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Applied and Environmental Microbiology logoLink to Applied and Environmental Microbiology
. 2002 Jun;68(6):3094–3101. doi: 10.1128/AEM.68.6.3094-3101.2002

Fluorescence In Situ Hybridization and Catalyzed Reporter Deposition for the Identification of Marine Bacteria

Annelie Pernthaler 1, Jakob Pernthaler 1,*, Rudolf Amann 1
PMCID: PMC123953  PMID: 12039771

Abstract

Fluorescence in situ hybridization (FISH) with horseradish peroxidase (HRP)-labeled oligonucleotide probes and tyramide signal amplification, also known as catalyzed reporter deposition (CARD), is currently not generally applicable to heterotrophic bacteria in marine samples. Penetration of the HRP molecule into bacterial cells requires permeabilization procedures that cause high and most probably species-selective cell loss. Here we present an improved protocol for CARD-FISH of marine planktonic and benthic microbial assemblages. After concentration of samples onto membrane filters and subsequent embedding of filters in low-gelling-point agarose, no decrease in bacterial cell numbers was observed during 90 min of lysozyme incubation (10 mg ml−1 at 37°C). The detection rates of coastal North Sea bacterioplankton by CARD-FISH with a general bacterial probe (EUB338-HRP) were significantly higher (mean, 94% of total cell counts; range, 85 to 100%) than that with a monolabeled probe (EUB338-mono; mean, 48%; range, 19 to 66%). Virtually no unspecific staining was observed after CARD-FISH with an antisense EUB338-HRP. Members of the marine SAR86 clade were undetectable by FISH with a monolabeled probe; however, a substantial population was visualized by CARD-FISH (mean, 7%; range, 3 to 13%). Detection rates of EUB338-HRP in Wadden Sea sediments (mean, 81%; range, 53 to 100%) were almost twice as high as the detection rates of EUB338-mono (mean, 44%; range, 25 to 71%). The enhanced fluorescence intensities and signal-to-background ratios make CARD-FISH superior to FISH with directly labeled oligonucleotides for the staining of bacteria with low rRNA content in the marine environment.


Fluorescence in situ hybridization (FISH) of bacteria was first described more than a decade ago (2, 11) and was hailed as a breakthrough for microbial ecology. However, researchers initially encountered difficulties in applying the method to environmental samples other than from highly eutrophic systems. Most bacteria in aquatic habitats are small, slow growing, or starving (31), and the signal intensities of hybridized bacterioplankton cells were frequently below the detection limits or lost in high background fluorescence. During the last few years numerous efforts have been made to increase the sensitivity of FISH, including the use of brighter fluorochromes (1, 19), image-intensified video microscopy (17), chloramphenicol treatment to increase the rRNA content of the growing bacterial fraction (35), hybridization with more than one fluorescently labeled oligonucleotide probe (27, 29), helper oligonucleotide probes (15, 21), multiply labeled polyribonucleotide probes (10, 25, 36), and signal amplification with reporter enzymes (27, 40).

The tyramide signal amplification (TSA), also known as catalyzed reporter deposition (CARD) was introduced more than a decade ago (5) for immunoblotting and immunosorbent assays using horseradish peroxidase (HRP) and haptenized tyramines. CARD is based on the deposition of a large number of labeled tyramine molecules by peroxidase activity. Tyramines are phenolic compounds, and HRP can catalyze dimerization of such compounds when they are present in high concentrations, probably by the generation of free radicals (49). If applied at lower concentrations, such as in the signal amplification reaction, the probability of dimerization is reduced, whereas the binding of the highly reactive intermediates to electron-rich moieties of proteins, such as tyrosine, at or near the site of the peroxidase binding site is favored. In this way, if fluorochrome-labeled tyramides are used, numerous fluorescent molecules can be introduced at the hybridization site in situ. This results in greatly enhanced FISH sensitivity compared to probes with a single fluorochrome. CARD in combination with nucleotide probes and/or antibodies is routinely used in histology and cytochemistry to localize specific nucleic acid sequences (DNA and RNA) in microscopic preparations of tissues, cells, and chromosomes and allows the detection of rare and even single-copy-number targets (mRNAs and genes) (6). To date, a wide variety of research and diagnostic applications have been described, making this technique an integral part of studies of gene mapping, gene expression, RNA processing and transport, the three-dimensional organization of the nucleus, tumor genetics, microbial infections, and prenatal diagnosis (43).

Unfortunately, this signal amplification technique is currently not applicable to heterotrophic bacteria in environmental samples (40). The critical step of this approach is the diffusion of large molecules such as enzymes, antibodies, or (strept)avidin into whole fixed cells (4). It is usually necessary to include a very carefully controlled permeabilization step prior to enzymatic signal amplification, balancing permeability with cellular integrity (41). Since cell wall composition varies greatly among prokaryotes, such procedures usually compromise the universal applicability of this approach in mixed microbial communities (40).

In this study, we modified preparation and permeabilization procedures, as well as staining protocols for FISH with HRP-labeled oligonucleotide probes and CARD, for the quantification of planktonic and benthic marine bacteria. This led to a significant improvement in detection rates compared to our current protocol for FISH with monolabeled probes (37).

MATERIALS AND METHODS

Sample collection and preparation.

Bacterioplankton samples originated from a cruise on the RV Uthörn between 1 and 3 October 1999. On three consecutive days, samples were collected from horizontal transects between the island of Helgoland and the estuaries of the rivers Elbe and Eider, respectively (days 1 and 2) and from Helgoland into open North Sea waters (day 3) (Fig. 1). Samples were fixed for 1 h in particle-free formaldehyde solution (final concentration, 2% [vol/vol]) and were prefiltered through cellulose nitrate membrane filters (pore size, 3 μm; Sartorius, Göttingen, Germany). For FISH, 10-ml portions were filtered onto white polycarbonate membrane filters (type GTTP; pore size, 0.2 μm; size, 47 mm; Millipore, Eschborn, Germany), washed with 5 ml of distilled water, and stored at −20°C until further processing. Additional subsamples (2 ml) were placed in reaction vials and stored at −20°C for flow cytometric determination of total cell counts.

FIG. 1.

FIG. 1.

Map of the German Bight of the North Sea indicating the sampling locations along the three transects (numbers) and the site of sediment sampling (⊗). The arrow points to the location of the island of Helgoland.

Sediment samples were collected on 20 February 2001 from a near-shore intertidal mud flat at Dangast, located in the Jadebusen Bay of the German Wadden Sea. Sediment cores were sliced into 0.5-cm sections and fixed in 4% (vol/vol) formaldehyde solution. Subsamples were diluted, sonicated, and filtered onto white membrane filters (type GTTP; pore size, 0.2 μm; size, 25 mm; Millipore) as described previously (37).

Total cell counts.

Total picoplankton cell numbers in the <3-μm water fraction were determined flow cytometrically as described previously (12). For quantification of potential cell loss during lysozyme treatment (see below), plankton samples were filtered onto polycarbonate filters (type GTTP; diameter, 25 mm; pore size, 0.2 μm; Millipore) by using a gentle vacuum and cellulose nitrate support filters (pore size, 0.45 μm; Sartorius) to optimize the distribution of cells on the filters. Filters were subsequently washed twice with 5 ml of ultrapure water (MQ; Millipore). Next, the filters were (i) either embedded in agarose (see below) or left unembedded; (ii) treated with lysozyme for 0, 40, or 90 min; and (iii) hybridized with the HRP-labeled probe EUB338 (2) as described below. All preparations were done in triplicate.

FISH with Cy3-labeled oligonucleotide probes.

Sections of filters were hybridized with the probes EUB338, NON338 (3), ROS537 (14), and SAR86-1249 (13) as described previously (19). Oligonucleotides labeled with the cyanin dye Cy3 were purchased from ThermoHybaid (Interactiva Division, Ulm, Germany).

Sample prozessing for hybridization with HRP-labeled probes.

A detailed protocol of all steps of sample processing for CARD-FISH is given in Table 1. To avoid cell loss during cell wall permeabilization, filters were dipped in low-gelling-point agarose (0.2% [wt/vol] in MQ [MetaPhor Bioproducts, Rockland, Maine]), dried face up on glass slides at 35°C, and subsequently dehydrated in 96% (vol/vol) ethanol for 1 min. To inhibit endogenous peroxidases, samples from Wadden Sea sediment were treated overnight with 0.1% (wt/vol) active diethyl pyrocarbonate (Fluka, Taufkirchen, Germany) in phosphate-buffered saline (PBS; 145 mM NaCl, 1.4 mM NaH2PO4, 8 mM Na2HPO4 [pH 7.4]) at 37°C. For cell wall permeabilization, filters were incubated in a lysozyme solution (10 mg ml−1 in 0.05 M EDTA, 0.1 M Tris-HCl [pH 7.5]; Fluka) at 37°C for at least 30 min. The sections were washed with MQ, dehydrated with 96% ethanol, dried at room temperature, and subsequently stored in petri dishes at −20°C until further processing.

TABLE 1.

Summary of steps for FISH and CARD of marine bacteria

Stage Step no. Descriptiona
Embedding 1 Prepare subsamples on membrane filters (37).
2 Dip filters in 0.2% low-gelling-point agarose; place filters face up onto glass slides and air dry at 35°C.
3 Dehydrate filters in 96% ethanol (1 min, RT).
4 Air dry filters.b
Permeabilization and inactivation of peroxidases 5 6 7 Incubate in lysozyme (37°C, >30 min). Sediment samples: incubate them in 0.1% active diethyl pyrocarbonate in PBS (37°C, overnight). Wash filters twice in MQ (1 min, RT).
8 Wash filters in 96% ethanol (1 min, RT).
9 Air dry filters.b
Hybridization 10 Cut filters into sections.
11 Place sections in reaction vial (0.5 ml, 10 to 20 sections per vial).
12 Mix 400 μl of hybridization buffer and 4 μl of probe working solution, and add to filter sections.
13 Incubate filters at 35°C for at least 2 h.
14 Wash filters in prewarmed washing buffer (10 min, 37°C); do not air dry filter sections after washing them.
Tyramide signal amplification 15 16 Remove excess liquid with blotting paper but do not let the filters run dry. Incubate filters in 1× PBS amended with 0.05% of Triton X-100 (50 ml, RT, 15 min, mild agitation).
17 Dab filters on blotting paper but do not let them run dry.
18 Incubate filters in substrate mix (1 part Cy3-tyramide, 10 parts of amplification diluent) (RT, 10 min, in the dark).
19 Dab filter on blotting paper.
20 Wash filter for 15 min as described in step 16.
21 Wash filter in 10 ml of MQ (RT, 1 min).
22 Wash filter in 10 ml of 96% ethanol (RT, 1 min).
23 Air dry preparations.b
24 Counterstain filters with DAPI.b
a

RT, room temperature.

b

Preparations may be stored at −20°C for several days to weeks without an apparent loss in signal.

FISH with HRP-labeled oligonucleotide probes.

For FISH with the probes EUB338, NON338, ROS537, and SAR86-1249 labeled with HRP, 10 to 20 filter sections were placed in a 0.5-ml reaction vial. Then, 400 μl of hybridization buffer (0.9 M NaCl, 20 mM Tris-HCl [pH 7.5], 10% dextran sulfate [wt/vol], 0.02% [wt/vol] sodium dodecyl sulfate [SDS], 55% [vol/vol] formamide [Fluka], 1% [wt/vol] Blocking Reagent [Boehringer, Mannheim, Germany], 0.5 mg of salmon sperm DNA [Boehringer] ml−1, 0.5 mg of Escherichia coli tRNA [Boehringer]ml−1) and 4 μl of HRP probe working solution (50 ng μl−1; ThermoHybaid) were pipetted onto the filter sections. The reaction vial was incubated at 35°C for 2 h, and the filter sections were removed from the hybridization mixture and incubated in 50 ml of prewarmed washing buffer (3 mM NaCl, 5 mM EDTA [pH 8.0], 20 mM Tris-HCl [pH 7.5], 0.01% [wt/vol] SDS) at 37°C for 10 min. A formamide concentration of 55% was used for all probes. The hybridization buffer was prepared as follows: dextran sulfate, NaCl, SDS, and Tris-HCl were mixed, brought into solution at 60°C, and subsequently cooled on ice. Formamide, Blocking Reagent, salmon sperm DNA, and E. coli tRNA were then added. The hybridization buffer was then stored at −20°C for up to 3 months without any apparent effects on FISH detection rates.

In situ detection of HRP-conjugated oligonucleotide probes.

To equilibrate the probe-delivered HRP, sections were placed in 10 ml of 1× PBS amended with 0.05% of Triton X-100 for 15 min at room temperature. To remove excess buffer, the filter sections were dabbed onto blotting paper and immediately transferred to a substrate mix containing 1 part of tyramide-Cy3 and 10 parts of amplification buffer (TSAdirect; NEN Life Science Products, Boston, Mass.) and incubated for 10 min at room temperature in the dark. Filter sections were then briefly placed on blotting paper to remove excess tyramide-Cy3 and washed at room temperature in the dark in 10 ml of 1× PBS amended with 0.05% of Triton X-100, MQ, and 96% ethanol, respectively. To decrease background fluorescence, sections were subsequently washed in MQ and 96% ethanol for 1 min. Afterward, filter sections were air dried and stored at −20°C until further processing (within 2 days).

In order to test whether a higher substrate concentration would increase detectability, a concentration series of tyramide-Cy3 was performed at the following dilutions (parts of tyramide-Cy3:parts of amplification buffer): 1:200, 1:100, 1:50, 1:20, and 1:10.

Microscopic evaluation.

Filter sections were covered in mountant (5.5 parts of Citifluor [Citifluor, Ltd., London, United Kingdom], 1 part of VectaShield [Vector Laboratories, Burlingame, Calif.], and 0.5 parts of 1× PBS amended with DAPI [4′,6′-diamidino-2-phenylindole] at a final concentration of 1 μg ml−1]) and evaluated on a Zeiss Axioplan microscope (Carl Zeiss, Jena, Germany), equipped with an HBO 100-W Hg vapor lamp, appropiate filter sets for Cy3 and DAPI fluorescence (20), and a 100× Plan Apochromat objective. Between 600 and 800 DAPI-stained objects were counted per sample.

Statistical evaluation.

Statistical evaluation was carried out with the software STATISTICA (v.5.0; StatSoft, Tulsa, Okla.). We tested whether the percentage of DAPI counts detected by probe EUB338 and CARD-FISH were different from those detected with monolabeled EUB338 in plankton and sediment samples. The Wilcoxon matched pair test was used as a nonparametric alternative to the Student's t test for dependent samples.

RESULTS

Optimization of sample pretreatment, hybridization, and substrate reaction for CARD-FISH.

Initial experiments for method development were carried out with an HRP-labeled oligonucleotide probe targeting Bacteria (EUB338) and surface bacterioplankton samples from the North Sea. To optimize the permeabilization of bacterial cell walls, different chemicals and enzymes, such as SDS, formamide, Triton X-100, acetone, proteinase K, and lysozyme, were examined. The latter showed the best results with respect to detection rate and was therefore used for CARD-FISH. In order to quantify potential cell loss, a lysozyme incubation time series was performed. We could not detect significant cell loss (DAPI total counts) in agarose-embedded samples even after 90 min of lysozyme treatment (Fig. 2). In contrast, a strong decline in cell numbers was observed in samples that were not embedded. After 90 min of lysozyme incubation, two-thirds of the cells were lost, i.e., had detached from the filters or were disrupted beyond DAPI detectability. Samples that were not treated with lysozyme showed lower detection rates and hybridization signals after CARD-FISH. Detection rates of a EUB338-HRP with CARD increased from (46±2)% of DAPI-stained cells in the unpermeabilized samples to (86±5)% after 40 min of permeabilization (Fig. 2).

FIG. 2.

FIG. 2.

Lines and symbols indicate the abundances of bacterioplankton cells on membrane filters during incubation with lysozyme (10 mg ml−1 at 37°C) with or without embedding in low-gelling-point agarose. Bars indicate the percent FISH detection rates with an HRP-labeled probe and CARD in embedded samples. The error bars indicate either standard deviations (abundances) or total ranges (percentages) of triplicates. Symbols: ▧, EUB338-HRP; ○, agarose embedding (DAPI); •, not embedded (DAPI).

At the probe concentrations recommended by many FISH protocols (2 to 5 ng μl−1) (19), we observed numerous unspecific fluorescent deposits after CARD-FISH. In order to decrease background, we lowered the probe concentration 10-fold (48). This resulted in the elimination of nonspecific deposits of Cy3-tyramide without decreasing the signal intensities or detection rates (data not shown). We also varied the tyramide concentration in the substrate mix for TSA (Fig. 3). At the tyramide dilutions recommended by the manufacturer (1:50 to 1:200), we could detect only 37 to 66% of the DAPI-stained cells (Fig. 3). After we increased the tyramide concentration to 1:10 and 1:20, the abundances of probe-positive cells increased to 86 and 71% of the DAPI-stained cells, respectively, without a substantial increase in background fluorescence. Tyramide concentrations higher than 1:10 resulted in a high background fluorescence (data not shown). A prolonged hybridization period also positively influenced the detection rates (Table 2), yet hybridization periods longer than 2 h did not further raise detection rates (data not shown). For subsequent quantification of North Sea bacterioplankton and Wadden Sea bacteriobenthos by CARD-FISH, we used the optimal set of conditions as determined in our earlier experiments (see also Table 1).

FIG. 3.

FIG. 3.

FISH detection rates with HRP-labeled probes and CARD at increasing dilution of tyramide substrate in plankton samples. The numbers on the x axis indicate parts of amplification diluent added to one part of tyramide-Cy3. The arrow indicates the range of tyramide concentrations recommended by the manufacturer. The error bars show the ranges of triplicate experiments.

TABLE 2.

Detection rates of bacterioplankton by FISH with HRP-labeled probes and CARD after 1.5 and 2.0 h of hybridization, respectively, and by FISH with Cy3-monolabeled probesa

Probe (hybridization period [h]) Label Detection rate (% DAPI)
Mean Range
EUB338 (1.5) HRP 81.3 55.0-99.6
EUB338 (2.0) HRP 93.8 84.9-100.0
EUB338 Cy3 47.8 19.4-66.2
ROS537 HRP 4.7 1.9-7.2
ROS537 Cy3 4.6 2.4-7.1
SAR86 HRP 7.4 2.9-13.2
SAR86 Cy3 NDb
NON338 HRP ND
a

EUB338, most bacteria; SAR86-1249, members of the SAR86 clade; ROS537, members of the Roseobacter clade; NON338, EUB338 antisense probe.

b

ND, not detectable (<1 positive cell in 10 microscopic fields).

We also tested whether our setup allowed specific discrimination of microbes with a one-base mismatch at the probe target site. We hybridized a pure culture of a Pseudoalteromonas sp. strain (γ-proteobacteria) with the oligonucleotide probes Bet42a (β-proteobacteria) and Gam42a (γ-proteobacteria) (3). No nonspecific FISH staining of the strain by probe Bet42a was observed (data not shown).

Quantification of cells in environmental samples.

The densities of heterotrophic picoplankton in 3-μm prefiltered water along the three transects ranged between 1.7 × 105 and 9.9 × 105 cells ml−1, and abundances were highest in samples that were closest to the coast (Table 3). In all of these samples, bacterial cells detectable by FISH with EUB338-HRP accounted for most (mean, 94%; range, 85 to 100%) of the DAPI-stained cells (Fig. 4). The detection rates with monolabeled EUB338-Cy3 were significantly lower (mean, 48%; range, 19 to 66%; n = 20; P < 0.001) (Fig. 4). A highly significant difference in detection rates was also observed in Wadden Sea sediment samples from February 2001 (n = 10, P < 0.01) (Fig. 5). In the permanently mixed upper sediment layers (0 to 6 cm), cell densities determined with EUB338-HRP (mean, 93%; range, 87 to 100%) were almost twice as high as cell densities determined by EUB338-Cy3 (mean, 51%; range, 35 to 72%). In the deeper layers the detection rates obtained with both EUB338-HRP (mean, 63%; range, 53 to 74%) and EUB338-Cy3 (mean, 31%; range, 26 to 39%) were lower than those in the upper layers. In samples from both the water column and the sediment, the fluorescence intensities of single cells and the signal-to-background ratios were much greater with HRP-labeled probes than with monolabeled probes (Fig. 6). Consequently, the discrimination between probe-positive and probe-negative cells was much easier with HRP-labeled probes, and therefore quantification was much faster than with singly labeled probes.

TABLE 3.

Cell numbers of heterotrophic picoplankton in 3-μm prefiltered surface water from the German Bight obtained along three transects in October 1999

Station Abundance (105 cells ml−1) in transect:
1 2 3
1 4.5 6.5 2.8
2 4.2 6.3 1.7
3 2.5 5.1 2.4
4 6.0 3.2 2.6
5 6.2 3.2 2.5
6 6.0 2.1 2.3
7 9.9
8 5.6

FIG. 4.

FIG. 4.

Comparison of detection rates by FISH with a Cy3-monolabeled general bacterial probe (EUB338) and CARD-FISH with an HRP-labeled probe along three transects in North Sea surface water samples obtained in October 1999. Symbols: ○, EUB338-HRP, •, EUB338-mono.

FIG. 5.

FIG. 5.

Comparison of detection rates by FISH with a Cy3-monolabeled general bacterial probe (EUB338) and CARD-FISH with an HRP-labeled probe in Wadden Sea sediment samples obtained in February 2001. Symbols: ○, EUB338-HRP, •, EUB338-mono.

FIG. 6.

FIG. 6.

Photomicrographs of FISH-stained marine bacteria. Each double panel depicts DAPI staining in blue (left) and probe staining in red (right). Exposure times for images of FISH staining with Cy3-monolabeled probes (FISH-mono) were 10 times those for CARD-FISH staining. (a to d) FISH with the general bacterial probe EUB338: sediment, FISH-mono (a); sediment, CARD-FISH (b); plankton, FISH-mono (c); plankton, CARD-FISH (d). (e) Plankton, CARD-FISH with ROS537, specific for members of the Roseobacter lineage. (f) Plankton, CARD-FISH with SAR86-1249, specific for members of the SAR86 clade. Scale bar, 10 μm.

For the determination of the nonspecific binding of HRP-labeled probes and nonspecific substrate precipitation by endogenous peroxidases and/or pseudoperoxidase activities, all samples were also hybridized with an antisense EUB338, NON338-HRP. We found no probe-positive cells in the transect samples (20 samples, 10 microscopic fields inspected per sample) and four probe-positive cells in all of the sediment samples (10 samples, 10 microscopic fields inspected per sample).

In samples from the transect the detection rates of members of the Roseobacter group with either CARD-FISH or a Cy3-monolabeled probe were statistically indistinguishable (n = 20, P = 0.84) (Table 2), and both techniques stained a morphologically homogeneous cell population of 0.5 × 105 to 3.9 × 105 cells ml−1 (Fig. 6 and 7). The highest Roseobacter abundances were found nearest to the coast, and this group closely followed the patterns of total cell numbers (Spearman rank correlation, n = 20, r = 0.89, P < 0.001) (Fig. 7 and Table 2). By using a Cy3-monolabeled probe specific for members of the SAR86 clade (13), we could not detect any stained cells. In contrast, the relative abundances of up to 13% of the DAPI counts could be observed after CARD-FISH with an HRP-labeled probe, and SAR86 exhibited a pronounced fluctuation in cell numbers across the three transects (Fig. 7 and Table 2). Cells detected with probe SAR86-1249-HRP were morphologically uniform (Fig. 6)

FIG. 7.

FIG. 7.

Abundances of members of the SAR86 (probe SAR86-1249) and Roseobacter (probe ROS537) clades, with specific HRP-labeled probes and CARD-FISH along three transects in surface water samples from the North Sea obtained in October 1999. Symbols: ▵, ROS537-HRP; ▪, SAR86-1249-HRP.

We also tested our protocol on samples from Monterey Bay, Calif. (depth profile, 0 to 200 m). At a depth below 50 m, the densities of positive cells after CARD-FISH were comparable to those from hybridizations with a multiply labeled polyribonucleotide probe targeted to Bacteria (10, 36), whereas only a few cells were detectable with Cy3-monolabeled probes (data not shown).

DISCUSSION

In this study, we modified and extended existing protocols by using HRP-labeled oligonucleotides and CARD for the identification of single prokaryotic cells. The combination of several small but significant modifications (Table 1) allowed a substantial increase of FISH sensitivity in marine bacterioplankton and bacteriobenthos compared to that observed in previous reports (27, 40). The attachment of cells onto polycarbonate filters with freshly prepared low-gelling-point agarose was found to be crucial for preventing cell loss during a permeabilization step that was required for high FISH detection rates (Fig. 2). Lowering the probe concentration 10-fold helped to eliminate high background fluorescence without loss of signal intensity of the specifically stained cells, and increasing the tyramide concentration also resulted in significantly increased detection (Fig. 3). Negative controls without probe or with probe NON338-HRP consistently yielded very few or no fluorescently labeled cells. A potential future improvement of the method might aim at lowering the required tyramide concentration, e.g., by increasing the temperature during signal amplification (A. Pernthaler, unpublished data).

By using our CARD-FISH protocol, we were able to detect the majority of DAPI-stained cells in plankton samples, suggesting that the permeabilization procedure is sufficient for most bacteria in North Sea surface waters and for surface Wadden Sea sediments. However, the protocol was not specifically tested for either archaea, planctomyces, or gram-positive bacteria, which may be present in the marine environment (9, 13, 16, 25, 38), and our permeabilization strategy might not be adequate for the detection of these groups (47). Our results are consistent with previously reported low abundances of marine archaea in coastal surface waters during autumn, as determined by other techniques (33, 36), and currently there is no evidence that Actinobacteria occur in high densities in the marine plankton. The comparatively low CARD-FISH detection rates in the permanently stratified, deeper layers of Wadden Sea sediments (Fig. 5) might be due to the presence of inadequately permeabilized Archaea or Actinobacteria or to other groups that are not targeted by the bacterial probe EUB338, such as Planctomycetales or Veruccomicrobiales (8). Alternatively, higher relative abundances of dead or empty cells (23) might also be present in deeper sediment layers.

It has been shown in pure cultures that FISH reliably detects subpopulations with higher rRNA contents but may miss nongrowing or starving cells (12, 34). Since only a fraction of bacteria in the marine pelagic environment is growing (18, 26, 28), FISH counts with monolabeled probes may not show the true abundances of particular target organisms in oligotrophic environments (36). In fact, whole populations of particular taxa, such as members of the ubiquitous marine SAR86 clade (32), may remain completely undetected by FISH with directly Cy3-labeled probes (Table 2). SAR86 has been shown to be abundant in different marine surface waters (7, 22, 44). Members of this lineage could be detected in coastal North Sea surface plankton during summer, when FISH detection rates with monolabeled probes exceeded 70%, but not in the spring, autumn, or winter samples (13). In contrast, a substantial population was readily visualized and quantified by CARD-FISH even in October (Fig. 6 and 7). Microbes belonging to SAR86 are apparently not reliably detected with monolabeled fluorescent probes. This conclusion is also supported by the complete absence of SAR86 in only some of the stations along a coastal transect in the Pacific Ocean (7).

The application of single monolabeled oligonucleotide FISH probes in the marine environment is, therefore, probably limited to surface waters and to particular productive regions, seasons, or sediments (30, 36, 42). In addition, it is sometimes hardly predictable if bacterial populations are detected only partially or quantitatively by this FISH approach. For example, members of the Roseobacter lineage could be adequately quantified both by singly labeled probes and by CARD-FISH (Fig. 7 and Table 2) even in plankton samples in which the general FISH detection rates were <50% of those for the DAPI-stained objects (Fig. 4).

Recently, multilabeled polyribonucleotide probes (10, 25, 36) have been introduced to overcome this limitation, and other techniques for the quantification of population sizes, such as the 5′-nuclease assay (45), are also unaffected by low bacterial activity. In many instances our protocol might provide a technically less demanding alternative to the above approaches. CARD-FISH could furthermore be attractive to researchers because an increasing number of well-tested oligonucleotide probes are available for different marine environments (13, 39, 50) and the design of new probes is relatively simple (37). In addition, there are well-established protocols for the conjugation of tyramine with fluorescent dyes at a fraction of the costs of the commercial products (24).

The potential of the CARD approach is not limited only to the staining of rRNAs. If whole fixed cells are made accessible for enzymes and/or antibodies, a wide range of methods routinely used in histology and cytology could also be applied in environmental microbiology, such as detection of mRNAs (47). Many mRNA species are present in abundances ranging from 1 to 1,000 copies per cell and therefore are not detectable for most nonradioactive in situ assays. Various CARD-FISH methods for the detection of mRNA in single cells might be developed, depending on the sample and the target copy number. For example, it is feasible to hybridize not only with oligonucleotide probes directly labeled with HRP but also with digoxigenin-labeled polynucleotide probes followed by an antibody reaction which delivers the HRP (6, 46, 47). Furthermore, tyramides with different types of haptens (both fluorescent and nonfluorescent) could be used for the signal amplification step. Haptens could be involved in another anti-hapten antibody reaction, and antibodies can again be labeled with HRP for a second (and a third) layer of CARD, allowing an increase in sensitivity of up to 1,000-fold (43). However, one should keep in mind that the size of the HRP alone is ca. 40,000 Da, and the size of this complex increases when it is linked to other molecules such as oligonucleotides or antibodies. This may again compromise diffusion through cell walls and membranes and may require major adaptations of permeabilization procedures (47).

In summary, we developed and explored a novel FISH protocol based on CARD and FISH with HRP-labeled oligonucleotides. This approach permits the detection of small marine bacteria with low ribosome content that are not or only barely detectable with monolabeled probes.

Acknowledgments

We thank M. Mussmann for providing sediment samples, G. Gerdts for organizing the North Sea cruise and help during sampling, and the crew of the RV Uthörn. V. T. Tempranillo is acknowledged for fruitful discussions.

This work was supported by the German Ministry of Education and Research (BMBF 01 LC0021/TP4) and by the Max Planck Society.

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