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Applied and Environmental Microbiology, February 2004, p. 804-813, Vol. 70, No. 2
0099-2240/04/$08.00+0 DOI: 10.1128/AEM.70.2.804-813.2004
Copyright © 2004, American Society for Microbiology. All Rights Reserved.
Department of Biological Oceanography, Royal Netherlands Institute for Sea Research, Texel, The Netherlands
Received 29 August 2003/ Accepted 31 October 2003
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Although the overall role of bacterioplankton in the cycling of organic carbon and nutrients in the sea has been fairly well studied (2, 3, 10), current knowledge of the functional role of planktonic Archaea is rather rudimentary. Archaea are ubiquitously distributed throughout the world's oceans (11, 19) and constitute a numerically dominant group of the microbial community in the meso- and bathypelagic zones (12). It has been reported that marine planktonic Archaea take up amino acids (30) and bicarbonate (48) and therefore are metabolically active in the oceanic water column. Thus far, marine pelagic Archaea have withstood all attempts at cultivation in pure cultures, making it impossible to isolate viruses infecting these Archaea. Thus, the question arises as to whether marine Archaea are controlled by viruses in a manner similar to that reported for Bacteria. Previous studies of interactions of viruses and Archaea focused on viruses of extremophiles (4, 29, 49); however, the influence of viruses on marine pelagic Archaea has not been studied yet.
For decades, microbial ecologists used batch cultures to investigate the responses of complex prokaryotic communities to experimental manipulation. However, conclusions based on such incubations must be drawn cautiously, as first noted by ZoBell (50). Recently, studies on the effects of confinement of prokaryotic assemblages found shifts in the phylogenetic compositions of bacterial communities as a consequence of the exclusion of grazers (37, 40) and increased metabolic activity of at least some prokaryotes compared to the results obtained under in situ conditions (36). Massana and Pedrós-Alió (20) showed that bacterial communities in confinement are altered significantly within a few days of incubation and that these alterations are accompanied by dramatic decreases in community richness. However, incubation of microorganisms in micro- and mesocosms remains an invaluable tool for answering specific questions, especially when dealing with otherwise unculturable microorganisms such as marine Archaea.
The objective of this study was to monitor the responses of complex bacterial and archaeal communities to virus amendments by using terminal restriction fragment length polymorphism (T-RFLP) analysis of PCR-amplified 16S rRNA gene fragments. We present the results of batch culture experiments carried out with samples from two contrasting environments, the tropical Atlantic Ocean and the North Sea.
(This work was carried out in partial fulfillment of the requirements for a Ph.D. degree from the University of Groningen by C. Winter.)
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FIG. 1. Map of the sampling stations in the tropical Atlantic Ocean (A) and the North Sea (B). AF1, 28 January; AF2, 3 February; AF3, 6 February; NS1, 13 December.
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Each experiment consisted of four batch cultures in 10-liter glass bottles (Duran glass; Schott), soaked in 1 N HCl overnight and rinsed several times with virus-free ultrafiltrate before use. After an aliquot (100 to 150 ml) of the prokaryotic concentrate was dispensed into the culture flasks, virus-free ultrafiltrate from the same sampling site was added to a total volume of 500 ml. An aliquot (95 to 200 ml) of the viral concentrate was heated three times nearly to boiling in a microwave oven and chilled on ice for 10 min between the heating steps to inactivate the viruses (32). The viral concentrate was distributed as follows: one flask received no viruses; the second flask received one aliquot of the heat-inactivated viral concentrate; and the third and fourth flasks received one and two aliquots, respectively, of the untreated viral concentrate. Thus, each experiment consisted of two negative controls, corresponding to the treatments without virus amendment and with inactivated viruses, and two virus treatments. Finally, the culture flasks were filled with virus-free ultrafiltrate from the same sampling site to a final volume of 10 liters. The treatments are referred to here according to the initial viral abundance relative to the in situ abundance (e.g., 100%Vir-inactive indicates treatment with a microwave-treated aliquot of the viral concentrate equivalent to 100% of the in situ viral abundance, 0%Vir indicates treatment without the addition of viruses, and 100%Vir indicates treatment with an aliquot of the viral concentrate equivalent to 100% of the in situ abundance). Prokaryotic abundance at the start of the incubations ranged from 10 to 100% of the in situ prokaryotic abundance. The label used for the stations (AF1, AF2, AF3, and NS1) was also used to denote the experiments performed with water from these stations. The batch cultures were incubated in the dark at the in situ temperature for up to 96 h. Subsamples for prokaryotic and viral abundance determinations were taken from each batch culture at regular intervals (4 to 6 h). Additionally, prokaryotic cells from 1-liter subsamples of each batch culture were collected on 0.22-µm-pore-size filters (Isopore GVWP, 100-mm diameter; Millipore) every 24 h. These filters were shock frozen in liquid nitrogen and stored at -80°C until further processing for nucleic acid extraction and T-RFLP analysis.
In order to obtain an estimate of the viral impact on prokaryotes during the incubations, we assumed that increases in viral abundance typically detected in 4- to 6-h intervals in the incubations are a measure of net viral production. For each peak in the development of viral abundance, the net increase in viral abundance per time was divided by an assumed burst size of 30 and by the bacterial abundance at the start of the peak. The lysis rates expressed as a percentage of the prokaryotic standing stock lysed per hour were averaged over all detected peaks in an incubation.
Prokaryotic and viral abundance.
Samples (3 ml) for the enumeration of prokaryotic cells and viruses were fixed with formaldehyde (final concentration, 2%) and filtered through 0.02-µm-pore-size filters (Anodisc, 25-mm diameter; Whatman). Prokaryotic cells and viral particles on the filters were stained with SYBR-Green I (Molecular Probes) and enumerated by epifluorescence microscopy by the procedure of Noble and Fuhrman (27).
Nucleic acid extraction.
Extraction of the nucleic acids from the filters was carried out as described by Winter et al. (45). Briefly, the procedure consisted of four freeze-thaw cycles (-196°C to +37°C) and subsequent treatment with lysozyme (Sigma catalog no. L-7651) and proteinase K (Fluka catalog no. 82456) in 1% sodium dodecyl sulfate. No intact cells were found after the final incubation step, as determined by epifluorescence microscopy for selected samples from all experiments, indicating complete lysis of the cells. The liquid phase was extracted once with an equal volume of a mixture of phenol, chloroform, and isoamyl alcohol (25:24:1) buffered with 10 mM Tris-HCl (pH 8.0)-1 mM disodium EDTA and with chloroform-isoamyl alcohol (24:1) (35). Ethanol precipitation overnight at -20°C was used to concentrate and clean the extracted nucleic acids. The pellet was redissolved in 100 µl of ultrapure water (Sigma catalog no. W-4502). Fifty microliters of this crude nucleic acid extract was purified further by using a QIAEX II gel extraction kit (Qiagen) as recommended by the manufacturer for DNA fragments of larger than 10 kbp. The nucleic acids were recovered in a final volume of 20 µl of elution buffer (Qiagen) and used for subsequent PCR amplification. Two microliters of this nucleic acid extract were loaded onto a 1% agarose gel to check the integrity of the DNA.
PCR, restriction digestion, and T-RFLP analysis.
The PCR conditions and chemicals used here were the same as those described by Moeseneder et al. (23). Briefly, 1 to 2 µl of the cleaned nucleic acid extract was used as a template in a 50-µl PCR mixture. We used primer 27F, specific for Bacteria, in combination with universal primer 1492R (14) and, in a second reaction, primers 21F and 958R, specific for Archaea (8), to amplify ca. 1,480-bp and ca. 920-bp fragments of the bacterial and archaeal 16S rRNA genes, respectively. For T-RFLP analysis, forward and reverse primers were fluorescently 5'-end labeled with phosphoramidite fluorochrome 5-carboxy-fluorescein and 6-carboxy-4',5'-dichloro-2',7'-dimethoxyfluorescein, respectively (both from Interactiva, Ulm, Germany). After PCR amplification, excess fluorescently labeled primer was removed by ethanol precipitation and subsequent gel purification in a 1% agarose gel with TAMRA loading dye (Perkin-Elmer Applied Biosystems). Properly sized bands were cut from the gel, and the PCR fragments were recovered in 20 µl of elution buffer by using a QIAquick gel extraction kit (Qiagen). Finally, 1 µl of the purified PCR fragments and 5 µl of SmartLadder (Eurogentec, Seraing, Belgium) were run on a 1% agarose gel for quantification purposes.
The restriction digests contained 50 ng of purified PCR fragments as well as 20 U of HhaI restriction enzyme and the recommended buffer (both from Amersham Pharmacia Biotech) in a total volume of 100 µl. Restriction was performed at 37°C for 12 h to ensure complete digestion. The DNA fragments from the restriction digests were recovered in a final volume of 2 µl of ultrapure water by performing linear polyacrylamide precipitation (22). T-RFLP analysis was performed with an ABI Prism 310 automated capillary sequencer (Perkin-Elmer Applied Biosystems) as previously described (23).
Cloning of PCR-amplified archaeal 16S rRNA gene fragments.
Cloning of PCR-amplified fragments of the archaeal 16S rRNA gene was performed by using a pMOSBlue blunt-ended cloning kit (Amersham Pharmacia Biotech catalog no. RPN 5110) according to the manufacturer's instructions. Based on the uniqueness of the T-RFLP patterns, 11 samples from the tropical Atlantic Ocean were chosen for cloning. Inserts were obtained by PCR amplification with the archaeal primer pair as described above, except that the primers were not 5'-end labeled. We used 40 ng of insert per cloning reaction, corresponding to a molar ratio of vector to insert of 1:2.5. Thirty colonies containing an insert were randomly picked from each of the 11 transformations, resuspended in 200 µl of ultrapure water, and incubated at 95°C for 5 min. The clone libraries were screened by using 1 µl of this suspension as a template in PCRs with the fluorescently labeled archaeal primer pair and performing T-RFLP analysis as described above.
Sequencing and phylogenetic analysis.
Sequencing of the clones harboring unique archaeal 16S rRNA gene fragments was performed by using an ABI Prism BigDye terminator cycle sequencing ready reaction kit (Perkin-Elmer Applied Biosystems) in a PCR consisting of 25 cycles (denaturation at 96°C for 10 s, annealing at 55°C for 5 s, and elongation at 60°C for 4 min). We sequenced from both ends of the fragments by using forward primer 21F and reverse primer 958R. Amplicons were subsequently purified by isopropanol precipitation, and sequences were obtained by using an automated sequencer (ABI Prism 310). Contiguous sequences were assembled by using the software package AutoAssembler (version 2; Perkin-Elmer Applied Biosystems). First, the nucleotide sequences were evaluated with the program Chimera_Check (version 2.7; Ribosomal Database Project at Michigan State University; http://rdp.cme.msu.edu/html/) (18) to identify possible chimeric artifacts. Further analysis involved alignment of the sequences with ARB (version 071101-7; Technical University of Munich; http://www.arb-home.de) and comparison to the 16S rRNA gene sequences in the GenBank nucleotide library by BLASTN searching (version 2.2.5; National Center for Biotechnology Information; http://www.ncbi.nlm.nih.gov/BLAST/) (1). The sequences from this study, together with 16 additional sequences retrieved from GenBank, were used to construct a phylogenetic tree with maximum likelihood (PHYLIP; version 3.5; http://evolution.genetics.washington.edu/phylip.html/) (9). The additional sequences from GenBank were Thermus aquaticus, Cenarchaeum symbiosum, AEGEAN_52, AEGEAN_58, AEGEAN_59, AEGEAN_66, AEGEAN_70, DCM65231, PVA_OTU_1, DCM875, SBAR16, ME-450_P9, 19a-27, DCM858, PVA_OTU_3, and WHARQ. The branching of the tree was evaluated by bootstrapping with the programs Seqboot and Consense (PHYLIP).
Numerical analysis of T-RFLP patterns.
Due to the variability in the discriminatory power of the forward and reverse primers for the Bacteria and the Archaea, the results obtained with both primers were combined for each group, serving as a measure of community richness. Additionally, the frequency of appearance of each individual peak in the T-RFLP patterns, subsequently referred to as OTUs (25) and obtained at three time points during incubation in experiment NS1 and at four time points in experiments AF1, AF2, and AF3, was calculated for each treatment to identify potential effects of virus amendment on individual OTUs.
Prokaryotic production.
Prokaryotic production was measured as the incorporation of [3H]leucine (final concentration, 20 nM) in duplicate samples and one formaldehyde (final concentration, 2%)-killed blank sample (13). We used a conversion factor of 0.07 x 1018 cells produced per mol of leucine incorporated (33) and a carbon content of 20 fg of C per cell to convert cell production into C biomass production (15).
Concentration of organic carbon.
The concentration of organic carbon in duplicate samples was measured after high-temperature combustion (5) by using an automated analyzer (TOC-5000A; Shimadzu). Unfiltered samples (8 ml; total organic carbon [TOC]) were dispensed directly into combusted (450°C for 4 h) glass ampoules (except for North Sea seawater, which was filtered through combusted [450°C for 4 h] Whatman GF/F filters [nominal pore size, 0.7 µm]; dissolved organic carbon [DOC]) and acidified with 3 or 4 drops of concentrated HCl before the ampoules were sealed. The samples were stored frozen at -20°C until analysis.
Nucleotide sequence accession numbers.
The 16S rRNA gene sequences obtained in this study were submitted to GenBank and are available under the accession numbers listed in Table 1.
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TABLE 1. Clone designations, corresponding restriction fragments, lengths of nucleotide sequences, and GenBank accession numbers
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TABLE 2. Physicochemical and biological characterization of sampling stations
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FIG. 2. Time courses of prokaryotic abundance in the treatments in experiments AF1, AF2, AF3, and NS1. The error bars represent the standard error of the mean obtained from 30 fields or 300 prokaryotic cells counted per filter. If no error bars are shown, they are smaller than the width of the symbol. Missing data points are due to problems in preserving these samples. N, number.
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FIG. 3. Development of viral abundance in the 0%Vir, 100%Vir-inactive, 100%Vir, and 200%Vir treatments in experiment AF1. The error bars represent the standard error of the mean obtained from 30 fields or 300 viral particles counted per filter. If no error bars are shown, they are smaller than the width of the symbol. N, number.
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TABLE 3. Effects of viral lysis on prokaryotes in the treatments
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FIG. 4. Effects of confinement and virus amendment on the numbers of peaks in the treatments in experiments AF1, AF2, AF3, and NS1, as determined by T-RFLP analysis. The numbers of peaks in the patterns obtained with the forward and reverse primers were combined for the Bacteria and the Archaea. Missing T-RFLP patterns due to problems with PCR amplification are marked by an X. The low bacterial richness in the 65%Vir treatment in experiment AF3 after 24 h is regarded as an outlier.
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FIG. 5. Example of T-RFLP patterns obtained with the archaeal reverse primer (958R) for Archaea with the 0%Vir, 100%Vir-inactive, 100%Vir, and 200%Vir treatments in experiment AF1 after 96 h of incubation. The T-RFLP patterns are centered on the region of interest, and the sizes of the OTUs in base pairs are noted next to the arrows.
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TABLE 4. Effects of virus amendment on OTUs
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FIG. 6. Phylogenetic tree of the archaeal 16S rRNA gene sequences obtained in this study (in bold type) and sequences retrieved from GenBank, as inferred by maximum likelihood based on homologous nucleotide sequences from 49 to 926 bp (Escherichia coli numbering). The accession numbers of the reference sequences retrieved from GenBank are shown in parentheses. Numbers at the nodes represent percentages of bootstrap replicates supporting the branching order. The scale bar represents 0.10 substitution per nucleotide position.
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The use of different volumes of virus concentrate in the treatments might have increased the fraction of bioavailable organic carbon for the confined prokaryotic community compared to the fraction present under in situ conditions. However, the virus fraction of DOC typically is only a small portion of the total DOC (26). Moreover, in experiment AF1, TOC concentrations were measured at the start of the experiment with the different treatments and were lower than the TOC concentrations in situ (data not shown), suggesting that there was no contamination with organic carbon in the ultrafiltration steps. Therefore, it seems unlikely that virus amendment substantially increased the fraction of bioavailable organic carbon at the start of the incubations compared to the fraction present under in situ conditions.
Since no viruses could be detected in the <30-kDa filtrate (data not shown), the initial viral abundance in the 0%Vir treated-samples (Fig. 3) was the result of viruses added with the prokaryotic concentrate. A microwave treatment was used to inactivate the viruses (32), but this treatment did not physically disintegrate all of the viruses, as indicated by the higher viral abundance seen with the Vir-inactive treatments than with the 0%Vir treatments at the start of the experiment (Fig. 3). Due to the inability to differentiate between inactivated viral particles and intact viruses by epifluorescence microscopy, the actual number of intact viruses in the Vir-inactive treatments probably was grossly overestimated in the initial phase of the incubation. However, within the first ca. 30 h of the experiments, viral abundance in the Vir-inactive-treated samples decreased to values similar to those in the 0%Vir-treated samples, likely due to the decay of the inactivated viruses. Furthermore, viral lysis of bacterial cells already infected at the start of the incubations and the potential induction of lysogenic cells could have contributed to viral numbers in all of the treatments.
A number of studies showed that the quantitative interpretation of the results of fingerprinting techniques based on PCR amplification, such as T-RFLP analysis, potentially is biased (7, 31, 41). Thus, only the presence or absence of OTUs was used for subsequent numerical analysis. Due to the variation in the discriminatory power of the forward and reverse primers for Bacteria and Archaea, we found it necessary to combine the results of both primers for each group. Therefore, the results obtained by this approach represent a relative measure of community richness (Fig. 4).
To prove the archaeal origin of the PCR products obtained from the archaeal primers, cloning and sequencing were performed. The archaeal origin of 17 unique OTUs obtained directly from the experiments at different time points was confirmed by phylogenetic analysis (Fig. 6). Although not all of the detected archaeal OTUs could be identified by the cloning procedure, we are confident that the T-RFLP patterns obtained with the archaeal primers reflected the development of the archaeal assemblages, since all 330 screened clones were of archaeal origin.
Development of prokaryotic and viral abundance.
The major loss factor for prokaryotic cells in the experiments likely was viral lysis, since grazers were excluded by filtration. Although the initial prokaryotic abundance in experiment AF1 was similar to that in experiment AF2 (AF1, 0.11 x 106 ml-1, equivalent to 10% of the in situ abundance; and AF2, 0.16 x 106 ml-1, equivalent to 20% of the in situ abundance), the prokaryotic abundance increased sharply after a lag phase of ca. 20 h in experiment AF1 but increased at a lower rate in experiment AF2 (Fig. 2). This difference cannot be explained by the higher virus amendments used in experiment AF1 (100 and 200% of in situ viral abundance) than in experiment AF2 (35 and 55% of in situ viral abundance), since the 0%Vir treatment led to the same sharp increase (Fig. 2). It is possible that prokaryotic abundance at station AF1 was grazer controlled and that, after elimination of the grazing pressure by filtration, prokaryotic cells responded with elevated net growth. Station NS1 (13 December 2000) differed in many aspects from the stations in the tropical Atlantic Ocean (Table 2). The winter situation in the North Sea is characterized by lower temperatures and lower biological activity than in the summer months (17). These unfavorable conditions could explain the unusually long lag phase of ca. 60 h before a sharp increase in prokaryotic abundance was detectable with all of the treatments in experiment NS1 (Fig. 2).
The development of viral abundance in our experiments was a consequence of viral lysis and decay. The strong fluctuations of viral abundance in the experiments (Fig. 3) suggest that viral lysis was changing dynamically over time, even in the samples with strongly reduced viral abundance (0%Vir and Vir-inactive treatments). Among the factors which potentially influenced the development of viral abundance in our experiments were changes in prokaryotic community composition during the incubations (Fig. 4; see below also), the release of virucidal organic matter during viral lysis, prophage induction, and changes in prokaryotic activity.
Proctor and Fuhrman (32) reported that the addition of viruses to incubations of unfiltered seawater (including grazers) reduced prokaryotic abundance by about 25% within 24 h compared to the results for controls without virus amendments. However, in experiments without grazers, the addition of viruses resulted in increases in bacterial abundance (28). This result is similar to the findings of this study, where the average prokaryotic abundance was highest in the presence of the highest virus amendments. In the absence of grazers, the stimulation of prokaryotic growth likely was caused by the increased release of products of viral lysis in the samples with a high viral abundance (28).
Effects of confinement and virus amendment on archaeal and bacterial community richness, as detected by T-RFLP analysis.
Generally, confinement had a strong influence on the prokaryotic communities in our incubations and resulted in dramatic decreases in bacterial and archaeal community richness. Such confinement effects were reported previously for Bacteria but not for archaeal communities and can be more important than treatment effects (20). The removal of phytoplankton and grazers likely contributed to the changes in prokaryotic community composition as well (40).
Bacterial and archaeal communities appeared to react at different times in the incubations. In experiments AF1 and AF2, confinement resulted in decreased bacterial community richness already by 24 h, while the strongest effect of confinement on archaeal community richness was detected in these experiments only after 72 h (Fig. 4). Higher rates of growth of Bacteria than of Archaea in surface waters could explain this pattern by causing a faster response of the bacterial community to changing conditions. Changes in community composition as a result of prokaryotic growth likely occurred in experiment NS1. The unfavorable conditions during winter resulted in a long lag phase with few initial changes in the bacterial community composition. The decrease in bacterial community richness after 67 h coincided with the dramatic increase in prokaryotic abundance, indicating the development of prokaryotic populations which were adapted to the specific experimental conditions (Fig. 2 and 4). The effects of confinement on the bacterial and archaeal communities in experiment AF3 differed from those in experiments AF1 and AF2. While bacterial community richness decreased only slightly compared to initial conditions (to ca. 90%), archaeal community richness decreased by about 60% already by 24 h (Fig. 4). The water used to perform experiments AF1 and AF2 was sampled below the thermocline, whereas the water for experiment AF3 was sampled above the thermocline (data not shown). If indeed differences in growth rates were the cause for the different responses of Bacteria and Archaea to confinement, then our results suggest that Archaea might have been more active in the experiments with water sampled from above the thermocline than from below the thermocline. Alternatively, dilution of the prokaryotes in the experiments, which ranged from 10 to 20% of in situ abundance in experiments AF1 and AF2 and from 90 to 100% of in situ abundance in experiments AF3 and NS1, could have resulted in changes in community composition. If this notion holds true for our experiments, Archaea would react most rapidly to confinement at low dilution rates and Bacteria would do so at high dilution rates (Fig. 4).
Thingstad and Lignell (42) suggested that viruses selectively infect the most abundant members of the prokaryotic community and therefore might be a driving force in maintaining prokaryotic diversity. However, in our incubations, differences in bacterial and archaeal richness between the negative controls and the virus-treated samples were small compared to the effects of confinement and were not consistent over time (Fig. 4). Essentially the same results were obtained when similarity values calculated from the T-RFLP patterns were used (data not shown).
A prediction of the "killing the winner" hypothesis is that the species composition of viral communities should reflect the composition of the host community. Thus, the most abundant viral populations should be infective for the most abundant host populations. It is conceivable that the viral communities in our incubations were not sufficiently adapted to the changing prokaryotic communities; hence, the overall effect of virus amendment on the level of prokaryotic communities as detected by T-RFLP analysis might have been rather small. Another possible explanation for the small differences between the negative controls and the virus-treated samples could be that most members of the prokaryotic communities were resistant to viral infection. Resistance could be caused by a reduction in the number and/or a change in the structure of virus receptors at the surface of the cells or by lysogenic viruses (46). Previous studies demonstrated the ability of prokaryotes to quickly acquire resistance to cooccurring viruses, especially under favorable growth conditions (16, 43). At times when prokaryotes entered logarithmic growth (Fig. 2), resistance to viral infection might have been established in some prokaryotic populations. However, a substantial fraction of the prokaryotic cells receiving the virus treatments in our experiments was infected with viruses (Table 3). Thus, resistance to viral infection and the changing prokaryotic communities in the incubations cannot explain the small differences in community composition between the samples. Middelboe (21) demonstrated that viruses can influence the ratio of sensitive to resistant clones in a prokaryotic population. Therefore, if viruses influence the clonal composition rather than the community composition of prokaryotes, then the effect of viruses might not be detectable by 16S rRNA gene-based community fingerprinting.
Influence of virus amendment on individual OTUs in T-RFLP patterns.
Although the differences seen with the treatments were small and variable over time at the level of archaeal and bacterial communities (Fig. 4), individual OTUs in the T-RFLP patterns of Archaea and Bacteria showed distinct responses to the presence of infectious viruses (Fig. 5). The negative response of some of the OTUs to virus amendment might be explained best by viral lysis and would be consistent with the finding that viral infection increased with virus amendment (Table 3). Another group of OTUs showed no response to virus amendment, possibly as a consequence of resistance of these OTUs to viral infection. Furthermore, the number of lytic viruses infecting these OTUs might have been too low to cause detectable differences in the treatment groups.
It has been argued that the noninfected prokaryotic community can benefit from lysis products (21); consequently, one might expect that some prokaryotic populations are stimulated by the presence of viruses. However, we found no case in which an archaeal or bacterial OTU was detected more frequently in the presence of the virus treatments than in the presence of the 0%Vir and Vir-inactive treatments (Table 4 and Fig. 5). OTUs which were not detected or were hardly detected with the 0%Vir treatments were found with the Vir-inactive treatments, indicating the presence of a stimulatory factor in the virus concentrate (e.g., 172, 179, and 547 bp; Fig. 5). When only the Vir-inactive and virus treatments were compared, these OTUs either were not affected by the infectious viruses or responded negatively only at a high viral abundance. The nature of the stimulatory factor is not known, but it does not seem to be temperature sensitive, since its effect could be detected when the Vir-inactive treatments (microwave-treated virus concentrate) and virus treatments (untreated virus concentrate) were used.
By comparing the frequencies of appearance of the OTUs in the T-RFLP patterns obtained with the different treatments, we found that six OTUs were more frequently detected in the negative controls throughout the entire incubation period (Table 4). In a comparison between the Vir-inactive treatments and the two virus treatments, we found that 44 OTUs (Archaea and Bacteria) were more frequently detected in the presence of the Vir-inactive treatments (data not shown). These results indicate that there is a negative effect of viruses on some OTUs and that viral infection and lysis affect a few abundant hosts, notions that are compatible with the "killing the winner" hypothesis.
Summary and conclusions.
On the level of archaeal and bacterial community richness, the effects of virus amendment were rather small compared to the strong influence of confinement and, moreover, were variable over time. Differences in the responses of individual OTUs to virus amendment were detected for both groups, Archaea and Bacteria. These results are augmented by the finding that six OTUs were detected more frequently in the negative controls throughout the incubation period than in the samples receiving virus treatments. This negative response to the addition of intact viruses probably was due to viral lysis of Archaea and Bacteria. We conclude from this study that marine Archaea respond to confinement and to virus amendment. This conclusion further substantiates the emerging notions that marine pelagic Archaea are metabolically active in the surface layer of the sea and that viral lysis potentially influences the community composition of pelagic Archaea.
Funding for this study was provided by the Dutch Science Foundation (NWO-ALW grant 809.33.004 and grant 835.20.004).
Present address: Diversity, Biogeochemistry, and Microbial Ecology Group, Laboratoire d'Océanographie de Villefranche, 06234 Villefranche-sur-mer, France. ![]()
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