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Applied and Environmental Microbiology, September 1999, p. 3976-3981, Vol. 65, No. 9
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Phylogenetic Affiliation and Quantification of
Psychrophilic Sulfate-Reducing Isolates in Marine Arctic
Sediments
Kerstin
Sahm,1,*
Christian
Knoblauch,2 and
Rudolf
Amann1
Molecular Ecology
Group1 and Biogeochemistry
Group,2 Max-Planck-Institute for Marine
Microbiology, D-28359 Bremen, Germany
Received 2 April 1999/Accepted 2 July 1999
 |
ABSTRACT |
Thirteen psychrophilic sulfate-reducing isolates from two
permanently cold fjords of the Arctic island Spitsbergen (Hornsund and
Storfjord) were phylogenetically analyzed. They all belonged to the
subclass of Proteobacteria and were widely distributed within this group, indicating that psychrophily is a polyphyletic property. A new 16S rRNA-directed oligonucleotide probe was designed against the largest coherent cluster of these isolates. The new probe,
as well as a set of available probes, was applied in rRNA slot blot
hybridization to investigate the composition of the sulfate-reducing
bacterial community in the sediments. rRNA related to the new cluster
of incompletely oxidizing, psychrophilic isolates made up 1.4 to 20.9%
of eubacterial rRNA at Storfjord and 0.6 to 3.5% of eubacterial rRNA
at Hornsund. This group was the second-most-abundant group of sulfate
reducers at these sites. Denaturing gradient gel electrophoresis and
hybridization analysis showed bands identical to those produced by our
isolates. The data indicate that the psychrophilic isolates are
quantitatively important in Svalbard sediments.
 |
INTRODUCTION |
Low environmental temperatures
characterize the habitat of many prokaryotes living in marine
sediments, since 90% of the sea floor has a temperature of less than
4°C (15). While prokaryotic activity is commonly found to
be lower during cold seasons in temperate environments (for a review,
see reference 23), the current data suggest that in
permanently cold habitats bacterial activity is comparable to that in
temperate environments at the respective ambient temperature (2,
9, 23, 27). Arnosti et al. (2) determined the
temperature dependence of microbial degradation of organic matter and
showed that carbon turnover in the cold Arctic is not intrinsically
slower than in temperate environments. Also, Sagemann et al.
(27) and Glud et al. (9) found rates of sulfate
reduction and benthic carbon mineralization in Arctic sediments to be
comparable to those in temperate or even tropical sediments. Optimal
temperatures for polysaccharide hydrolysis, oxygen consumption
(2), and sulfate reduction (27) in permanently
cold sediments were significantly higher than the ambient temperature;
however, the relative activity at a low in situ temperature compared to
optimum activity was generally higher than in samples from temperate
habitats. These observations indicate that the bacterial community in
these Arctic sediments is adapted to cold temperature. However, little
is known about the diversity and composition of prokaryotic communities
in cold marine sediments; only a few cold-adapted psychrophilic
isolates from these environments have been studied so far (for a
review, see reference 26). In addition, few
cultivation-independent studies have been conducted in these habitats
(28).
The aims of our project, conducted in the context of the
above-mentioned studies, were to characterize the sulfate-reducing bacterial community of permanently cold habitats and to quantify the
abundance of psychrophilic sulfate reducers. We chose two sites, off
the coast of Spitsbergen (Hornsund and Storfjord), which are never
exposed to temperatures higher than 3°C. We concentrated on
sulfate-reducing prokaryotes because sulfate reduction is a major
process of carbon mineralization in marine sediments (11). A
set of probes is available for the main phylogenetic groups of
gram-negative mesophilic sulfate reducers (7), and the
different phylogenetic groups can be defined by distinct physiological
features (35, 36). In a related study, most probable number
(MPN) counts were determined and psychrophilic sulfate reducers were
isolated to enumerate and identify the sulfate-reducing bacteria (SRB) (12). A new oligonucleotide probe was designed to target the largest cluster of these isolates. This newly developed probe, along
with an established set of probes, was applied to quantify sulfate
reducer rRNA in the sediment. The presence of the isolates was further
evaluated by denaturing gradient gel electrophoresis (DGGE) analysis.
The results of this study will be discussed in relation to data from a
16S ribosomal DNA (rDNA) clone library presented in an accompanying
paper (22).
 |
MATERIALS AND METHODS |
Study site and sampling procedure.
Our study was conducted
as part of a research cruise in the Arctic Sea from Tromsø (northern
Norway) to Spitsbergen (Arctic Ocean) in September and October of 1995. Sediments from two different stations (Hornsund [76°58.2'N,
15°34.5'E] and Storfjord [77°33.0'N, 19°05.5'E]) were
investigated. In situ temperatures and depths were 2.6°C and 155 m for Hornsund and
1.7°C and 175 m for Storfjord. Sediment
samples were collected with a multicorer. Samples for MPN dilutions
(12) and molecular analysis were taken from the same core.
The individual subcores (our replicates A and B) derived from two
different multicorer cores. The sediments were anoxic below a depth of
approximately 8 mm (9). Five distinct vertical horizons of 2 to 3 cm in thickness were sectioned from the upper 30 cm of each core.
The sediment of each section was carefully homogenized, and subsamples
of 1 or 2 cm3 were immediately frozen in liquid
N2.
DNA extraction and amplification of 16S rDNA.
After three
cycles of freezing and thawing, DNAs were extracted directly by the
method of Zhou et al. (38), which is based on lysis with a
high-salt extraction buffer and extended heating in the presence of
sodium dodecyl sulfate and hexadecyltrimethylammonium bromide. Lysis
efficiency was checked by DAPI (4',6-diamidino-2-phenylindole) staining. In general, at least 90 to 96% of the cells were lysed. The
DNA could be used for PCR without further purification. Primers GM5clamp (Escherichia coli positions 341 to 357) and 907R
(19) were used to amplify variable regions V3 to V5 of the
16S rDNA in a touchdown PCR, as described by Buchholz-Cleven et al.
(5). To amplify the nearly complete 16S rDNA, primers 8F and
1492R (5) were used in a 35-cycle PCR with an annealing
temperature of 40°C. Bovine serum albumin (final concentration, 3 mg
ml
1) was added routinely to the PCR mixtures to prevent
interference by humic acids (24).
16S rDNA sequencing.
PCR products were purified with a
QIAquick PCR Purification Kit (Qiagen, Hilden, Germany). A
Taq DyeDeoxy Terminator Cycle Sequencing Kit (Applied
Biosystems, Foster City, Calif.) was used to directly sequence the
purified PCR products. Sequencing reactions were analyzed on an Applied
Biosystems model 373S DNA sequencer. Both strands of the amplification
products were sequenced with primers 8F, 787F, 787R, 1175R, 1099F, and
1492R (5). Primer nomenclature refers to 5' ends of the
respective target sites on the 16S rDNA according to the E. coli numbering of 16S rRNA nucleotides (4).
Phylogenetic analysis.
The ARB program package and the ARB
database (34) were used for phylogenetic analysis. Sequences
were aligned to the 16S rRNA primary structures present in the ARB
database by using the automatic aligner tool, and the results were
corrected manually where necessary. Pairwise distance matrix analysis
was performed with the 16S rRNA sequences by considering only those
positions that were present in both sequences. Phylogenetic trees were
reconstructed for all available sequences from the
subclass of
Proteobacteria, and a selection of representatives of major
groups outside this subclass was used as an outgroup. Only sequences
with at least 1,350 nucleotides were used. Tree topology was evaluated
by using neighbor-joining, maximum-parsimony, and maximum-likelihood
algorithms on the full set of data or on a subset. Furthermore, we
applied filters that excluded positions with less than 50%
conservation within the
subclass. Branching orders that were not
supported by all methods are shown as multifurcation (Fig.
1).

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FIG. 1.
Phylogenetic affiliations of psychrophilic
sulfate-reducing isolates and specificities of probes used in this
study. The tree shows members of the subclass of
Proteobacteria and was constructed by using the
neighbor-joining algorithm and a 50% conservation filter. The arcs
comprise the respective probe target groups. Sval428 is described in
this study. Other probes are as described by Devereux et al.
(7). Strains isolated from Svalbard sediments are shown in
boldface type. Strain names indicate the carbon sources on which the
strains were isolated (A, acetate; L, lactate; P, propionate; and B,
betaine) and the sampling site (Sv2 indicates Hornsund and Sv5
indicates Storfjord).
|
|
Oligonucleotide probes.
Oligonucleotides were purchased from
Biometra (Göttingen, Germany). The probe target sequence of
Sval428 is 5' GTAAAATCCTGTCAGATGG 3' (E. coli
positions 428 to 446). Probes used and their specificities are shown in
Fig. 1.
RNA extraction and slot blot hybridization.
Nucleic acids
were isolated directly by bead beating, phenol extraction, and
isopropanol precipitation as described by Sahm and Berniger
(28). Between 10 and 100 ng of RNA was blotted on nylon
membranes (Magna Charge; Micron Seperations, Westborough, Mass.) in
triplicate and probed with radioactively labeled oligonucleotides as
described previously (33). Membranes were prehybridized at 40°C and washed at different temperatures depending on the
dissociation temperature (Td) of the probe as
follows: 54°C (EUB338 [1]), 45°C (687 [7]), 59°C (660 [7]),
46°C (804 [7]), or 52°C (Sval428). The Td
for probe Sval428 was determined according to the method of Raskin et
al. (21), with rRNA from strain LSv20 being used as one
mismatch control. Intensity of hybridization signal was measured with a
PhosphorImager (Molecular Dynamics, Sunnyvale, Calif.) and quantified
as described by Sahm et al. (29) with the program ImageQuant
(Molecular Dynamics). rRNA isolated from Desulfovibrio
salexigens (DSM 2638), Desulfobulbus elongatus (DSM 2908), Desulfococcus multivorans (DSM 2059), and strain
LSv23 served as standards for hybridization with the probes specific for sulfate reducers.
DGGE and Southern hybridization analysis.
DGGE was performed
on a D-Gene system (Bio-Rad, Munich, Germany) as described previously
(17, 18). PCR products were analyzed directly on a
1-mm-thick 6% polyacrylamide gel containing a denaturing gradient from
20 to 80%. Electrophoresis with 1× TAE buffer (40 mM Tris-acetate, 1 mM EDTA [pH 8]) was performed at 100 V for 20 h. After
electrophoresis, the gels were stained in ethidium bromide and
photographed on a UV transilluminator. DGGE gels were blotted onto
nylon membranes via electroblotting as described by Muyzer et al.
(18). Hybridization analysis was performed with probe
Sval428 by the protocol described by Santegoeds et al. (30).
The probe was end labeled with [
-32P]ATP, and the
membrane was hybridized at 40°C overnight. Stringent washes were
performed in 2× SSC (1× SSC is 0.15 M NaCl plus 0.015 M sodium
citrate)-0.1% (wt/vol) sodium dodecyl sulfate at the previously
determined Td of 56°C. The
Td of the probe was determined by the method
described by Raskin et al. (21) for DNA and RNA targets. The
hybridized membranes were sealed in plastic bags and exposed for 1 to 7 days on an X-ray film or a PhosphorImager screen.
Nucleotide sequence accession numbers.
The 16S rDNA
sequences have been deposited in the GenBank database. Accession
numbers are AF099054 to AF099065 and AF136008.
 |
RESULTS AND DISCUSSION |
Phylogenetic affiliation of isolates.
Psychrophilic sulfate
reducers isolated from MPN enrichments (12) were
phylogenetically analyzed by 16S rDNA sequencing. All isolates belonged
to the
subclass of the Proteobacteria, as is the case
for the majority of mesophilic sulfate reducers (32).
Adaptation to cold temperatures as represented by our sulfate-reducing
isolates was widely spread within this phylogenetic group (Fig. 1). On
the basis of their phylogenetic distance, strains ASv25, BSv41, and
LSv20 belong to the existing genera Desulfobacter, Desulfobacterium, and Desulforhopalus (3.6, 1.9, and 0.7% phylogenetic distance, respectively) (Fig. 1). The remaining
10 strains were only distantly related (phylogenetic distance, 6.4 to
11.6%) to known sulfate reducers. Five of these have recently been
described as members of three new genera (13). The results
suggest that psychrophily is a polyphyletic property within
gram-negative sulfate reducers. Furthermore, the wide distribution of
our isolates within the
-Proteobacteria indicates that
the diversity among psychrophilic SRB might be as high as among mesophiles.
Probe design.
Since cultivation is inherently selective and
often leads to the isolation of quantitatively less-important microbial
groups, we estimated the abundance of these isolates by a
cultivation-independent method, i.e., rRNA slot blot hybridization.
Besides LSv55, all strains that were related to the
Desulfobacteriaceae were targeted by an already existing
probe (probe 804) designed by Devereux et al. (7). Of the
remaining strains, six incomplete oxidizers formed a cluster related to
Desulfocapsa sp., Desulfofustis glycolicus, and
the only other known moderately psychrophilic sulfate reducer, "Desulforhopalus vacuolatus" ltk10 (10) (Fig.
1). Two strains of this cluster have recently been described as species
of the new genus Desulfotalea (13). The cluster
will in what follows be referred to as the Desulfotalea
cluster. This cluster was chosen for the design of a new
oligonucleotide probe (Sval428). In addition to the two
Desulfotalea strains and strains LSv23, LSv24, and LSv53,
one of the mesophilic sulfate reducers, Desulfofustis
glycolicus (8), is targeted by the probe (Fig. 1). It
has one mismatch to LSv20 and "Desulforhopalus
vacuolatus" ltk10 (10). LSv55 and LSv20 are the only
strains isolated from Spitsbergen sediments not targeted by the set of
probes used.
rRNA quantification of sulfate reducers.
rRNA slot blot
hybridization revealed that the concentration of SRB rRNA for all
target groups generally decreased with depth (Table
1), following the trend of total
prokaryotic rRNA (28) and MPN counts (12). The
relative contribution of SRB rRNA to total eubacterial rRNA (pooled
signals from all probes), however, increased from 3.8% in core A and
4.0% in core B at the surface to 10.5% in core A and 17% in core B
at a depth of 15 to 18 cm in Hornsund and from 10.5% in core A and 7%
in core B to 58.6% in core A and 36.4% in core B at a depth of 27 to
30 cm in Storfjord (Table 2).
The high concentration of detectable SRB rRNA in the first 2 to 3 cm of
the sediment is in striking contrast to the very low
sulfate reduction
rates measured within this layer in parallel
cores (
12,
27).
The high abundance of SRB in the zone where
low sulfate reduction rates
are measured can also be seen in MPN
counts (
12) and was
also observed in a coastal sediment of the
Baltic Sea by RNA slot blot
hybridization (
29). These findings
suggest that SRB might
use electron acceptors other than sulfate
in the oxidized zone of the
sediment. In this respect it is interesting
that four of the five
isolated strains tested for iron reduction
were able to grow on Fe(III)
(
13). In addition Kostka et al.
(
14) showed that
in Storfjord sediments Fe(III) reduction accounted
for almost 10% of
the total carbon oxidation but that it was insignificant
at Hornsund.
Other potential electron acceptors like NO
3
or Mn(IV) were of minor importance in the investigated sediments
(
14).
Relative abundance of SRB and physiological considerations.
SRB can, in general, be divided into two major groups: those that
oxidize the carbon source completely to CO2 and those that oxidize the carbon source incompletely to acetate. rRNA hybridization revealed a predominance of incompletely oxidizing SRB in these sediments. We detected incompletely oxidizing groups targeted by probes
687 (Desulfovibrionaceae but also some
Geobacteraceae [16]), 660 (Desulfobulbus sp.), and Sval428 (Desulfotalea
cluster), while the completely oxidizing genera
Desulfococcus, Desulfosarcina, Desulfobacterium, and Desulfobacter targeted by
probe 804 were below the detection limit (Table 2). This result is in
agreement with cultivation-dependent data, since cell numbers of
complete oxidizers on acetate were 10- to 100-fold lower than those of lactate oxidizers (12). If this finding reflects the actual relation between complete and incomplete oxidizers, the RNA
concentration for acetate oxidizers would be at or below the detection
limit of slot blot hybridization. Another possible explanation for not detecting RNA of complete oxidizers is that these organisms were not
targeted by the probe used; all completely oxidizing strains isolated
in this study, however, had the target sequence of probe 804.
The low abundance of complete oxidizers contrasts with results from
estuarine, coastal, and vegetated salt marsh sediments
(
6,
25,
29), where the 804 target group was reported to
be one of the
major groups of SRB. Dominant sulfate reducers in
these studies were
species of the nutritionally versatile genera
Desulfobacterium,
Desulfococcus, and
Desulfosarcina. The occurrence
of these groups may reflect
the input of a wide variety of carbon
sources in coastal zone habitats
close to the mainland. Our study,
in contrast, was conducted in a
remote, sparsely populated region.
Data on the amount and type of
biologically available carbon sources
would be necessary to determine
the relationship between substrates
and the occurrence of specific
groups of
SRB.
A second group of complete oxidizers, namely, those that grow readily
on acetate, is of special interest in sediments. These
bacteria belong
to the genus
Desulfobacter, like strain ASv25,
or to the
gram-positive genus
Desulfotomaculum. Although acetate
is
hypothesized to be one of the major carbon sources for SRB
in marine
sediments (
20,
31), we could not detect
Desulfobacter sp. rRNA in our samples. Boschker et al.
(
3) showed recently
that addition of
[
13C]acetate to an intertidal sediment led to an
incorporation of
label in polar-lipid-derived fatty acids typical of
Desulfotomaculum acetoxidans. An rRNA probe for
Desulfotomaculum sp. is not yet
available. Neither
cultivation (
12) nor clone library (
22)
data
indicate the presence of
Desulfotomaculum sp., but the use
of a specific probe is needed to further investigate their role
in
acetate oxidation in marine
sediments.
The major group of SRB was the
Desulfovibrionaceae or
Geobacteraceae cluster (probe 687), which in the deeper
zones accounted
for up to 8.6 and 12.9% of the RNA at Hornsund (15 to
18 cm) and
for 36.0 and 20.4% at Storfjord (27 to 30 cm) (Table
2);
however,
no
Desulfovibrionaceae were isolated from MPN
cultures (
12).
We took this as an indication that the
detected RNA might be coming
from organisms of the
Geobacteraceae group. A clone library established
for
Hornsund sediment samples (see the accompanying publication
[
22]) further supported this theory. Of all clones
screened,
46 (13%) gave a positive signal with probe 687. Diversity
within
this group was very low, with one phylotype being represented
by
39 clones and six additional phylotypes being represented by
only one
or two clones (
22). All belonged to the family
Geobacteraceae and were most closely related to
Desulfuromonas palmitatis. Species
of the genus
Desulfuromonas belong to the

subclass of
Proteobacteria and are able to completely oxidize acetate
via reduction of sulfur
(
37). Since completely oxidizing
genera of sulfate reducers
(804 target group) were below the detection
limit, the high abundance
of sequences related to
Desulfuromonas sp. in the clone library
might indicate that
acetate is mineralized by sulfur reducers
in these sediments; however,
the phylogenetic distance between
the clones and
Desulfuromonas
palmitatis is so large (6.3%) that
we can only speculate on the
possible physiological properties
of this group until pure cultures
have been isolated. Sequence
information derived from the clone library
will enable us now
to design a specific probe for this 687-positive
clone group and
investigate its actual abundance. Furthermore, the
phylogenetic
affiliation might help to choose selective culture
conditions.
RNA related to the genus
Desulfobulbus (probe 660) was
present in small amounts in both stations, with relative contributions
varying between 0.5 and 2.7%. Clone library data suggest at least
one
additional group of SRB not targeted by our probes. This group
is
related to
Desulfobulbus sp. and to isolate LSv55 and
represents
6.5% of the clone library (
22). A new specific
probe is being
developed to investigate the abundance of these isolates
in the
sediment.
Occurrence of the new psychrophilic isolates.
The
Desulfotalea cluster (probe 428), containing many
psychrophilic isolates, was the second largest group among the detected sulfate reducers. In Storfjord, up to 15.0 and 20.9% (27 to 30 cm) of
the eubacterial RNA was related to our isolates (Table 2). To estimate
whether potentially dominant strains of the target group had been
isolated, DGGE and Southern hybridization with probe Sval428 were
performed on community DNAs. Positions of the hybridization signals
within the community pattern were compared to the positions of
amplified 16S rDNAs from isolates belonging to this group (Fig.
2). In both stations, we could detect
several positive bands. One of them had the same position as isolates LSv23, LSv24, and LSv53 (Fig. 2). These isolates are closely related, showing three to four bases' difference within the amplified DNA fragment, and cannot be distinguished by DGGE. The presence of additional positive bands showed that there are at least three additional RNA species of this group present in Hornsund (Fig. 2) and
one in Storfjord (data not shown) sediments. The high abundance of
Desulfotalea-related rRNAs and the identification of bands corresponding to isolates in the community DNA profile demonstrate that
a quantitatively important group of sulfate reducers was isolated from
Svalbard sediment. In addition, this group was the second most abundant
of the detected SRB (Table 2). Since it is doubtful that the most
abundant SRB group, target group 687, is really a group of sulfate
reducers, the Desulfotalea cluster, containing mainly
psychrophilic strains, may even be the most abundant of SRB. This
observation relates to the question of whether the bacterial community
in Arctic sediments consists of cold-adapted prokaryotes. Our results
show that a major group of SRB in this habitat is psychrophilic.

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FIG. 2.
DGGE-hybridization analysis of community 16S rDNA
patterns with probe Sval428 for Hornsund sediments. (A) DGGE results;
(B) corresponding hybridization results. Numbers give the depth ranges
from which target DNAs were extracted. For each depth, two cores have
been investigated. "LSv" followed by a number indicates a DGGE
fragment of a psychrophilic sulfate-reducing isolate targeted by probe
Sval428. The arrow indicates corresponding bands between the community
profile and isolates.
|
|
In the present study, we showed that psychrophilic SRB are related to
mesophilic strains and are probably as phylogenetically
diverse as the
mesophiles. A new group of psychrophilic sulfate-reducing
isolates is
abundant in their source sediments. Their abundance
suggests that they
may play a previously unrecognized role in
the sulfur cycle of marine
sediments.
 |
ACKNOWLEDGMENTS |
We are grateful to Birgit Rattunde for excellent technical
assistance. We also thank the cruise leader Donald E. Canfield and the
crew of the RV Jan Mayen for a successful cruise. We
acknowledge two anonymous reviewers for helpful comments on the manuscript.
This work was supported by the Max-Planck-Society.
 |
FOOTNOTES |
*
Corresponding author. Present address: Biotechnology I,
Technology Microbiology, Technical University Hamburg-Harburg,
Denickestr. 15, D-21073 Hamburg, Germany. Phone: 49 (0)420 42878 3336. Fax: 49 (0)40 42878 2909. E-mail: ksahm{at}mpi-bremen.de.
 |
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Applied and Environmental Microbiology, September 1999, p. 3976-3981, Vol. 65, No. 9
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Copyright © 1999, American Society for Microbiology. All rights reserved.
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