiments using these probes accounted for 90 to 100% of the total
4',6-diamidino-2-phenylindole (DAPI)-stained cells in most samples. As
predicted in a previous study (R. Massana, A. E. Murray,
C. M. Preston, and E. F. DeLong, Appl. Environ. Microbiol.
63:50-56, 1997), group I and II marine archaea predominate in
different zones in the water column, with maximal cell densities of
105/ml. The high cell densities of archaea, extending from
surface waters to abyssal depths, suggest that they represent a large and significant fraction of the total picoplankton biomass in coastal
ocean waters. The data also show that the vast majority of planktonic
prokaryotes contain significant numbers of ribosomes, rendering them
easily detectable with polyribonucleotide probes. These results imply
that the majority of planktonic cells visualized by DAPI do not
represent lysed cells or "ghosts," as was suggested in a previous report.
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INTRODUCTION |
Fluorescent in situ hybridization
(FISH) probes that target intracellular rRNA (e.g., phylogenetic
stains; 10) have become widely used tools over the
past decade (for a review, see reference 4). The
approach has been successfully applied for phylogenetic identification
of individual microbial cells in a number of different environmental
contexts. Diverse applications of the technique continue to be
developed and include the identification and quantification of specific
cell types in plankton (1, 23, 27, 56), sediments (31,
48, 53), and soils (9); estimation of physiological activity via cellular rRNA content (23, 26, 39); and spatial localization of microorganisms along environmental gradients (42, 46) or in symbiotic associations (2, 7, 12-15, 38).
Detection methods have included epifluorescence microscopy, laser
scanning confocal microscopy (10, 54), and flow cytometry
(3, 47, 55). A promising recent modification of the
technique combines microautoradiography with rRNA-targeted FISH,
allowing the assignment of radiotracer uptake to specific phylogenetic
types (25, 36). Another advanced application includes
spatial correlation of population structure measured via FISH, with the
corresponding chemical environment assessed using microelectrodes
(42, 45, 46).
Despite the utility of the approach, difficulties are often encountered
when applying rRNA-targeted, fluorescent oligonucleotide probes and
FISH to complex environmental samples. Problems encountered include
variable probe binding to different rRNA target sites (16,
17), a highly autofluorescent sample or cell background, and the
inherently low ribosome content of many naturally occurring cells. In
aquatic samples, the proportion of cells visualized with monolabeled
oligonucleotide probes can be highly variable. Some successful
applications of rRNA-targeted oligonucleotide probes and FISH for
visualizing picoplankton and nanoplankton have been reported (1,
19-21, 23, 27, 28, 30, 56). In many aquatic samples, however,
the percentage of cells detected by oligonucleotide probes and FISH may
be significantly lower than the total prokaryotic cell count (1,
19, 21, 24, 26, 27, 33, 37, 56). Probe-conferred fluorescence of many naturally occurring cells often seems to be below current detection limits using monolabeled oligonucleotides and standard epifluorescence microscopy.
A number of signal amplification methodologies have been tested and
applied. Many of these are based on an enzymatic amplification step
that produces a precipitating fluorescent or colored product (5,
44, 57). Although improvements in signal strength can be
obtained, the penetration of enzyme complexes into prokaryote cells can
be inefficient. It is usually necessary to include a very carefully
controlled permeabilization step with enzymatic signal amplification
approaches, balancing permeabilization with cellular integrity. Since
cell wall composition varies greatly among prokaryotes, such procedures
may compromise the universal applicability of this approach. In another
approach, biotin-avidin systems have been applied to detect and
quantify marine protists using rRNA-targeted oligonucleotides and FISH
(28, 29). An alternative method to amplify a FISH signal
uses multiply labeled polyribonucleotide probes (6, 32).
This approach has been used to discriminate closely related
Pseudomonas species and uncultivated magnetotactic bacteria
(49, 52).
In this study, we modified polyribonucleotide probe protocols to
quantify two abundant groups of planktonic marine archaea and bacteria.
Our results extend previously reported strategies (6, 19, 32,
52) used to identify and enumerate single microbial cells with
FISH. Fluor-labeled polyribonucleotide probes were developed for
planktonic bacteria and two groups of planktonic archaea and tested for
sensitivity and specificity. Dual-staining capabilities were developed
and applied to identify and enumerate the different cell types in
the same microscopic field in seawater samples. We modified FISH
protocols by using multiply labeled polyribonucleotide probes for
application to marine plankton samples. The technique was then
successfully applied to identify and quantify archaeal and bacterial
cells in seawater to depths of 3,400 m.
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MATERIALS AND METHODS |
Cloning of archaeal small- and large-subunit rRNA operons and
genes.
Archaeal group I and II polyribonucleotide probes were
synthesized via PCR amplification from plasmid or fosmid templates. The
group I probe spanned the entire small-subunit rRNA and approximately 2,600 bases of the large-subunit rRNA. DNA templates for the generation of group I probes were fosmid clones with ca. 40-kb DNA inserts that
contained 16S and 23S rRNA linked in an operon (43, 50). The
following group I rRNA operon-containing fosmids were used for
polynucleotide probe preparation: clone 101G10 (cloned from Cenarchaeum symbiosum [41]), clone 4B7
(from a 200-m Oregon coast sample [50]), and clone
ANT2-74A4 (from an Antarctic marine planktonic fosmid library). The
preparation of two of the fosmid DNA clone libraries has been
previously described (41, 50). The third library was
prepared from picoplankton collected in coastal waters off Anvers
Island, Antarctica, by previously described methods (50).
Fosmid templates were prepared by using Qiagen Maxi kits (Qiagen,
Valencia, Calif.) and following the manufacturer's recommendations for
low-copy-number vectors.
Archaeal group II polyribonucleotide probes were prepared from clones
derived from PCR-amplified 16S and 23S rRNA genes recovered from this
group. The 23S and 16S rRNA gene clones were prepared separately.
(Available data suggest that 16S and 23S rRNA genes of group II archaea
are not linked in an operon, similar to Thermoplasma acidophilum [data not shown].) The group II 16S rRNA gene clones used for probe generation (SB95-74, SB95-75, and SB95-76) were isolated
in a previous study (34). Group II 23S rRNA genes were recovered from surface water plankton samples containing a large proportion of group II archaea. Amplifications were performed on a
Perkin-Elmer 9700 thermal cycler by using Taq Plus Precision (Stratagene, La Jolla, Calif.), following the manufacturer's
recommendations, and using primers LSU190F and LSU2445aR (Table
1). After an initial denaturation step of
3 min at 92°C, the thermal cycling parameters were denaturation at
92°C for 30 s, annealing at 56°C for 30 s, and extension
at 72°C for 1 min for a total of 35 cycles. The resulting PCR
products were purified by phenol-chloroform extraction (1:1) and spin
dialysis in Centricon 100 units (Amicon, Beverly, Mass.). Purified
amplicons were subsequently treated with cloned Pfu
polymerase (Stratagene) at 72°C for 15 min in 1× cloned
Pfu PCR buffer (Stratagene) by following the manufacturer's
recommendations. Amplicons were then cloned into the pCRBlunt vector
(Invitrogen, Carlsbad, Calif.) by following the manufacturer's
recommendations. 23S rRNA clones were bidirectionally sequenced by
using infrared dye-labeled primers and a Licor automated DNA sequencer.
Sequences were aligned within a database of 23S rRNA sequences by using ARB (51). Subsequent bootstrap distance analyses were
performed by using PAUP, version 4.0.0d55, Unix version, in conjunction with the GCG package (Genetics Computer Group, Inc., Madison, Wis.).
The logdet distance correction was used for evolutionary distance
estimation with a transition/transversion ratio of 2.0 empirical base
frequencies, random taxon addition, and 1,000 bootstraps of the data
set to assign confidence to branches.
Preparation of DNA templates for transcription reactions.
DNA templates used for transcription reactions were prepared by PCR
amplification with the Taq Plus Precision enzyme mixture (Stratagene)
by following the manufacturer's recommendations. The templates and
primers used to generate T7 promoter-containing amplicons for use in
subsequent transcription reactions are shown in Tables 1 and
2. After an initial denaturation step of
3 min at 94°C, the thermal cycling parameters were denaturation at
92°C for 30 s and annealing at 56°C for 30 s. An
extension time of 3 min at 72°C was used to generate eubacterial,
group I, and negative control probe templates. An extension time of 1 min at 72°C was used to generate group II probe templates (23S or 16S
rRNAs; Table 2). A total of 30 PCR cycles were used to generate all of
the T7 promoter-containing amplicons. The resulting amplicons, each containing a T7 promoter region, were purified by phenol-chloroform extraction (1:1) and subsequent spin dialysis in Centricon 100 units
(Amicon).
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TABLE 2.
Primers and templates used to generate amplicons for
transcription reactions and optimized hybridization conditions
for FISH
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Generation of fluorescently labeled polyribonucleotide
probes.
Polyribonucleotide probes were generated from PCR
amplicons that contained a T7 RNA polymerase promoter at the 5'
end. The oligonucleotide primer sequences, primer pairs, and DNA
templates used in PCR amplifications are shown in Tables 1 and 2.
Polyribonucleotide probes were synthesized by using a protocol modified
from that of Chee et al. (8). Transcription reactions were
performed with Ampliscribe T7 RNA polymerase (Epicentre, Madison, Wis.) by using a modification of the manufacturer's suggested protocol. Diethyl pyrocarbonate (DEPC)-treated water and precautions for eliminating potential RNase contamination were used throughout the
procedure. To generate fluorescein-containing transcripts, transcription reaction mixtures (100-µl total volume) contained 0.5 mM ATP, 0.5 mM GTP, 0.25 mM UTP, 0.25 mM CTP, 0.14 mM
fluorescein-12-CTP (NEN, Boston, Mass.), 0.14 mM fluorescein-12-UTP
(Boehringer), 10 mM dithiothreitol, 1× Ampliscribe Reaction
Buffer, 10 µl of Ampliscribe T7 RNA polymerase enzyme solution, and
approximately 2.5 µg of T7 promoter-containing amplicon (DNA
template; see above). Following transcription reactions, the
fluorescent RNA products were purified by spin dialysis in DEPG-treated
H2O and adjusted to a volume of 100 to 200 µl. For
hydrolysis of transcripts, MgCl2 was added to a final
concentration of 30 mM and the reaction mixtures were heated at 90°C
for 5 min. After a 5-min hydrolysis time, the samples were placed on
ice and the average size of fragmented transcripts was estimated by
agarose gel electrophoresis in comparison to known standards. When
necessary, the hydrolysis was resumed for an additional 2 to 5 min at
90°C to attain average fragment sizes of
100 nucleotides. Reaction
mixtures were subsequently reassayed by agarose gel electrophoresis.
Reactions were terminated by addition of 50 mM Na2EDTA. The
hydrolysis reactions were monitored by agarose gel electrophoresis in
0.5× Tris-borate-EDTA in 2.5% (wt/vol) Nusieve 3:1 (FMC Bioproducts,
Rockland, Maine) gels. An RNA marker (Sigma, St. Louis, Mo.) was
included to estimate the sizes of the hydrolysis products. Following
electrophoresis, gels were examined for fluorescent products by using a
flat-bed fluorescence scanner (FluorImager; Molecular Dynamics,
Sunnyvale, Calif.). Gels were subsequently stained with Sybr Green 2 (FMC Bioproducts) and visualized by fluorescence scanning, and the average RNA hydrolysate size was estimated by comparison to RNA size standards.
For labeling of transcripts with the cyanine dye CY-3, transcription
reactions (120-µl total volume) contained 4.2 mM ATP, 6.3 mM GTP, 6.3 mM UTP, 6.3 mM CTP, 2.1 mM N6-(6-aminohexyl)ATP (Gibco
Bethesda Research Laboratories, Gaithersburg, Md.), 10 mM
dithiothreitol, 1× Ampliscribe Reaction Buffer, 12 µl of Ampliscribe
T7 RNA polymerase enzyme solution, and 2 to 5 µg of T7
promoter-containing amplicon (see above). Following the transcription
reaction, the reaction mixture was purified by gel filtration on Micro
BioSpin columns (Bio-Rad, Hercules, Calif.) equilibrated with
DEPC-treated H2O and the purified transcripts were mixed
1:1 (vol/vol) with 250 mM sodium carbonate buffer, pH 9.2. The sample
was next mixed with dried reactive CY-3 monofunctional dye (Fluorolink;
Amersham, Chicago, Ill.) by following the manufacturer's recommendations, and reaction mixtures were incubated for 1 h at
room temperature. Labeled transcripts were separated from unbound dye
by gel filtration on Micro BioSpin columns (Bio-Rad) equilibrated with
DEPC-treated H2O. Labeled transcripts were hydrolyzed as described above for the fluorescein-labeled transcripts. Unlabeled RNA,
used as a competitor probe in some experiments, was synthesized by
using the Ampliscribe kit (Epicentre) and following the manufacturer's recommendations.
Sample collection, processing, and storage.
Following
initial tests with cells of C. symbiosum, experiments were
performed on formalin-fixed seawater samples collected on polycarbonate
filters. For whole-cell hybridization with seawater samples, we
modified the protocol of Glöckner et al. (19) by adjusting the hybridization conditions for polynucleotide probes. Seawater samples were collected with a rosette sampler at a series of
offshore stations near Moss Landing, Calif. The sites sampled, total
bottom depth, and miles offshore were, respectively, as follows: C1,
250 m, 2.6 miles; M1, 1,097 m, 10.8 miles; M2, 1,645 m, 26.5 miles; 67-90, 4,424 m, 177 miles. Seawater samples were fixed in 3.7%
(wt/vol) formalin overnight at 4°C. A total of 3 to 10 ml of seawater
(depending on the depth of origin) was filtered onto a 25-mm-diameter,
0.2-µm-pore-size polycarbonate GTTP filter (Millipore, Bedford,
Mass.) under a vacuum of <5 mm Hg. The vacuum was released, and 1 ml
of 2% (wt/vol) NaCl-50% (vol/vol) ethanol was placed on the filter.
After a 1-min incubation, the ethanol solution was filtered through
completely and the filters were dried. Filters were stored in petri
slides (Millipore) at
20°C. This storage method was tested for
periods of as long as 1 year with no apparent hybridization signal loss.
FISH.
Fluorescent hybridizations were performed in the
inverted lids of 12-well polystyrene culture dishes. Filters were
quartered with a razor blade, and the sections were placed face up on
the inverted lid of a culture dish. Approximately 20 µl of preheated hybridization solution was placed on each filter, and 100 ng of hydrolyzed, fluor-labeled polynucleotide probe was subsequently added.
The hybridization solution contained 50 to 70% (vol/vol) formamide (depending on the experiment; see below), 10% (wt/vol) dextran sulfate, 0.01% (wt/vol) poly(A), and 5× SET (1× SET is 150 mM NaCl, 1 mM Na2EDTA, 20 mM Tris-HCl, pH 7.8). A
round 18-mm-diameter coverslip was placed over the filter, and the
culture wells were placed over the lid to seal the individual
hybridization mixtures. The whole assembly was then placed in a sealed
container containing a small beaker with 5 ml of 5× SET to maintain
humidity. Hybridization mixtures were incubated overnight in a
hybridization oven (Robbins Scientific, Sunnyvale, Calif.) at the
temperatures specified below. After overnight incubation, the filters
were removed and placed in 5 ml of a wash solution containing 0.2× SET
and 50% (vol/vol) formamide. The filters were washed for 2 h at
the appropriate temperature (depending on the experiment; see below).
The filters were subsequently incubated in 1× PBS (145 mM NaCl,
8.7 mM Na2HPO4, 1.5 mM
NaH2PO4, pH 7.4) containing DAPI
(4',6-diamidino-2-phenylindole) at 1 µg/ml for 2 min at room
temperature and quickly rinsed in 1× PBS. Filters were placed on
slides and covered with approximately 10 µl of Citifluor solution
(Citifluor, London, United Kingdom), and a coverslip.
A variety of conditions were tested to optimize the signal strength and
specificity of each probe. The main variables tested were formamide
concentration in the hybridization buffer, hybridization temperature,
and wash temperature. Subsequent to these tests, the standard
conditions for hybridization formamide concentration, hybridization
temperature, and wash temperature indicated in Table 2 were employed.
Following hybridizations, the standard wash buffer used for all of the
probes consisted of 0.2× SET and 50% (vol/vol) formamide.
Filters were viewed immediately but could be used for several days
after mounting when stored in the dark at 4°C. Filters were viewed
with an Axiophot 2 microscope equipped with an HBO 100-W mercury lamp
and a 100× Plan-APO objective (Zeiss, Thornwood, N.Y.). The following
filter sets were used for fluorescence microscopy: fluorescein, a
D480/30 exciter filter, a 505DCLP beam splitter, and a D535/40 barrier
filter (Chroma Technology Corp., Brattleboro, Vt.); CY-3, an HQ545/30
exciter filter, a Q565LP beam splitter, and an HQ610/75 barrier
filter (Chroma Technology Corp.); DAPI, a D360/40 exciter filter, a
400DCLP beam splitter, and a GG420 barrier filter (Chroma Technology
Corp.). Images were captured with a Spot SP100 cooled digital color
charge-coupled device camera (Diagnostic Instruments, Inc., Sterling
Heights, Mich.).
Total prokaryotic cell densities were estimated by DAPI staining and
direct epifluorescence microscopic counting (22). To quantify probe-positive cells, five fields of approximately 50 to 150 cells per field were counted for each probe in each sample. A negative
control probe (the complement of either the archaeal probe or the
bacterial probe) was included for every sample and used to calculate
the final probe-positive cell concentration. The fraction of
probe-positive cells was calculated as the ratio of the number of
probe-positive cells (archaeal group I, archaeal group II, or bacteria)
to the total number of DAPI-stained cells after background subtraction
of the control probe counts for each probe treatment. The cell
densities of group I archaea, group II archaea, and bacteria were
calculated by multiplying the fraction of probe-positive cells by the
total prokaryotic cell concentration estimated from direct
epifluorescence microscopic counts.
Quantitative rRNA blotting experiments.
Collection of
picoplankton samples, nucleic acid extractions, and quantitative slot
blotting experiments were performed as previously described (34,
35). The relative abundance of eucaryal, bacterial, and archaeal
rRNAs in nucleic acid extracts was estimated by using oligonucleotide
probe hybridization as previously described (34, 35).
Nucleic acids were immobilized on nylon membranes (Hybond-N; Amersham)
and then hybridized with 32P-labeled, rRNA-targeted
oligonucleotide probes. The binding of each group-specific probe was
quantified relative to that of a universal probe and normalized to the
relative response of each probe to known standards.
Nucleotide sequence accession numbers.
The sequences
obtained in this study have been submitted to the GenBank database and
assigned accession no. AF198456 and AF198457.
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RESULTS |
Cloning and characterization of rRNA genes and operons.
The
archaeal 23S rRNA genes amplified from surface seawater were not
related to group I archaeal 23S rRNA genes, consistent with previous
observations of low group I archaeal abundance in surface waters
(34). The archaeal 23S rRNA gene fragment on clone 1A10 was
most closely affiliated with the Euryarchaota and specifically related to T. acidophilum (Fig.
1). This phylogenetic placement is nearly
identical to that of group II archaeal 16S rRNA genes (11,
34), including the specific affiliation with T. acidophilum. To verify that the 23S rRNA gene contained on clone
1A10 was derived from a group II archaeon, we performed dual-hybridization experiments with a fluorescein-labeled group II 16S
rRNA probe and a CY-3-labeled group II 23S rRNA probe (derived from
clone 1A10; Table 2). The results showed that the same population of
cells that bound the group II 16S probe also bound the 1A10-derived, 23S rRNA-targeted probe (Fig. 2). In
combination, the ecological, phylogenetic, and FISH data provided
strong evidence that the 23S rRNA gene contained on clone 1A10 was
indeed derived from group II planktonic archaea. Consequently, we used
23S rRNA clone 1A10 to generate group II rRNA probes in subsequent
experiments.

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FIG. 1.
Phylogenetic position of the planktonic euryarchaeal 23S
rRNA gene contained on clone G2lsu-1A10. The number at each bifurcation
represents the percentage of 1,000 bootstrap resamplings that yielded
the branching pattern appearing to the right of the value. The scale
bar represents the estimated number of fixed mutations per nucleotide
position.
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FIG. 2.
Surface seawater sample from Monterey Bay hybridized
with a fluorescein-labeled 23S group II archaeal probe and a
CY-3-labeled 16S group II archaeal probe (Table 2). Images of the same
field were captured by using the fluorescein filter set (A), the CY-3
filter set (B), and the DAPI filter set (C). Bars, 5 µm.
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Synthesis of rRNA-targeted, fluorescent polyribonucleotide
probes.
The large evolutionary distance separating group I and
group II archaea from other archaeal and bacterial groups
facilitated the application of polyribonucleotide probes for their
identification. Plots of the unrestricted sequence similarity of
templates used to generate the archaeal probes versus homologues from
other archaeal and bacterial groups are shown in Fig.
3. The 23S and 16S rRNA genes of the
group I archaeon C. symbiosum are highly similar to those of
group 1 marine planktonic archaea,
90% over most 100-nucleotide
segments (Fig. 3A). The similarity of C. symbiosum to other
archaea and bacteria is much lower, on average,
75% over most
regions of the 23S and 16S rRNAs. The large evolutionary distance
separating group II archaea from other known archaea and bacteria is
evident in Fig. 3B. The group II 16S rRNAs are
75% similar to those
of other archaea and bacteria over most of the molecule. Group II 23S
rRNAs are
70% similar, over most of the molecule, to other known and
cultivated and uncultivated microorganisms.

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FIG. 3.
Similarity plots comparing rRNA sequences of templates
used to generate probes to homologous regions in other bacteria or
archaea. Each data point represents the unrestricted sequence
similarity value along a 100-nucleotide stretch. Nonoverlapping
similarity values were calculated in 100-nucleotide sequence segments
along the length of the 16S and 23S genes. (A) Group I archaea
(C. symbiosum) rRNA compared to homologous regions of other
bacteria and archaea. (B) Group II 16S (SB95-72) and 23S (G2lsu-1A10)
rRNAs compared to homologous regions of other bacteria and archaea. The
respective accession numbers of the small-subunit (SSU) and
large-subunit (LSU) rRNA sequences used are as follows: 4B7, U39635 and
AF198456; 101G10, AF083071 and AF083071; Escherichia coli,
U00006 and U00006; Sulfolobus solfataricus, X03235 and
U32322; Archaeoglobus fulgidus, X05567 and M64487; T. acidophilum, M38637 and M32298.
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Transcription reactions incorporating fluorescein-12-CTP and
fluorescein-12-UTP yielded the expected full-length products, in yields
ranging from 5 to 10 µg of RNA per 100-µl transcription reaction
mixture. Since the fluor-labeled RNA transcripts were greater than 1 kb
in size, a hydrolysis step was employed to fragment them to an average
size of
100 nucleotides. The hydrolysis step facilitated probe
penetration into fixed cells and may also improve the uniformity and
specificity of hybridization (8). Fragmentation of large
transcripts to an average size of around 100 nucleotides has been
reported to be essential for strong hybridization signals using FISH
(6). In addition, 23S rRNA-targeted probes of >200 nucleotides used for FISH may incompletely penetrate cells, as indicated by a halo of fluorescence surrounding the periphery of cells
hybridized with these large RNA probes (52).
Time series for transcript hydrolysis were performed to optimize
conditions for generation of probe fragments with an average size of
100 nucleotides. It was important to monitor the reactions after a
5-min hydrolysis time to carefully control the average fragment size.
When necessary, hydrolysis was resumed for an additional 2 to 5 min at 90°C. For 4.2-kb transcripts, 10 min of hydrolysis at 90°C
was sufficient for the generation of fragments of
100 nucleotides. To
fragment shorter full-length RNA transcripts, it was necessary to
reduce the total hydrolysis time to between 5 and 7.5 min. By using
this approach, it was possible to reproducibly generate fluor-labeled
polyribonucleotide probes of approximately 100 nucleotides for use in
FISH experiments. Small variations in the average size of the
hydrolyzed transcripts did not noticeably affect their hybridization
properties or the FISH signal.
Optimization of hybridization conditions for polyribonucleotide
probes.
Initial experiments to determine optimal hybridization
conditions for specificity and sensitivity were performed with
fluorescein-labeled, group I-targeted polyribonucleotide probes.
Formalin-fixed, macerated tissues from the marine sponge Axinella
mexicana that contained large numbers of the archaeon C. symbiosum (40, 41) were used to initially assess
hybridization conditions. The variables examined included formamide
concentration in the hybridization buffer, hybridization temperature,
and wash temperature. Comparison of the polynucleotide probe
results to results obtained with 16S rRNA-targeted
oligonucleotide probes verified the specificity of these probes for
their intended targets (40). The group I probes clearly
discriminated archaeal symbionts from contaminating bacteria in the
sponge tissue and, at high stringencies, did not cross-react with
formalin-fixed preparations of cultivated bacteria or archaea (data not
shown; 40). The fluorescence intensity obtained with
polyribonucleotide probes was much greater than that observed with
singly labeled oligonucleotide probes. We estimate at least a 10- to
50-fold increase in sensitivity with the multiply labeled probes
compared to that obtained with single-fluorochrome-labeled oligonucleotides (data not shown).
The group I probe bound a morphologically homogeneous population of
cells in seawater samples. We could not detect the archaeal cells in
the same seawater samples by using singly fluorescein-labeled or
CY-3-labeled oligonucleotides and standard epifluorescence microscopy
(data not shown). The group I archaeal shape and staining pattern (Fig.
4) were nearly identical to those of
cells previously observed in Antarctic picoplankton
(35) and C. symbiosum (41) visualized
by using multiple oligonucleotide probes. The group I probe-binding
cells displayed strong fluorescence at both poles, as well as an
unstained central region, giving them a peanut-like shape (Fig. 4A, B,
and H). The central portion, devoid of bound probe, corresponded to the
DAPI-staining nucleoid region within these cells (41). Dual
hybridization experiments demonstrated that group I archaeal, group II
archaeal, and bacterial polynucleotide probes did not cross-react with
the same cell population (Fig. 4H). CY-3-labeled and
fluorescein-labeled group I polynucleotide probes applied to the same
sample bound to a morphologically identical cell population and yielded
identical group I cell densities (data not shown). We routinely used
fluorescein-labeled negative control probes that comprised the reverse
complement of the group I archaea or bacterial probes (Table 2).
Background counts with these negative control probes were consistently
low, typically representing <1% of the total epifluorescence direct
counts.

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FIG. 4.
Epifluorescence micrographs of picoplankton
visualized with polynucleotide probes and FISH on polycarbonate
filters. (A and B) Seawater sample, collected from a 200-m
depth at a nearshore station in Monterey Bay, hybridized with the
CY-3-labeled group I probe and viewed by using the CY-3 (A) or the DAPI
(B) filter set. (C and D) Surface seawater sample, from a
nearshore station in Monterey Bay, hybridized with the
fluorescein-labeled 23S rRNA group II probe and viewed with the
fluorescein (C) or the DAPI (D) filter set. (E to G) A 100-m sample,
from an offshore station in Monterey Bay, dually hybridized with the
fluorescein-labeled 23S group II probe and the CY-3-labeled group I
probe. The sample was viewed with the fluorescein (E), DAPI (F), and
CY-3 (G) filter sets. (H) Seawater sampled at an 80-m depth at 177 miles offshore of Moss Landing, Calif. The sample was dually hybridized
with the fluorescein-labeled bacterial probe and the CY-3-labeled group
I probe. Images were captured independently by using the fluorescein or
CY-3 filter set, and the separate images were overlaid in Adobe
PhotoShop. Scale bars, 5 µm.
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Cells that bound the group II probe had a different morphology than
group I cells, generally a coccoid shape that uniformly stained with the polynucleotide probe throughout the entire cell (Fig.
4C and D). Dual hybridization with a fluorescein-labeled group II 23S
probe and a CY-3-labeled group I probe showed two discrete cell
populations with no cross-hybridization between them (Fig. 4E, F, and
G). The group II cells had a characteristic DAPI staining compared to
other cell types, with the DAPI-staining region appearing more diffuse
and weakly stained than in group I archaea or bacteria. This phenomenon
may be an artifact of the fixation or hybridization treatment but
might also reflect specific characteristics of group II archaeal
cell walls or cytoplasm. There was generally no cross-reaction
between the group I, group II, and eubacterial probes
each
recognized a discrete and unique cell population (Fig. 4E to H). In
rare cases, a weak cross-reaction between eubacteria and the group II
probe was observed. This cross-reactivity could be eliminated by the
inclusion of unlabeled bacterial polyribonucleotide probe in the
fluorescein-labeled group II probe hybridization mixtures (data not shown).
Estimation of group I and II archaeal cell densities in ocean
waters.
The FISH assays were highly reproducible. The mean and
standard error for replicate experiments, performed at a variety of depths at station M2, are shown in Fig.
5. We also checked reproducibility by
routinely performing dual hybridizations with a CY-3-labeled group I
probe, included in the fluorescein-labeled group II hybridizations. Dual hybridizations using the CY-3-labeled group I archaeal probe consistently yielded group I cell densities that were identical to
those obtained with hybridizations using the fluorescein-labeled group I probe alone. To independently assess the reliability of the FISH method, cell densities of group I and II archaea determined by
FISH were compared with the relative rRNA abundance derived from
radiolabeled oligonucleotide probe hybridization experiments (Fig.
6). In general, the FISH results and the
estimates of relative rRNA abundance were in good agreement. As a
further indicator of reliability, the sum of archaeal group I, group
II, and bacterial cells determined by FISH generally accounted for the
majority of the DAPI-stained cells in seawater samples (Table
3). In most samples, 90% or more of the
total DAPI-staining cells were accounted for by the combined total
derived from the three probes (Table 3).

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|
FIG. 5.
Group I archaea and bacterial cell concentrations at
various depths, determined by polyribonucleotide probe hybridization
and FISH and performed in triplicate. Error bars represent standard
errors, and where not visible, they are smaller than the symbols.
Methods are described in the text.
|
|

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FIG. 6.
Cell densities of group I and II archaea determined by
polyribonucleotide probe hybridization (Hyb) and FISH, compared to the
percentage of rRNA from each group in the same sample estimated by
quantitative oligonucleotide probe hybridization. Methods are described
in the text.
|
|
Group I archaeal cell numbers were generally lower in surface waters
and increased with depth as total prokaryotic cell numbers decreased.
At greater depths, group I archaeal cell densities were quite high,
approximately 105/ml (Fig. 5 and 6 and Table 3). In most
samples, group I archaea in Monterey Bay reached maximal cell densities
at depths of
60 m (Fig. 5 and 6), a distribution strikingly similar
to that observed in previous studies of rRNA abundances in the Santa
Barbara Channel (34). Also in agreement with previous
studies of rRNA relative abundance, group II archaeal cell numbers
exceeded those of group I archaea at depths of less than 40 m
(Fig. 6; Table 3). The polynucleotide probes could be used successfully
even at great depths (Fig. 7; Table 3).
Group I archaeal abundances were continuously high below 80 m, and
these archaea made up a substantial fraction of the total cell
population at 3,400 m. Group I and II archaeal cells were generally
smaller and dimmer at great depths than those found at the depth with
the cell density maximum (data not shown).

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FIG. 7.
Densities of group I archaea and bacterial cells at
various depths, determined by polyribonucleotide probe hybridization
and FISH. The sampling site was 177 miles offshore of Moss Landing,
Calif. Methods are described in the text. Eubac, eubacterial.
|
|
 |
DISCUSSION |
In this study, we modified and extended the use of multiply
labeled polyribonucleotide probes to identify and enumerate
uncultivated planktonic archaeal groups. After optimization of probe
synthesis and hybridization, the technique proved much more sensitive
than FISH using single oligonucleotides, consistent with previous
findings. The inclusion of a hydrolysis step after probe syntheses
resulted in efficient probe penetration into bacterial and archaeal
cells. Dual-staining approaches using probes labeled with different
fluorochromes allowed simultaneous identification of different target
groups and provided better assessment of the binding specificity of
each probe. Negative control probes consistently yielded few or no fluorescently labeled cells, further indicating the high
signal-to-noise ratio obtained with the approach. As previously
reported for oligonucleotides and FISH (19), hybridization
on polycarbonate filters was efficient and this approach facilitated
rapid processing and quantitative analysis of multiple aquatic samples.
In seawater samples, target archaeal groups that could not be reliably
visualized or quantified with oligonucleotide probes were easily and
routinely visualized and quantified with the polyribonucleotide probes.
The approach described here differs from those used in previous studies
in several respects. Unlike in previous studies (49, 52), we
used large rRNA sequence tracts to generate specific probes. This was
possible because the groups to be distinguished (group I archaea, group
II archaea, and bacteria) are so evolutionarily distant from one
another. Polyribonucleotide probes with greater specificity could
easily be generated by targeting more variable regions, particularly in
23S rRNA (49, 52). Unlike some previous studies, ours also
used a hydrolytic step to generate shorter probe fragments from long
transcripts. When using this protocol, it is important to carefully
control the hydrolysis of the probe after initial synthesis. If the
probes are hydrolyzed for too long, they could be reduced to the size
of short oligonucleotides, altering their binding specificity or
rendering them incapable of binding under the stringency conditions used.
We are currently applying these polynucleotide probes in ecological
studies of marine archaeal and bacterial spatial and temporal variability. These data provide a much higher degree of reliability and
resolution than is possible by using quantitative rRNA blots, fluorescent oligonucleotides and FISH, or PCR experiments. Preliminary results suggest that high archaeal cell densities are a common feature
of the world's oceans. If this is true, then archaea appear to
represent a very large and significant fraction of the picoplankton biomass in the world's oceans.
Polynucleotide probes targeting planktonic bacteria consistently
yielded a high signal intensity for a wide variety of morphotypes that
accounted for the majority of cells enumerated by epifluorescence direct counts in seawater. Significantly, the bacterial and archaeal probe-positive cells accounted for a majority percentage (>90%) of
the total cells enumerated by DAPI staining. Even in deep seawater samples, most of the DAPI-stained cells appear to contain significant amounts of rRNA readily detectable by the polyribonucleotide probe and
FISH protocol reported here. These results suggest that the majority of
the marine picoplankton visualized by DAPI staining does not represent
lysed cells or ghosts devoid of nucleic acids, as was suggested in a
previous report (58). Our results strongly suggest that the
majority of marine picoplankton cells visualized by epifluorescence
direct counts are intact and ribosome replete and so represent viable
and, quite possibly, physiologically active cells.
This work was supported by a grant to MBARI from the David and
Lucille Packard Foundation and NSF grant OCE95-29804 to E.F.D.
We thank Oded Beja, Marcelino Suzuki, Victoria Orphan, Grieg Steward,
and Christa Schleper for advice, suggestions, and encouragement. We
also thank the officers and crew of the Point Sur and
Point Lobos for able assistance.
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