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Applied and Environmental Microbiology, November 2001, p. 5134-5142, Vol. 67, No. 11
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.11.5134-5142.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Isolation of Novel Pelagic Bacteria from the German
Bight and Their Seasonal Contributions to Surface
Picoplankton
Heike
Eilers,1
Jakob
Pernthaler,1,*
Jörg
Peplies,1
Frank
Oliver
Glöckner,1
Gunnar
Gerdts,2 and
Rudolf
Amann1
Max-Planck-Institut für Marine
Mikrobiologie, D-28359 Bremen,1 and
Biologische Anstalt Helgoland, D-27498
Helgoland,2 Germany
Received 22 June 2001/Accepted 4 September 2001
 |
ABSTRACT |
We tested new strategies for the isolation of abundant bacteria
from coastal North Sea surface waters, which included reducing by
several orders of magnitude the concentrations of inorganic N and P
compounds in a synthetic seawater medium. Agar plates were resampled
over 37 days, and slowly growing colonies were allowed to develop by
repeatedly removing all newly formed colonies. A fivefold increase of
colonies was observed on plates with reduced nutrient levels, and the
phylogenetic composition of the culture collection changed over time,
towards members of the Roseobacter lineage and other
alpha-proteobacteria. Novel gamma-proteobacteria from a previously
uncultured but cosmopolitan lineage (NOR5) formed colonies only after
12 days of plate incubation. A time series of German Bight surface
waters (January to December 1998) was screened by fluorescence in situ
hybridization (FISH) with isolate-specific and general probes. During
spring and early summer, a prominent fraction of FISH-detectable
bacteria (mean, 51%) were affiliated with the
Cytophaga-Flavobacterium group (CF) of the
Bacteroidetes. One Cytophaga sp. lineage with
cultured representatives formed almost 20% of the CF group. Members of
the Roseobacter cluster constituted approximately 50% of
alpha-proteobacteria, but none of the Roseobacter-related
isolates formed populations of >1% in the environment. Thus, the
readily culturable members of this clade are probably not
representative of Roseobacter species that are common in
the water column. In contrast, members of NOR5 were found at high
abundances (>105 cells ml
1) in the summer
plankton. Some abundant pelagic bacteria are apparently able to form
colonies on solid media, but appropriate isolation techniques for
different species need to be developed.
 |
INTRODUCTION |
Early marine microbiologists were
convinced that a high percentage of abundant pelagic bacteria
could be recovered on substrate-amended agar plates
(49). This was supported by comparing the
morphologies and Gram-staining reactions of isolates and
free-living cells. Since then, epifluorescence microscopy
(24) and molecular biological techniques have changed our
paradigm about the culturability of common aquatic microbes.
Frequently, less than 1% of all the cells from marine picoplankton
form colonies on solid media (15). The reasons for this
low recovery remain subject of debate (46).
Molecular biology has developed tools that help us to study the
contributions of individual microbial lineages to the picoplankton (11, 17, 19, 36, 38, 47). This knowledge provides ecological criteria for choosing bacterial species as the focus of
cultivation attempts and conversely can show whether isolated strains
belong to lineages that are frequent in the environment (14). With the exception of the Roseobacter
lineage (19), there are no isolates available from many of
the abundant phylogenetic groups in the picoplankton (e.g., the SAR86
cluster or the marine crenarchaeota) (21, 27). In
contrast, a large fraction of frequently isolated bacterial strains are
related to opportunistic genera, such as Vibrio,
Alteromonas, and Marinomonas, which probably inhabit
niches with high substrate concentrations (32) but do not
form large populations in the water column (14).
On the other hand, although the environmental parameters found at
abundance maxima of particular phylogenetic groups may provide important information, a knowledge of the in situ densities does not
readily result in specific cultivation strategies. The sizes of
individual populations in the picoplankton are determined not only by
substrate availability but also by food web structure and by viral
mortality (48). Moreover, many heterotrophic pelagic bacteria and archaea probably overlap in their substrate spectra (26, 28, 35). At present, the appropriate conditions for the cultivation of common pelagic microbes can only be determined empirically.
It is, therefore, generally believed that isolation of model organisms
for the oligotrophic pelagic microbiota will involve laborious and
time-consuming strategies, e.g., dilution to extinction (2, 6,
7). This view has recently been challenged by Pinhassi et al.
(37, 38), who reported that a majority of the common
bacterial species from the water column of the Baltic Sea could be
grown on agar plates amended with ZoBell's original substrate mix
(49). However, Eilers et al. have pointed out the
practical limitations of such an approach (14). In their study, molecular biological techniques indicated the importance of
uncultured gamma-proteobacteria related to SAR86 in coastal North Sea
surface waters, but no representatives from this lineage were found in
>140 bacterial strains collected over 2 years. The probability of
retrieving any additional, novel gamma-proteobacterial isolates without
a change of isolation strategy had decreased to less than 1 in every 50 new strains. So even if all pelagic marine bacteria and archaea were
capable of forming colonies on agar plates, many strains from important
marine lineages might still remain undetected, because of a
predominance of isolates from genera that are rare in the picoplankton.
For example, some oligotrophic species might exhibit a prolonged growth
delay upon transfer to a solid medium. Such bacteria would be rapidly
overgrown by other strains, such as those that are able to actively
disperse over plate surfaces by swarming (12).
We attempted to obtain novel alpha- and gamma-proteobacteria from
coastal North Sea surface waters by modified isolation strategies. The
concentrations of the inorganic nutrients N and P in the growth medium
were reduced, and plate cultivation techniques were adapted to allow
the colony formation of microbes with longer growth delays. The
abundances of those phylogenetic lineages that had been the target of
cultivation were determined in environmental samples collected during
the previous year. In addition, we determined the in situ densities of
members from one culturable lineage of the
Cytophaga-Flavobacterium (CF) group (14).
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MATERIALS AND METHODS |
Sampling site and fixation.
Surface water was collected
weekly (total bacterial counts and phytoplankton) or biweekly (specific
bacterial groups) for the analysis of picoplankton dynamics between
January and December 1998. Samples were obtained by pumping from a 1-m
depth at the Helgoland Roads station (54°09'N, 7°52'E) near the
island of Helgoland, which is situated approximately 50 km offshore in
the German Bight of the North Sea. For cultivation, seawater was
sampled once on 25 August 1999 at the same site. Water was stored at
4°C and processed within approximately 1 h. For fluorescence in
situ hybridization (FISH), portions of 100 ml of unfiltered seawater
were processed as described by Glöckner et al. (16).
Colony formation and enrichment cultures.
A synthetic
seawater medium (MPM) was prepared for cultivation on agar plates as
described by Schut et al. (44). In a modified version of
this salt mix (MPM-m), the pH was adjusted to 7.5 and the
concentrations of NH4Cl and KH2PO4
were reduced to 50 and 1.5 µM, respectively. Both media were amended
with a mix of monomers (5.7 mg of C/liter) (14), and for
plate cultivation, 1% (wt/vol) agar (Difco Laboratories, Detroit,
Mich.) was added. Subsamples (100 µl) of unfiltered seawater were
directly spread on triplicate petri dishes containing either MPM or
MPM-m. Over a period of 37 days the numbers of visible colonies were
determined with a binocular microscope at a ×4 magnification. After 2, 7, 12, 15, 19, 29, and 36 days, all visible colonies were removed from
the plate by excising the entire colony and the underlying agar with a
sterile spatula. One plate containing MPM-m was selected for further
characterization of isolates. The collected strains were subcultured in
liquid medium before replating.
For the enrichment of marine alpha-proteobacteria in liquid cultures,
MPM-m without additional substrates was inoculated with unfiltered or
prefiltered (pore size, 1.2 and 0.45 µm) seawater (1:100 to 1:1,000).
The dilutions were incubated at 16°C in the dark. The enrichments
were continously screened by FISH with the oligonucleotide probe
ALF968, specific for the alpha-proteobacteria (33), over a
period of 9 weeks. If the alpha-proteobacterial abundances in the
enrichments significantly increased (>20% of total counts), aliquots
were plated on solid medium containing the MPM-m salt mix without
additional carbon source. Representatives of all discernible colony
morphotypes were selected from agar plates and subcultured under the
same conditions. Only isolates that hybridized with probe ALF968 were
included in the subsequent analysis.
Phylogenetic analysis.
Bacterial 16S rRNA primers
8f (5'-AGAGTTTGATCMTGGC-3') and 1542r
(5'-AAAGGAGGTGATCCA-3') were used to amplify almost
full-length 16S ribosomal DNAs (rDNAs) from isolates (5)
by PCR (42). Amplified 16S rRNA genes from isolates were
sequenced by Taq cycle sequencing and universal 16S
rRNA-specific primers using an ABI377 (Applied Biosystems, Inc.)
sequencer. Sequence data were analyzed with the ARB software
package (http://www.mikro.biologie.tu-muenchen.de). Phylogenetic trees
were reconstructed using neighbor-joining, maximum-parsimony, and
maximum-likelihood analyses. Only sequences that were at least 90%
complete were used for tree construction. Alignment positions at which
less then 50% of sequences of the entire set of data had the same
residues were excluded from the calculations to prevent uncertain
alignments within highly variable positions of the 16S rDNA, which may
cause mistakes in the tree topology.
Cell counts, FISH, and probe design.
Total picoplankton
counts were determined by epifluorescence microscopy (24).
Isolates were screened by FISH with the oligonucleotide probes EUB338,
targeted to Bacteria (1), ALF968, GAM42a,
targeted to the gamma proteobacteria (31), and CF319a,
targeted to the CF group of the Bacteroidetes
(30). The specific oligonucleotide probes NOR5-730,
NOR5-130, CYT1448, CYT1438, ROS537, KT13-231, KT09a, KT09b, RC1031,
RC1239, ROS7-1029, ERYTH69, and RHIZO218 (Table
1) were designed using the ARB software
package. Probe specificity was evaluated with ARB against the rRNA
database of the Technical University Munich (release 12/98), by the
BLAST queueing system (http://www.ncbi.nlm.nih.gov/blast/blast.cgi), and by FISH to selected strains with base pair mismatches at the probe
target sites. Probes labeled with the cyanine dye CY3 were synthesized
by Interactiva (Ulm, Germany). Stringent hybridization conditions for
the newly designed probes were determined for isolates by varying
concentrations of formamide (34).
Samples from North Sea surface waters were analyzed by FISH with all of
the above probes. Hybridizations, counterstaining with
4,6-diamidino-2-phenylindole (DAPI; 1 µg/ml), mounting, and microscopic evaluations were performed as described previously (16). The fraction of FISH-stained bacteria in at least
1,000 DAPI-stained cells per sample was quantified.
Nucleotide sequence accession numbers.
The 16S rDNA
sequences from isolates generated in this study were deposited in
GenBank under the accession numbers AY007676 to AY007684 and AF305498.
 |
RESULTS |
Colony-forming bacteria obtained by time series.
Over 37 days
of incubation, only 0.25 × 103 ± 0.11 × 103 (mean ± 1 standard deviation) CFU
ml
1 appeared on plates containing the original MPM
medium, while 1.21 × 103 ± 0.01 × 103 CFU ml
1 were obtained on MPM-m plates
(Fig. 1A). Of the isolates that appeared
during the first 2 days of incubation on MPM-m, 41% were affiliated
with the gamma-proteobacteria (14 out of 34), 20% were affiliated with
the CF branch of the Bacteroidetes, and only 9% were
affiliated with alpha-proteobacteria. Within the next 13 days the
number of additional alpha-proteobacteria increased by a factor of 10, whereas the number of additional isolates from the gamma-proteobacteria
and the CF group increased less than three-fold (Fig. 1B). During the
second half of the incubation period the majority of newly retrieved
isolates were affiliated with the alpha-proteobacteria. Altogether
there were 19 colonies that did not grow after reinoculation in liquid
medium ("not transferable" in Fig. 1B). At the end of incubation
the gamma-proteobacteria constituted 29%, members of the CF group
constituted 12%, and the alpha-proteobacteria constituted 33% of the
culture collection (Fig. 1B). The number of alpha-proteobacteria
affiliated with the "marine alpha" lineage (i.e., that hybridized
with probe ROS537) (Fig. 2A) increased
from a single colony during the first 2 days to a total of 11 strains
(9%).

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FIG. 1.
(A) Cumulative abundances of colony-forming bacteria
from coastal North Sea surface waters on artificial seawater medium
(MPM) during 37 days of incubation and on MPM with reduced
concentrations of NH4 and PO4 (MPM-m). (B)
Cumulative percentages of colonies from different phylogenetic groups
on MPM-m. The arrow indicates the time of colony formation of isolate
KT71, affiliated with the gamma-proteobacterial clade NOR5. "not
transferable," isolates that could not be subcultured.
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FIG. 2.
Phylogenetic trees based on comparative 16S rDNA
sequence analysis of selected isolates of alpha-proteobacteria (A),
gamma-proteobacteria (B), and the CF cluster (C). Brackets indicate
specificity of the probes ROS537, NOR5-730, CYT1438, and CYT1448. Scale
bars depict 10% sequence divergence. Names in bold indicate sequences
targeted by newly designed specific probes. The asterisk indicates the
probe that specifically targets the depicted phylotype KT71.
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During the first 2 days of plate incubation, we obtained
well-known alpha-proteobacteria such as
Roseobacter spp., gamma-proteobacteria affiliated with
the genera Pseudoalteromonas, Alteromonas,
Colwellia, and Photobacterium, and members of the CF
cluster from the genera Cytophaga, Polaribacter,
and Flavobacterium. Between days 3 and 11, bacteria from
numerous additional genera were isolated, e.g., Erythromicrobium, Agrobacterium,
Paracoccus, and Sulfitobacter (alpha
proteobacteria); Marinomonas,
Shewanella, Sedimentobacter, and
Alcanivorax (gamma proteobacteria); and
Flexibacter (Bacteroidetes). One isolate (strain
KT71) that was affiliated with a newly defined lineage of the
gamma-proteobacteria (NOR5) (Fig. 2B) appeared only after 12 days of
incubation (Fig. 1). This was also the case for several strains
related to NOR1 (14). 16S rDNA sequence analysis of some
isolates that did not hybridize with the three group-specific
probes (ALF968, GAM42a, and CF319a) revealed that they belonged
to other lineages, such as the actinobacterial genus Microbacterium or the gamma-proteobacterial genus
Colwellia.
During a period of several weeks the liquid enrichment cultures were
regularly screened by FISH with probe ALF968. A total of 77 strains
were isolated from those treatments, consisting of at least 20%
alpha-proteobacteria. Twenty-three strains (30%) positively hybridized
with probe ALF968. For initial phylogenetic analysis, partial 16S rDNA
sequences of these isolates were determined. Sequences fell into eight
distinct groups within the alpha-proteobacteria, and at least one
nearly complete 16S rDNA sequence from each group was obtained (Table
2; Fig. 2A). The most frequent isolates
were related to the genus Erythrobacter (11 out of 23).
Three sequences affiliated with two lineages within the
Roseobacter cluster (Fig. 2A). The phylogenetic affiliation
of representative alpha-proteobacterial isolates from different
lineages, and of other strains that were screened for their in situ
occurrence in environmental samples, is shown in Table 2.
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TABLE 2.
Phylogenetic affiliations of representative
alpha-proteobacterial isolates and of isolates from other groups
that were screened for their in situ abundances by FISH
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Seasonal development of the plankton community.
The annual
temperature of surface waters of the German Bight in 1998 ranged
between 3.2 and 17.9°C. It increased between April and August and
declined thereafter (Fig. 3A). Between
April and October, several short-lived maxima of
phytoplankton biomass were observed (Fig. 3A)
(www.pangaea.de/projects/). Interestingly, the spring phytoplankton
bloom typically observed in the German Bight during April
(40) was comparatively low. Bacterial cell densities
remained more or less constant until late April (1.2 × 105 ml
1) (Fig. 3B), and cell numbers
increased more than 10-fold over the next 3 months. Several peaks of
total abundances were clearly separated by periods with lower cell
densities. Bacterial numbers decreased between July and September and
remained low thereafter.

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FIG. 3.
(A) Seasonal fluctuations of water temperature and of
phytoplankton biomass in German Bight surface waters in 1998. (B)
Seasonal fluctuations of total picoplankton abundances and of FISH
detection rates by the bacterial probe EUB338. Phytoplankton data are
from www.pangaea.de/projects/.
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Detection rates with probe EUB338, targeted to most
Bacteria, roughly followed the patterns of total abundances
(Fig. 3B) (Spearman rank correlation; n = 26, R = 0.7, P < 0.001). From January to March and from October to
December, usually <50% of all DAPI-stained objects were detected by
FISH. Between 52 and 92% of total picoplankton counts were
visualized by FISH from April to September (mean, 66% of DAPI
counts). The large majority of FISH-detectable bacteria (mean, 93%)
could be identified as members of the CF group or of the alpha- and
gamma-proteobacteria by the oligonucleotide probes CF319a,
ALF968, and GAM42a. On average, 37% of FISH-detectable cells were
affiliated with the CF group, 29% were affiliated with the
alpha-proteobacteria, and 19% were affiliated with the
gamma-proteobacteria (i.e., 21, 15, and 10% of DAPI counts,
respectively). On several occasions, the sum of the group-specific
probes even exceeded the total counts with probe EUB338, but with one
exception (week 31) this always ranged within the expected cumulative
counting error.
Between April and July, there were several peaks of abundance of
members of the CF group, with an annual maximum of 1.2 × 106 cells ml
1 in July (Fig.
4A). During this period they constituted
up to 55% of total picoplankton counts (i.e., DAPI; mean, 35%) and up to 76% of FISH-detectable bacteria (mean, 51%). Bacteria affiliated with the Cytophaga marinoflava-Cytophaga latercula
lineage (Fig. 2C and 4B) were detectable between April and September
and formed a constant fraction of 6% ± 2% of the DAPI count. This
corresponded to 0.75 × 105 cells ml
1 in
May and 1.1 × 105 cells ml
1 in July and
August.

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FIG. 4.
(A) Seasonal fluctuations of alpha-proteobacteria
(ALF968) and gamma-proteobacteria (GAM42a) and of members of the
CF lineage (CF319a) detected by FISH in German Bight surface waters in
1998. (B) Abundances of Cytophaga spp. (CYT1448), members of
the Roseobacter lineage (ROS537), and members of the NOR5
cluster (NOR5-730). Note the different y-axis scales.
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The relative abundances of bacteria detected by ALF968 ranged from 12 to 33% of total DAPI counts between April and September. Alpha-proteobacteria formed local maxima in mid-May and July (Fig. 4A).
In contrast to the CF group, the abundances of alpha-proteobacteria were not higher in July than in May. Roseobacter spp. and
other members of the "marine alpha" group (19), as
detected by probe ROS537 (Fig. 2A), formed the majority of the alpha
proteobacteria between April and September (mean, 67%; range, 44 to
100%, corresponding to 12% of DAPI counts) (Fig. 4B). During that
period, the counts with a published probe for the
Roseobacter group, MALF1 (19), were
significantly lower than with probe ROS537 (mean, 69% of detection
with ROS537; Wilcoxon matched-pair test, n = 9, P < 0.05). Culturable representatives from various phylogenetic
lineages within the Roseobacter cluster (isolates KT0202a,
KT0917, KT1117, and JP7.1) (Table 2) and from other
alpha-proteobacterial lineages (isolates JP13.1 and JP66.1) (Table 2)
never constituted more than 1% of DAPI counts in German Bight surface
waters, as determined by FISH with specific probes (Table 1).
A first maximum of bacteria hybridizing with probe GAM42a was observed
at the end of June (0.2 × 106 cells
ml
1, 20% of DAPI) (Fig. 4A). Between April and
September, the relative abundances of gamma-proteobacteria fluctuated
between 10 and >20% of DAPI counts. Bacteria detected by GAM42a had
densities similar to those of the alpha-proteobacteria during July and
August (0.4 × 106 cells ml
1). For a
period of approximately 3 months (May to August), members of the NOR5
cluster, as detected by probe NOR5-730, formed a large fraction (up to
61%) of gamma-proteobacteria. Two abundance maxima of NOR5 could be
discerned, in early June and late July (Fig. 4B), when members of this
group constituted 6 to 8% of total picoplankton (DAPI) counts.
 |
DISCUSSION |
Abundant culturable gamma-proteobacteria affiliated with NOR5.
So far, strain KT71 is the only isolated representative of a
probably cosmopolitan gamma-proteobacterial lineage (NOR5) (Fig. 2B).
Other members of this cluster are known exclusively from cloned 16S
rDNA sequences, which have been amplified from the coastal North Sea,
the Mediterranean Sea, and the Atlantic Ocean (14, 41,
43). Almost all bacteria affiliated with NOR5 in coastal North
Sea surface waters (Fig. 4B) were also detected by a second probe,
NOR5-130 (Table 2), which was targeted exclusively to strain KT71.
Thus, within the limits of our rRNA-based identification, KT71 is among
the first heterotrophic bacterial isolates that can be detected in the
marine picoplankton in high abundances by direct microscopic counts.
Bacteria related to KT71 formed populations of up to 1.5 × 105 cells ml
1 in the surface waters of the
German Bight (8% of DAPI counts) (Fig. 4B). They constituted a major
fraction of FISH-detectable gamma proteobacteria in the picoplankton
during May and June (33%) and July and August 1998 (66%). At present
we do not know whether NOR5 also plays a role in offshore microbial
communities or in deeper water layers. The two observed abundance
maxima coincided with biomass peaks of a single diatom species,
Lauderia sp. (23). However, it would be too
early to speculate about potential relationships between the two
populations, since our environmental data are limited to a 1-year
period and our sampling frequency probably did not provide sufficient
resolution for an adequate description of plankton bloom situations
(21).
Strain KT71 could be isolated on our mix of monomers and amino acids
only after substantially reduction of the originally reported
concentrations of N and P, and the strain formed a visible colony after
12 days of incubation. Eilers et al. (14) have shown that
the probability of obtaining additional diversity of gamma-proteobacteria from the German Bight by plating on MPM medium was
marginal, irrespective of a variety of different carbon sources. Therefore, the successful isolation of a member from the previously unculturable NOR5 lineage was most likely the consequence of our modifications of the original technique.
In a previous study, we discovered that frequently isolated
opportunistic gamma-proteobacteria affiliated with
Alteromonas and Vibrio were quickly enriched in
filtrates of coastal North Sea surface water (13). During
earlier cultivation attempts (14), we furthermore noticed
a rapid dispersal of some isolates over the agar surface, which
resulted in a fusion of different colonies after 2 to 3 days of plate
incubation. These observations inspired us to continuously remove newly
appearing colonies from the petri dishes and, thus, to extend the
potential period of colony formation to several weeks (Fig. 1A).
The isolation of KT71 after 12 days of incubation suggests that some
common pelagic bacteria may grow on agar plates only after an extended
lag phase. However, significant increases in the total number of
isolates, and in their phylogenetic diversity, were observed only if
the inorganic N and P concentrations in the medium were reduced to
match the maximal ambient levels of coastal North Sea waters in 1998 (1.3 µmol of P liter
1, 29 µmol of N
liter
1) (Fig. 1A). Cultivation of marine bacterioplankton
on common complex media (2, 38) might, therefore, prevent
the growth of autochthonous pelagic species because of excessively high
nutrient concentrations. Preliminary observations indicate that strain KT71 does not grow on media containing 0.2% peptone and 0.1% yeast extract but can be maintained in liquid culture on our modified synthetic medium (H. Eilers, unpublished results).
Cultured members of the Roseobacter lineage are rare in
the environment.
During recent years, the so-called "marine
alpha" cluster (19), a phylogenetic lineage harboring
genera such as Roseobacter, Sulfitobacter, and
Sagittula (Fig. 2A), has been shown to contribute significantly to coastal picoplankton (19, 21).
Concomitantly, a number of isolates from this cluster could be readily
obtained on substrates such as lignin or low-nutrient complex media
(19, 22), and this has been regarded as evidence for the
culturability of some abundant pelagic marine bacteria
(19). Strains from the Roseobacter lineage
serve as model organisms for the degradation abilities of
"ecologically relevant" bacteria (4) and for the study
of microbial sulfur cycling in the pelagic zone (18). This
group, furthermore, plays a key role in controlling the turnover of the
algal osmolyte dimethylsulfoniopropionate (50), and
bacteria from the Roseobacter cluster form prominent
populations during coccolithophore blooms (21, 50).
Altogether we obtained 14 strains that were affiliated with this
phylogenetic group. A reduction of inorganic N and P in the medium, and
an extended sampling of the agar plates, appeared to positively select
for such bacteria. More than 10% of all isolates that formed colonies
between day 2 and day 37 of plate incubation (10 of 87) were members of
the Roseobacter lineage, as determined by group-specific
FISH. In contrast, <6% of strains (8 of 142) were affiliated with
this group in a previous collection of isolates that was established on
the original MPM medium, and without plate resampling
(14). Some strains from the marine alpha cluster were also
isolated by plating on MPM-m medium after liquid enrichment on
MPM-m without additional substrates. However, the latter approach was
not particularly selective for this lineage but rather yielded numerous strains that were affiliated with
Erythrobacter (Fig. 2A).
We designed several probes targeting different groups of isolates
from the Roseobacter cluster (Table 1) and a new
group-specific probe, ROS537, with more complete coverage than a
previously described probe (19). Cells detected by
ROS537 (Fig. 4B) constituted a prominent fraction of all
alpha-proteobacteria in German Bight surface waters (annual mean, 49%,
corresponding to 8% of total DAPI counts). Yet the specific probes
revealed that bacteria related to our isolates (Table 2; Fig. 2A) did
not form large populations in the picoplankton, even when the FISH
detection rates were generally high. Interestingly, the majority of
Roseobacter cells in samples from July to October 1998 (mean, 60%) could be visualized by a recently described probe, RSB67
(50), that is targeted to the 16S rDNA sequence of
uncultured bacteria from this lineage (clone ZD0207) (Fig. 2A).
Bacteria detected by this probe constituted the majority of the DNA-
and protein-rich subpopulation in a picoplankton community during an
algal bloom (50) in the northern part of the North Sea.
We present evidence that several culturable members of the marine
Roseobacter group are rare in the environment, as has been documented for the marine gamma-proteobacteria (13). The
Roseobacter lineage is physiologically rather versatile,
including even phototrophic members (29). All previously
described species are phylogenetically more closely related to
our strains than to the uncultured phylotype ZD0207 (Fig. 2A).
Culturable members of the Roseobacter lineage might,
therefore, in general not be representative of the species that are
abundant in coastal waters (Fig. 4B) (19) or during phytoplankton blooms (21, 50). Some readily culturable
marine gamma-proteobacteria (Pseudoalteromonas and
Vibrio) are known to be associated with animal and plant
surfaces (25, 32). We speculate that the culturable
species of the Roseobacter group may preferentially inhabit
the surfaces of particular marine eucaryotes, e.g., algae
(39). This could account for their superior ability to
form colonies on solid media at reduced nutrient concentrations.
A lineage of culturable marine Cytophaga spp.
During an earlier study, only a few strains isolated on MPM medium were
affiliated with the CF cluster of the Bacteroidetes (14). However, this group formed an important component of
the surface picoplankton in the German Bight in 1998 and occasionally even numerically dominated the total bacterial community (Fig. 4A).
High relative abundances of members of the CF group have also been
found in the surface plankton of the coastal Atlantic Ocean during
summer (8), as well as in Antarctic waters, co-occurring with a Phaeocystis bloom (45). Marine CF group
members are apparently not limited to the attached bacterial fraction
(10) but are common in the water column.
We therefore designed probes targeted to isolates from the culture
collection of Eilers et al. (14) that were affiliated with
the C. marinoflava-C. latercula lineage (Fig. 2C). This
"marine cytophaga" cluster formed a small but constant fraction of
the picoplankton during spring and summer. Between April and September, 5% of all DAPI-stained objects (19% of CF) were detected by the specific probes on average (Fig. 4B). Little is known about the physiology of the CF group members that are common in the aquatic environment. Preliminary results indicate that isolated strains from
this C. marinoflava-C. latercula cluster do not grow on
hydrolyzed chitin (Eilers, unpublished), which is preferentially
consumed by some marine CF group members (9). Further
studies are required to adequately cover the phylogenetic diversity
within the CF lineage, and new isolation strategies that are more
selective for abundant pelagic members of the CF group need to be developed.
Study of seasonal population changes by FISH.
We did not
attempt an exhaustive analysis of the microbial community composition
in German Bight surface picoplankton, and important groups such as
SAR86, SAR11 (21), and the marine archaea have not been
studied (27). Our investigation focused on the dynamics of
a few lineages that were also targets of isolation attempts or from
which isolates had been obtained earlier (Fig. 2) (14).
Although a majority of the picoplankton community could be detected by
FISH between April and September, at elevated water temperature and
phytoplankton biomass (Fig. 1A), detection rates were low during
winter. For the latter period it is thus impossible to evaluate whether
and to what extent the per-cell activities of individual groups
influenced our abundance estimates. Other microscopic approaches, e.g.,
FISH with polyribonucleotide probes (27), might help
to overcome this limitation in the future.
Nevertheless, even a partial elucidation of the seasonal dynamics of
picoplankton community composition provided us with targets for a
directed screening and led to the investigation of isolates affiliated
with Roseobacter spp. and Cytophaga spp. (Fig. 2A
and C). The time series over the whole productive season (Fig. 4B) allowed a more integrated evaluation of the presence or absence of a
particular phylotype in the pelagic zone than a single sampling. Bacteria isolated at any particular season could be extremely rare at
that time point but could still form substantial populations during
other periods of the year. Our biweekly sampling scheme might actually
be too coarse to detect all abundance maxima of individual phylotypes,
since, e.g., phytoplankton blooms in the North Sea occur on a scale of
weeks (Fig. 1A). It is possible that some of the isolates affiliated
with the alpha-proteobacteria formed similarly short-lived peaks in the
German Bight. However, the probability of accidently missing all
indication of six different populations (Fig. 2A) by our sampling is
marginal. Nevertheless, investigations of single phylotypes at higher
temporal resolution will be necessary to elucidate the actual dynamics
and stability of bacterial populations in the plankton.
Conclusions.
Our results only partially support a hypothesis
by Pinhassi et al. (38) and Gonzalez and Moran
(19), who proposed that typical members of the marine
picoplankton can form colonies on substrate-amended agar plates. Both
the original and the modified synthetic medium yielded a few isolates
that were closely related to abundant bacteria from coastal North Sea
surface waters. However, most isolates were "laboratory weeds" with
good culturability but low in situ abundance, e.g., all strains from
the Roseobacter lineage. There is an obvious discrepancy
between the rapid advancement of cultivation-independent approaches for
the analysis of marine pelagic bacteria and the simplicity of typical
isolation strategies, which have changed little during the last 50 years. In this study, the successful isolation of abundant bacteria
from North Sea surface waters (Fig. 4B) was guided by information about
bacterial in situ growth conditions and by data about microbial
community composition. With this knowledge in hand, it is possible to
isolate truly pelagic bacteria and to detect important members of the
picoplankton hidden in culture collections.
 |
ACKNOWLEDGMENTS |
We thank Karl-Walter Klings for help during sampling and Birgit
Rattunde for assistance in maintaining the culture collection. The BAH
Helgoland is acknowledged for providing guest research facilities.
This study was supported by the Max Planck Society.
 |
FOOTNOTES |
*
Corresponding author. Mailing address:
Max-Planck-Institut für Marine Mikrobiologie, Celsiusstrasse 1, D-28359 Bremen, Germany. Phone: 49 421 2028 940. Fax: 49 421 2028 580. E-mail: jperntha{at}mpi-bremen.de.
 |
REFERENCES |
| 1.
|
Amann, R. I.,
L. Krumholz, and D. A. Stahl.
1990.
Fluorescent-oligonucleotide probing of whole cells for determinative, phylogenetic, and environmental studies in microbiology.
J. Bacteriol.
172:762-770[Abstract/Free Full Text].
|
| 2.
|
Bernard, L.,
H. Schäfer,
F. Joux,
C. Courties, and G. Muyzer.
2000.
Genetic diversity of total, active and culturable marine bacteria in coastal seawater.
Aquat. Microb. Ecol.
23:1-11.
|
| 3.
|
Brosius, J.,
T. J. Dull,
D. D. Sleeter, and H. F. Noller.
1981.
Gene organization and primary structure of a ribosomal RNA operon from Escherichia coli.
J. Mol. Biol.
148:107-127[CrossRef][Medline].
|
| 4.
|
Buchan, A.,
L. S. Collier,
E. L. Neidle, and M. A. Moran.
2000.
Key aromatic-ring-cleaving enzyme, protocatechuate 3,4-dioxygenase, in the ecologically important marine Roseobacter lineage.
Appl. Environ. Microbiol.
66:4662-4672[Abstract/Free Full Text].
|
| 5.
|
Buchholz-Cleven, B.,
B. Rattunde, and K. Straub.
1997.
Screening for genetic diversity of isolates of anaerobic Fe(II)-oxidizing bacteria using DGGE and whole-cell hybridization.
Syst. Appl. Microbiol.
20:301-309.
|
| 6.
|
Button, D. K.,
B. R. Robertson,
P. W. Lepp, and T. M. Schmidt.
1998.
A small, dilute-cytoplasm, high-affinity, novel bacterium isolated by extinction culture and having kinetic constants compatible with growth at ambient concentrations of dissolved nutrients in seawater.
Appl. Environ. Microbiol.
64:4467-4476[Abstract/Free Full Text].
|
| 7.
|
Button, D. K.,
F. Schut,
P. Quang,
R. Martin, and B. Robertson.
1993.
Viability and isolation of marine bacteria by dilution culture: theory, procedures, and initial results.
Appl. Environ. Microbiol.
59:881-891[Abstract/Free Full Text].
|
| 8.
|
Cottrell, M. T., and D. L. Kirchman.
2000.
Community composition of marine bacterioplankton determined by 16S rRNA gene clone libraries and fluorescence in situ hybridization.
Appl. Environ. Microbiol.
66:5116-5122[Abstract/Free Full Text].
|
| 9.
|
Cottrell, M. T., and D. L. Kirchman.
2000.
Natural assemblages of marine proteobacteria and members of the Cytophaga-Flavobacter cluster consuming low- and high-molecular-weight dissolved organic matter.
Appl. Environ. Microbiol.
66:1692-1697[Abstract/Free Full Text].
|
| 10.
|
DeLong, E. F.,
D. G. Franks, and A. L. Alldredge.
1993.
Phylogenetic diversity of aggregate-attached vs. free-living marine bacterial assemblages.
Limnol. Oceanogr.
38:924-934.
|
| 11.
|
DeLong, E. F.,
L. T. Taylor,
T. L. Marsh, and C. M. Preston.
1999.
Visualization and enumeration of marine planktonic archaea and bacteria by using polyribonucleotide probes and fluorescent in situ hybridization.
Appl. Environ. Microbiol.
65:5554-5563[Abstract/Free Full Text].
|
| 12.
|
Eberl, L.,
S. Molin, and M. Givskov.
1999.
Surface motility of Serratia liquefaciens MG1.
J. Bacteriol.
181:1703-1712[Free Full Text].
|
| 13.
|
Eilers, H.,
J. Pernthaler, and R. Amann.
2000.
Succession of pelagic marine bacteria during enrichment: a close look at cultivation-induced shifts.
Appl. Environ. Microbiol.
66:4634-4640[Abstract/Free Full Text].
|
| 14.
|
Eilers, H.,
J. Pernthaler,
F. O. Glöckner, and R. Amann.
2000.
Culturability and in situ abundance of pelagic bacteria from the North Sea.
Appl. Environ. Microbiol.
66:3044-3051[Abstract/Free Full Text].
|
| 15.
|
Ferguson, R. L.,
E. N. Buckley, and A. V. Palumbo.
1984.
Response of marine bacterioplankton to differential filtration and confinement.
Appl. Environ. Microbiol.
47:49-55[Abstract/Free Full Text].
|
| 16.
|
Glöckner, F. O.,
R. Amann,
A. Alfreider,
J. Pernthaler,
R. Psenner,
K. Trebeslus, and K.-H. Schleifer.
1996.
An in situ hybridization protocol for detection and identification of planktonic bacteria.
Syst. Appl. Microbiol.
19:403-406.
|
| 17.
|
Glöckner, F. O.,
B. M. Fuchs, and R. Amann.
1999.
Bacterioplankton compositions of lakes and oceans: a first comparison based on fluorescence in situ hybridization.
Appl. Environ. Microbiol.
65:3721-3726[Abstract/Free Full Text].
|
| 18.
|
Gonzalez, J. M.,
R. P. Kiene, and M. A. Moran.
1999.
Transformation of sulfur compounds by an abundant lineage of marine bacteria in the -subclass of the class Proteobacteria.
Appl. Environ. Microbiol.
65:3810-3819[Abstract/Free Full Text].
|
| 19.
|
Gonzalez, J. M., and M. A. Moran.
1997.
Numerical dominance of a group of marine bacteria in the -subclass of the class Proteobacteria in coastal seawater.
Appl. Environ. Microbiol.
63:4237-4242[Abstract].
|
| 20.
|
González, J. M., and M. A. Moran.
1997.
Numerical dominance of a group of marine bacteria in the -subclass of the class Proteobacteria in coastal seawater.
Appl. Environ. Microbiol.
63:4237-4242.
|
| 21.
|
Gonzalez, J. M.,
R. Simo,
R. Massana,
J. S. Covert,
E. O. Casamayor,
C. Pedros-Alio, and M. A. Moran.
2000.
Bacterial community structure associated with a dimethylsulfoniopropionate-producing North Atlantic algal bloom.
Appl. Environ. Microbiol.
66:4237-4246[Abstract/Free Full Text].
|
| 22.
|
Gonzalez, J. M.,
W. B. Whitman,
R. E. Hodson, and M. A. Moran.
1996.
Identifying numerically abundant culturable bacteria from complex communities: an example from a lignin enrichment culture.
Appl. Environ. Microbiol.
62:4433-4440[Abstract].
|
| 23.
|
Hagmeier, E.
1998.
Nordseebericht 1998:
In
Phytoplankton der Helgoland-Reede. Landesamt für Natur und Umwelt des Landes Schleswig-Holstein Flintbek, Germany.
|
| 24.
|
Hobbie, J. E.,
R. J. Daley, and S. Jasper.
1977.
Use of Nuclepore filters for counting bacteria by fluorescence microscopy.
Appl. Environ. Microbiol.
33:1225-1228[Abstract/Free Full Text].
|
| 25.
|
Holmström, C., and S. Kjelleberg.
1999.
Marine Pseudoalteromonas species are associated with higher organisms and produce biologically active extracellular agents.
FEMS Microbiol. Ecol.
30:285-293[Medline].
|
| 26.
|
Jannasch, H.
1967.
Enrichments of aquatic bacteria in continuous culture.
Arch. Mikrobiol.
59:165-173[CrossRef][Medline].
|
| 27.
|
Karner, M.,
E. F. DeLong, and D. M. Karl.
2001.
Archaeal dominance in the mesopelagic zone of the Pacific Ocean.
Nature
409:507-509[CrossRef][Medline].
|
| 28.
|
Karner, M., and J. A. Fuhrman.
1997.
Determination of active marine bacterioplankton: a comparison of universal 16S rRNA probes, autoradiography, and nucleoid staining.
Appl. Environ. Microbiol.
63:1208-1213[Abstract].
|
| 29.
|
Labrenz, M.,
M. D. Collins,
P. A. Lawson,
B. J. Tindall,
P. Schumann, and P. Hirsch.
1999.
Roseovarius tolerans gen. nov., sp. nov., a budding bacterium with variable bacteriochlorophyll a production from hypersaline Ekho Lake.
Int. J. Syst. Bacteriol.
49:137-147[Abstract/Free Full Text].
|
| 30.
|
Manz, W.,
R. Amann,
W. Ludwig,
M. Vancanneyt, and K.-H. Schleifer.
1996.
Application of a suite of 16S rRNA-specific oligonucleotide probes designed to investigate bacteria of the phylum Cytophaga-Flavobacter-Bacteroides in the natural environment.
Microbiology
142:1097-1106[Abstract].
|
| 31.
|
Manz, W.,
R. Amann,
W. Ludwig,
M. Wagner, and K.-H. Schleifer.
1992.
Phylogenetic oligodeoxynucleotide probes for the major subclasses of Proteobacteria: problems and solutions.
Syst. Appl. Microbiol.
15:593-600.
|
| 32.
|
Montanari, M. P.,
C. Pruzzo,
L. Pane, and R. R. Colwell.
1999.
Vibrios associated with plankton in a coastal zone of the Adriatic Sea (Italy).
FEMS Microbiol. Ecol.
29:241-247[CrossRef].
|
| 33.
|
Neef, A.
1997.
Ph.D. thesis.
Technical University, Munich, Germany.
|
| 34.
|
Neef, A.,
A. Zaglauer,
H. Meier,
R. Amann,
H. Lemmer, and K. H. Schleifer.
1996.
Population analysis in a denitrifying sand filter: conventional and in situ identification of Paracoccus spp. in methanol-fed biofilms.
Appl. Environ. Microbiol.
62:4329-4339[Abstract].
|
| 35.
|
Ouverney, C. C., and J. A. Fuhrman.
2000.
Marine planktonic Archaea take up amino acids.
Appl. Environ. Microbiol.
66:4829-4833[Abstract/Free Full Text].
|
| 36.
|
Pernthaler, J.,
F. O. Glöckner,
S. Unterholzner,
A. Alfreider,
R. Psenner, and R. Amann.
1998.
Seasonal community and population dynamics of pelagic Bacteria and Archaea in a high mountain lake.
Appl. Environ. Microbiol.
64:4299-4306[Abstract/Free Full Text].
|
| 37.
|
Pinhassi, J., and A. Hagström.
2000.
Seasonal succession in marine bacterioplankton.
Aquat. Microb. Ecol.
21:245-256[CrossRef].
|
| 38.
|
Pinhassi, J.,
U. L. Zweifel, and A. Hagström.
1997.
Dominant marine bacterioplankton species found among colony-forming bacteria.
Appl. Environ. Microbiol.
63:3359-3366[Abstract].
|
| 39.
|
Prokic, I.,
F. Brummer,
T. Brigge,
H. D. Gortz,
G. Gerdts,
C. Schutt,
M. Elbrachter, and W. E. G. Muller.
1998.
Bacteria of the genus Roseobacter associated with the toxic dinoflagellate Prorocentrum lima.
Protist
149:347-357.
|
| 40.
|
Radach, G.,
J. Berg, and E. Hagmeier.
1990.
Long-term changes of the annual cycles of meteorological, hydrographic, nutrient, and phytoplankton times series at Helgoland and at LV Elbe 1 in the German Bight.
Continental Shelf Res.
10:305-328[CrossRef].
|
| 41.
|
Rappé, M. S.,
P. F. Kemp, and S. J. Giovannoni.
1997.
Phylogenetic diversity of marine coastal picoplankton 16S rRNA genes cloned from the continental shelf off Cape Hatteras, North Carolina.
Limnol. Oceanogr.
42:811-826.
|
| 42.
|
Saiki, R. K.,
D. H. Gelfand,
S. Stoffel,
S. J. Scharf,
R. Higuchi,
G. T. Horn,
K. B. Mullins, and H. A. Erlich.
1988.
Primer-directed enzymatic amplification of DNA with a thermostable DNA polymerase.
Science
239:487-491[Abstract/Free Full Text].
|
| 43.
|
Schäfer, H.,
L. Bernard,
C. Courties,
P. Lebaron,
P. Servais,
R. Pukall,
E. Stackebrandt,
M. Troussellier,
T. Guindulain,
J. Vives-Rego, and G. Muyzer.
2001.
Microbial community dynamics in Mediterranean nutrient-enriched seawater.
FEMS Microbiol. Ecol.
34:243-253[Medline].
|
| 44.
|
Schut, F.,
E. J. De Vries,
J. C. Gottschal,
B. R. Robertson,
W. Harder,
R. A. Prins, and D. K. Button.
1993.
Isolation of typical marine bacteria by dilution culture growth maintenance and characteristics of isolates under laboratory conditions.
Appl. Environ. Microbiol.
59:2150-2160[Abstract/Free Full Text].
|
| 45.
|
Simon, M.,
F. O. Glöckner, and R. Amann.
1999.
Different community structure and temperature optima of heterotrophic picoplankton in various regions of the Southern Ocean.
Aquat. Microb. Ecol.
18:275-284.
|
| 46.
|
Straskrabová, V.
1983.
The effect of substrate shock on populations of starving aquatic bacteria.
J. Appl. Bacteriol.
54:217-224.
|
| 47.
|
Suzuki, M. T.,
L. T. Taylor, and E. F. DeLong.
2000.
Quantitative analysis of small-subunit rRNA genes in mixed microbial populations via 5'-nuclease assays.
Appl. Environ. Microbiol.
66:4605-4614[Abstract/Free Full Text].
|
| 48.
|
Thingstad, T. F., and R. Lignell.
1997.
Theoretical models for the control of bacterial growth rate, abundance, diversity and carbon demand.
Aquat. Microb. Ecol.
13:19-27[CrossRef].
|
| 49.
|
ZoBell, C. E.
1946.
Marine microbiology. A monograph on hydrobacteriology.
Chronica Botanica Company, Waltham, Mass.
|
| 50.
|
Zubkov, M. V.,
B. M. Fuchs,
S. D. Archer,
R. P. Kiene,
R. Amann, and P. A. Burkill.
2001.
Linking the composition of bacterioplankton to rapid turnover of dissolved dimethylsulfoniopropionate in an algal bloom in the North Sea.
Environ. Microbiol.
3:304-311[CrossRef][Medline].
|
Applied and Environmental Microbiology, November 2001, p. 5134-5142, Vol. 67, No. 11
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.11.5134-5142.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
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Beardsley, C., Pernthaler, J., Wosniok, W., Amann, R.
(2003). Are Readily Culturable Bacteria in Coastal North Sea Waters Suppressed by Selective Grazing Mortality?. Appl. Environ. Microbiol.
69: 2624-2630
[Abstract]
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Pernthaler, J., Pernthaler, A., Amann, R.
(2003). Automated Enumeration of Groups of Marine Picoplankton after Fluorescence In Situ Hybridization. Appl. Environ. Microbiol.
69: 2631-2637
[Abstract]
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Sekar, R., Pernthaler, A., Pernthaler, J., Warnecke, F., Posch, T., Amann, R.
(2003). An Improved Protocol for Quantification of Freshwater Actinobacteria by Fluorescence In Situ Hybridization. Appl. Environ. Microbiol.
69: 2928-2935
[Abstract]
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Peplies, J., Glockner, F. O., Amann, R.
(2003). Optimization Strategies for DNA Microarray-Based Detection of Bacteria with 16S rRNA-Targeting Oligonucleotide Probes. Appl. Environ. Microbiol.
69: 1397-1407
[Abstract]
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Pernthaler, A., Pernthaler, J., Schattenhofer, M., Amann, R.
(2002). Identification of DNA-Synthesizing Bacterial Cells in Coastal North Sea Plankton. Appl. Environ. Microbiol.
68: 5728-5736
[Abstract]
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Pernthaler, A., Pernthaler, J., Amann, R.
(2002). Fluorescence In Situ Hybridization and Catalyzed Reporter Deposition for the Identification of Marine Bacteria. Appl. Environ. Microbiol.
68: 3094-3101
[Abstract]
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Pernthaler, A., Preston, C. M., Pernthaler, J., DeLong, E. F., Amann, R.
(2002). Comparison of Fluorescently Labeled Oligonucleotide and Polynucleotide Probes for the Detection of Pelagic Marine Bacteria and Archaea. Appl. Environ. Microbiol.
68: 661-667
[Abstract]
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