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Applied and Environmental Microbiology, December 2008, p. 7546-7551, Vol. 74, No. 24
0099-2240/08/$08.00+0 doi:10.1128/AEM.01186-08
Copyright © 2008, American Society for Microbiology. All Rights Reserved.
Epsilonproteobacteria Represent the Major Portion of Chemoautotrophic Bacteria in Sulfidic Waters of Pelagic Redoxclines of the Baltic and Black Seas
,
Jana Grote,1*
Günter Jost,1
Matthias Labrenz,1
Gerhard J. Herndl,2 and
Klaus Jürgens1
Leibniz Institute for Baltic Sea Research, Section Biology, Seestrasse 15, 18119 Rostock-Warnemünde, Germany,1
Department of Biological Oceanography, Royal Netherlands Institute for Sea Research, 1790 AB Den Burg, The Netherlands2
Received 28 May 2008/
Accepted 15 October 2008

ABSTRACT
Recent studies have indicated that chemoautotrophic
Epsilonproteobacteria might play an important role, especially as anaerobic or microaerophilic
dark CO
2-fixing organisms, in marine pelagic redoxclines. However,
knowledge of their distribution and abundance as actively CO
2-fixing
microorganisms in pelagic redoxclines is still deficient. We
determined the contribution of
Epsilonproteobacteria to dark
CO
2 fixation in the sulfidic areas of central Baltic Sea and
Black Sea redoxclines by combining catalyzed reporter deposition-fluorescence
in situ hybridization with microautoradiography using [
14C]bicarbonate
and compared it to the total prokaryotic chemoautotrophic activity.
In absolute numbers, up to 3
x 10
5 14CO
2-fixing prokaryotic
cells ml
–1 were enumerated in the redoxcline of the central
Baltic Sea and up to 9
x 10
4 14CO
2-fixing cells ml
–1 were
enumerated in the Black Sea redoxcline, corresponding to 29%
and 12%, respectively, of total cell abundance.
14CO
2-incorporating
cells belonged exclusively to the domain
Bacteria. Among these,
members of the
Epsilonproteobacteria were approximately 70%
of the cells in the central Baltic Sea and up to 100% in the
Black Sea. For the Baltic Sea, the
Sulfurimonas subgroup GD17,
previously assumed to be involved in autotrophic denitrification,
was the most dominant CO
2-fixing group. In conclusion,
Epsilonproteobacteria were found to be mainly responsible for chemoautotrophic activity
in the dark CO
2 fixation maxima of the Black Sea and central
Baltic Sea redoxclines. These
Epsilonproteobacteria might be
relevant in similar habitats of the world's oceans, where high
dark CO
2 fixation rates have been measured.

INTRODUCTION
Pelagic redoxclines represent the transition zones between the
oxic and anoxic realms. Extensive pelagic redoxclines are reported
for the Black Sea (
18,
34,
36), the Cariaco Basin (
40,
42),
the Framvaren Fjord (
27), the Mariager Fjord (
45), the Baltic
Sea (
19), and freshwater lakes (
6,
9,
14) and are often characterized
by high dark CO
2 fixation rates. Characteristically, the peak
of dark CO
2 fixation within the water column is often located
below the chemocline, which we define as the shallowest appearance
of sulfide (
13).
Epsilonproteobacteria have already been suggested
to be involved in chemoautotrophic production at several marine
pelagic redoxclines (
21,
23,
26,
43), and their prevalence at
oxic-anoxic transition zones, especially in areas with previously
detected high chemoautotrophic activity, has been demonstrated
for the Black Sea and the Cariaco Basin (
23,
24,
26,
43). Whether
Epsilonproteobacteria are indeed responsible for chemoautotrophic
production, however, has not been shown for any of these habitats.
For the Baltic Sea, Jost et al. (19) determined the abundance of chemoautotrophic cells in waters below the chemocline by combining dark CO2 fixation measurements and flow-cytometric cell sorting. Two main prokaryotic cell clusters responsible for total dark CO2 fixation were detected, and 20 to 40% of the total prokaryotic community was estimated to be chemoautotrophic, but the phylogenetic identity of these clusters remained unknown. Recently, Glaubitz et al. (10) determined the diversity of chemoautotrophs using stable-isotope probing (rRNA-SIP) combined with fingerprint techniques in samples from the dark CO2 fixation maximum in the central Baltic Sea. Autotrophic activity of Gammaproteobacteria and Epsilonproteobacteria, mainly represented by the Sulfurimonas subgroup GD17, which previously has been found to be abundant in Baltic Sea redoxclines (4, 13, 21), was detected. However, these studies did not address the quantitative impact of Epsilonproteobacteria for chemoautotrophic activity in the central Baltic Sea. Consequently, the objective of the present work was to determine the contribution of Epsilonproteobacteria to dark CO2 fixation in sulfidic areas of marine redoxclines of the central Baltic Sea and the Black Sea.
For identification and quantification of metabolically active cells in environmental samples, the combination of fluorescence in situ hybridization (FISH) and microautoradiography has often been used (7, 12, 22). Here we used the more-sensitive catalyzed reporter deposition (CARD)-FISH protocol combined with microautoradiography (MICRO-CARD-FISH) to assess the specific uptake of radiolabeled bicarbonate by prokaryotic cells (41). Our results demonstrate, for the first time, with special emphasis on Epsilonproteobacteria, the quantitative distribution of CO2-fixing cells in the sulfidic areas of two marine redoxclines.

MATERIALS AND METHODS
Sampling.
The samples were obtained from the central Baltic Sea during
a research cruise onboard the RV
Professor Albrecht Penck in
April 2007 (station 271; 57°19.2'N, 20°03'E; Gotland
Deep) and from the Black Sea during a research cruise onboard
the RV
Meteor in May 2007 (station 21; 42°45'N, 37°30'E).
Water samples from the redoxclines were collected with free-flow
bottles (Hydrobios) attached to a conductivity, temperature,
and depth rosette (SBE 911+; Seabird). Concentrations of inorganic
nutrients, oxygen, and hydrogen sulfide were analyzed as described
by Grasshoff et al. (
11).
Microautoradiographic incubations and dark CO2 fixation measurements.
Incubations for MICRO-CARD-FISH and the determination of dark CO2 fixation rates started within one hour after collecting the samples from the free-flow bottles. Special care was taken to avoid oxygen contamination during sample collection. Therefore, samples were directly filled from free-flow bottles into the test tubes with an overflow of at least five tube volumes. In the Baltic Sea, samples were taken from three depths, and in the Black Sea, from six depths. One hundred µCi of [14C]bicarbonate in anoxic solution (specific activity, 53.0 mCi mmol–1; Hartmann Analytic GmbH, Braunschweig, Germany) was added to 9-ml glass test tubes containing the water samples. Thereafter, the tubes were sealed without headspace with glass stoppers. Controls were fixed with paraformaldehyde (2% final concentration) before the addition of the radiolabeled solution. After incubation at in situ temperatures (4°C for the Baltic Sea samples and 8°C for the Black Sea samples) for 24 h in the dark, 1-ml subsamples were filtered through 0.2-µm-pore-size cellulose nitrate filters (diameter, 25 mm; Purabind 02; Whatman) and exposed to HCl fumes, and the radioactivity of the individual filters was counted in a liquid scintillation counter (Packard). The activity ranged between 99 and 6,707 dpm ml–1 of filtered sample. For MICRO-CARD-FISH, the remaining volume was immediately fixed with particle-free paraformaldehyde (2% final concentration) for 12 to 18 h at 4°C. Portions of 1.5 to 4 ml were filtered onto white polycarbonate membrane filters (type GTTP; pore size, 0.2 µm; diameter, 25 mm; Millipore). The filters were then carefully rinsed with sterile Milli-Q water, air dried, and stored at –80°C until further processing. The total inorganic carbon content of both habitats was determined by a coulometric single-operator multimetabolic analyzer (SOMMA) system (17). For samples from the Black Sea, the mean inorganic carbon concentration accounted for 3,300 µmol/kg; for those from the Baltic Sea, the concentration was 1,950 µmol/kg. Dark CO2 fixation rates were calculated from the total inorganic carbon concentration, the initial amount of [14C]bicarbonate added, and the amount of 14CO2 fixed in biomass during the incubation time.
CARD-FISH.
CARD-FISH was carried out according to the protocols of Pernthaler et al. (33) and Sekar et al. (35), modified as described previously (13). For enumeration of Bacteria, a mix of probes EUB338 (GCTGCCTCCCGTAGGAGT) (3), EUB338-II (GCAGCCACCCGTAGGTGT), and EUB338-III (GCTGCCACCCGTAGGTGT) (8) was used. Epsilonproteobacteria were detected with probe EPS914 (25), and the specific Sulfurimonas subgroup GD17 was detected with probe SUL90 (CGTGCGCCACTAATCATA) (13). Probe EPS914 (GGTCCCCGTCTATTCCTT) was successfully tested for its specificity as described previously (13). Nonspecific binding was determined using the NonEUB probe (ACTCCTACGGGAGGCAGC) (44). Negative control counts with probe NonEUB averaged 0.08 to 0.6% for both the Baltic Sea and the Black Sea samples, implying that cell counts in the same order of magnitude could be considered negligible. For hybridization, 400 µl of hybridization buffer (55% formamide for all probes) and 2 µl of probe working solution (50 pmol µl–1) were mixed. For probe mix EUB338I-III, 600 µl of hybridization buffer and 3 µl of probe working solution were used. Hybridization was carried out at 35°C for 8 to 12 h on a rotary shaker in the dark. After the filter sections had been washed in a prewarmed washing buffer (37°C) for at least 10 min, the tyramide signal amplification with 5- and 6-carboxyfluorescein-labeled tyramides was carried out for 15 min in the dark on a rotary shaker. The filters were then washed first in phosphate-buffered saline and afterwards in ethanol and then air dried.
Microautoradiography.
The autoradiographic procedure followed the protocol of Teira et al. (41), modified according to Alonso and Pernthaler (1). Hybridized filter sections were glued onto glass slides (UHU Plus Sofortfest; UHU GmbH, Germany), which were then dipped into the photographic emulsion (Kodak; type NTB-2; melted at 43°C for 20 min) and placed in a light-tight box with silica gel as a drying agent. Optimal exposure times at 4°C were 2 days for the Baltic Sea samples and 3 days for the Black Sea samples. The slides were developed (Dektol developer) and fixed (Kodak fixer) according to the specifications of Kodak. The completely dry filter sections were counterstained with the previously described mixture of 4',6'-diamidino-2-phenylindole (DAPI), Citifluor, and VectaShield (33).
Microscopy.
Filter sections were examined with an epifluorescence microscope (Axioskop 2 MOT Plus; Zeiss) equipped with a 100x Plan Apochromat oil objective lens (Zeiss) and appropriate filter sets for DAPI and fluorescein isothiocyanate (FITC). The transmission mode of the microscope allowed the detection of silver grains attached to cells. Cells associated with two or more silver grains were defined as 14CO2 positive. In negative control samples, the percentage of cells attached to at least two silver grains accounted, on average, for only 1% of all DAPI-stained cells for the Baltic Sea redoxcline and 0.6% for the Black Sea redoxcline. Switching between fluorescence and transmission modes allowed probe-hybridized 14CO2-positive and inactive cells to be counted directly, followed by the determination of DAPI-stained cells to estimate the total prokaryotic abundance. Between 500 and 1,000 DAPI-stained cells in randomly distributed microscopic fields were counted for each filter section. Bacterial counting of DAPI-stained samples and hybridized samples is usually done with a standard deviation of less than 7.5% for replicates of the central Baltic Sea redoxcline (13).

RESULTS
Bacterial abundance and activity in the Baltic Sea.
The chemocline, defined as the shallowest appearance of hydrogen
sulfide, was located at a depth of 136 m in the Gotland Deep
in April 2007 (Fig.
1). Oxygen was not detected below a depth
of 121 m; nitrate was below the detection limit at a depth below
132 m. Dark CO
2 fixation rates below the chemocline ranged from
1.0 to 2.2 µmol of C liter
–1 day
–1; the highest
rate was measured at a depth of 142 m. Prokaryotic abundance,
determined by DAPI, remained constant across the three depth
layers, at around 1
x 10
6 cells ml
–1 (Fig.
2A). MICRO-CARD-FISH
was applied to visualize the
14CO
2-fixing activity of individual
prokaryotic cells, and
14CO
2-positive cells were enumerated
for the central Baltic Sea.
14CO
2-positive cells, ranging between
1.2
x 10
5 and 3.1
x 10
5 cells ml
–1, accounted for 12.2
to 29.0% of the total cell abundance (Fig.
2A). Nearly all
14CO
2-positive
cells were positive for probe EUB338I-III and were consequently
assigned to
Bacteria. The use of probe EPS914, specific for
Epsilonproteobacteria, revealed that
14CO
2-positive
Epsilonproteobacteria contributed between 63 and 77% of the total number of
14CO
2-fixing
Bacteria at all depths examined. Hence, in the Gotland Deep,
Bacteria taking up
14CO
2 belonged mainly to
Epsilonproteobacteria and, more specifically, to the
Sulfurimonas subgroup GD17 (Fig.
2B). Generally, the abundance of GD17 cells with respect to
total cell abundance was in the same order of magnitude as for
Epsilonproteobacteria; thus, members of group GD17 predominated
within this group (Table
1). Concerning the proportion of
14CO
2-positive
GD17 cells, no more than 65% of total GD17 cells were
14CO
2 fixing at all depths examined (Table
1).
View this table:
[in this window]
[in a new window]
|
TABLE 1. Proportion of Bacteria, Epsilonproteobacteria, and group GD17 cells as percentages of total cell abundance (DAPI counts) in the Baltic Sea and Black Sea redoxclinesa
|
Bacterial abundance and activity in the Black Sea.
In the Black Sea redoxcline, the chemocline was located at a
depth of 110 m (Fig.
3). Nitrate and oxygen were below the detection
limit at a depth of more than 90 m. The pronounced maximum of
dark CO
2 fixation rates was detected at a depth of 115 m (Fig.
3). Total prokaryotic abundance ranged between 0.45
x 10
6 and
0.72
x 10
6 cells ml
–1; between 0.1
x 10
5 and 0.95
x 10
5 cells ml
–1 were identified as
14CO
2 positive, constituting
up to 12.8% of total DAPI counts (Fig.
4A). As in the Baltic
Sea, MICRO-CARD-FISH of Black Sea samples revealed that
14CO
2-fixing
activity was exclusively due to
Bacteria, i.e., EUB338I-III-positive
cells.
Epsilonproteobacteria taking up
14CO
2 constituted 24
to 100% of all
14CO
2-positive cells, indicating their dominance
in dark CO
2 fixation among
Bacteria (Fig.
4B; also see Fig.
S1 in the supplemental material).
14CO
2-positive GD17 cells
were only detected at a depth of 120 m and amounted to only
1.6% of all DAPI-stained cells. The contribution of group GD17
cells to total cell abundance was low and below the detection
limit for deeper layers (Table
1) but accounted for, on average,
12% of total epsilonproteobacterial abundance in the upper layers.
14CO
2-assimilating cells within the
Epsilonproteobacteria ranged
from 33.0 to 61.0% of the total
Epsilonproteobacteria in the
zone characterized by the highest dark CO
2 fixation rates (110
to 125 m) (Table
1).

DISCUSSION
The results of this study provide direct evidence for the quantitative
significance of
Epsilonproteobacteria in dark CO
2 fixation in
sulfidic areas of two marine redoxclines. In the sulfidic area
of the Baltic Sea as well as the Black Sea redoxcline, cells
taking up
14CO
2 were identified by MICRO-CARD-FISH as
Bacteria;
more specifically, they were mainly composed of
Epsilonproteobacteria.
In this study, the fraction of
14CO
2-assimilating
Bacteria in
the Baltic Sea was two times higher than the highest corresponding
percentage obtained for the Black Sea. Similarly, dark CO
2 fixation
rates for the Baltic Sea were substantially higher than those
determined for the Black Sea, albeit comparable to previously
reported rates (
13,
18,
21,
37). The total abundance of
Epsilonproteobacteria in the Black Sea and, more specifically of group GD17 cells
in the Gotland Deep, was consistent with previous CARD-FISH
results, which showed high abundance and a wide depth distribution
(
13,
24). Likewise, the layer with the highest abundance of
CO
2-fixing cells was located in the sulfidic area, with a sulfide
concentration of 8 to 10 µmol liter
–1 for both habitats.
For the Baltic Sea, the number of cells taking up
14CO
2 generally
agreed with the calculations of Jost et al. (
19), who estimated
between 20 and 40% chemoautotrophic cells.
The importance of bacterial chemoautotrophic production, measured as dark CO2 fixation, has been discussed for different marine redoxclines in relation to phototrophic primary production (34, 39). Combining dark CO2 fixation measurements with the number of 14CO2-positive cells assessed by MICRO-CARD-FISH allows cell-specific dark CO2 fixation rates to be estimated for chemoautotrophic cells, assuming CO2 as the sole carbon source. The anaplerotic uptake of CO2 by heterotrophic bacteria was considered to be insignificant for chemoautotrophic CO2 fixation, as outlined by Jost et al. (19) and Taylor et al. (40). Based on these assumptions, cell-specific dark CO2 fixation rates would amount to 61 to 217 fg of C cell–1 day–1 for the Baltic Sea redoxcline and 61 to 115 fg of C cell–1 day–1 for the Black Sea redoxcline. These rates are unrealistically high and also are not in line with the cell-specific CO2 uptake rates of 10 to 25 fg of C cell–1 day–1 calculated for a Baltic Sea redoxcline by Jost et al. (19) after flow-cytometric sorting of 14CO2-labeled cell clusters. However, those authors based their calculation on a higher abundance of CO2-fixing cells than was found in the present study by using MICRO-CARD-FISH. It is possible that the amount of 14CO2-positive cells reported here was underestimated due to the detection limit of microautoradiography and to possible leakage of incorporated radioactivity during fixation and storage (31). Furthermore, protists that were grazing on chemoautotrophic bacteria during incubation or were harboring chemoautotrophic ecto- and endosymbiotic bacteria could have reduced the amount of 14CO2-positive cells visible after MICRO-CARD-FISH. It has been reported previously that the standard CARD-FISH procedure is destructive to protist cells (29).
Chemoautotrophic Archaea have recently been identified in mesopelagic waters of the North Atlantic (15) and elsewhere (16, 20). Almost all 14CO2-positive cells in the dark CO2 fixation maxima of the Baltic Sea and Black Sea redoxclines belonged to Bacteria, precluding a major archaeal contribution to the chemoautotrophic community in the sulfidic areas of these redoxclines. As mentioned above, for the Baltic Sea, Glaubitz et al. (10) investigated the incorporation of 13C into chemoautotrophic cells by rRNA-SIP. The authors could not identify autotrophic Archaea; however, autotrophic activity of Gammaproteobacteria in addition to that of Epsilonproteobacteria, mostly belonging to group GD17, was shown. Consequently, for the Baltic Sea, it is likely that the remaining proportion of unidentified 14CO2-fixing cells in the present study consisted, at least partly, of Gammaproteobacteria. However, hybridizations with probe GAM42a (28) did not detect chemoautotrophic cells in samples from the central Baltic Sea; however, this may have been due to sequence mismatch (our unpublished results) (2).
Campbell et al. (5) emphasized the potential role of Epsilonproteobacteria for biogeochemical cycles, especially at the oxic-anoxic interfaces. For deep-sea hydrothermal fields, chemoautotrophic activity by Epsilonproteobacteria has been demonstrated by different authors (30, 32, 38). Lin et al. (23, 24) showed elevated epsilonproteobacterial abundances but low epsilonproteobacterial 3H-leucine assimilation activity for the Cariaco Basin and proposed chemoautotrophic activity of Epsilonproteobacteria there. Epsilonproteobacteria constitute 75 to 100% of 14CO2-assimilating Bacteria in the layers of highest dark CO2 fixation in this study, and they apparently contributed substantially to chemoautotrophic production in both the Black Sea and Baltic Sea redoxclines and can be regarded as key organisms for chemoautotrophic production. Therefore, the question arises as to whether or not Epsilonproteobacteria are globally important chemoautotrophs in marine habitats where high dark CO2 fixation rates around redoxclines have been measured.
Among 14CO2-positive Epsilonproteobacteria, members of the Sulfurimonas subgroup GD17 were the dominant representatives in the sulfidic area of the Baltic Sea, in contrast to the rather low contribution of group GD17 to Epsilonproteobacteria in the Black Sea. Grote et al. (13) discussed the possible contribution of group GD17 to autotrophic activity, even though quantitative PCR data suggested a restricted high-activity zone of this group around the chemocline several meters above the dark CO2 fixation maximum. However, the results of this study evidence the major contribution of group GD17 to dark CO2 fixation in the sulfidic area of the Baltic Sea. Still, the prevailing metabolism for chemoautotrophy in marine sulfidic areas is unknown, and the availability of electron acceptors for chemoautotrophy has been discussed by several authors previously (13, 18, 40). Dark CO2 fixation driven by autotrophic denitrification with reduced sulfur compounds as electron donors is unlikely, since there was no evidence for a clear overlap between nitrate and hydrogen sulfide. The oxidation of reduced sulfur species combined with the reduction of particulate metal oxides might be possible in the Baltic Sea and in the Black Sea (18, 19). Members of group GD17 were initially regarded as sulfur-oxidizing denitrifiers, but the remaining high cell numbers in sulfidic nitrate-deprived waters suggested a possible metabolic versatility for this group (4, 13). Notably, the percentage of 14CO2-assimilating epsilonproteobacterial cells in layers with the highest dark CO2 fixation rates never exceeded 65% of total Epsilonproteobacteria, leaving 35% of the cells either metabolically inactive or heterotrophic. As mentioned above, Lin et al. (23) detected a significant number of heterotrophic Epsilonproteobacteria in the Cariaco Basin. These findings stress the potential for heterotrophic as well as autotrophic activity within the Epsilonproteobacteria at marine redoxclines. Moreover, considering the Baltic Sea redoxcline, with group GD17 as the dominant epsilonproteobacterial representative, it is likely that group GD17 is metabolically versatile, exhibiting chemoautotrophy and, potentially, heterotrophy. The ability of members of group GD17 to switch between heterotrophic and autotrophic metabolism could also explain its wide depth distribution, from the suboxic to the sulfidic layers, as reported by Grote et al. (13).
In conclusion, even though the entire ecophysiological capacity and metabolism of these Epsilonproteobacteria are not fully understood yet, this study demonstrates the major role of these bacteria in chemoautotrophic production in the sulfidic areas of redoxclines of the central Baltic Sea and Black Sea. Together with the results of Glaubitz et al. (10), who reported the transfer of chemoautotrophic production to the microeukaryotic community, our findings underline the importance of Epsilonproteobacteria for these habitats. Further studies in other sulfidic areas exhibiting high dark CO2 fixation rates will show whether Epsilonproteobacteria are also key players in inorganic carbon fixation in similar specific aquatic habitats worldwide.

ACKNOWLEDGMENTS
We are very grateful to the captains and crews of the RV
Professor Albrecht Penck and RV
Meteor for their excellent support during
sampling cruises. Data for the nitrate concentration in the
Black Sea were provided by G. Lavik. We thank A. Loy for making
available probe EPS914. The excellent technical assistance of
H. Brockmöller, B. Sadkowiak, D. Setzkorn, and N. Schreiber
is greatly appreciated.
This work was funded by the Leibniz-Institut für Ostseeforschung Warnemünde and by a DFG grant (LA 1466/4-1) to M.L.

FOOTNOTES
* Corresponding author. Mailing address: IOW-Baltic Sea Research Institute Warnemuende, Section Biology, Seestrasse 15, 18119 Rostock-Warnemuende, Germany. Phone: 49 (0)381 5197 109. Fax: 49 (0)381 5197 440. E-mail:
jana.grote{at}io-warnemuende.de 
Published ahead of print on 24 October 2008. 
Supplemental material for this article may be found at http://aem.asm.org/. 

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Applied and Environmental Microbiology, December 2008, p. 7546-7551, Vol. 74, No. 24
0099-2240/08/$08.00+0 doi:10.1128/AEM.01186-08
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