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Applied and Environmental Microbiology, September 1999, p. 4230-4233, Vol. 65, No. 9
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.

Community Size and Metabolic Rates of Psychrophilic Sulfate-Reducing Bacteria in Arctic Marine Sediments

Christian Knoblauch,1,* Bo Barker Jørgensen,1 and Jens Harder2

Departments of Biogeochemistry1 and Microbiology,2 Max Planck Institute for Marine Microbiology, D-28359 Bremen, Germany

Received 11 March 1999/Accepted 2 July 1999


    ABSTRACT
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The numbers of sulfate reducers in two Arctic sediments with in situ temperatures of 2.6 and -1.7°C were determined. Most-probable-number counts were higher at 10°C than at 20°C, indicating the predominance of a psychrophilic community. Mean specific sulfate reduction rates of 19 isolated psychrophiles were compared to corresponding rates of 9 marine, mesophilic sulfate-reducing bacteria. The results indicate that, as a physiological adaptation to the permanently cold Arctic environment, psychrophilic sulfate reducers have considerably higher specific metabolic rates than their mesophilic counterparts at similarly low temperatures.


    TEXT
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Dissimilatory sulfate reduction is the most important bacterial process in anoxic marine sediments, accounting for up to half of the total organic carbon remineralization (4, 12, 21). Since more than 90% of the global sea floor is cold (<4°C [19]), sulfate reducers must be able to metabolize and grow at low ambient temperatures. Sulfate reduction rates (SRRs) in polar sediments may be similar to those of temperate environments (14, 21, 24, 28), but sulfate reducers active in polar sediments have not been isolated and studied.

Similar SRRs in cold and temperate sediments could be explained either by (i) the presence of more sulfate reducers in cold environments, thus compensating for lower per-cell SRRs (i.e., cell-specific SRRs) at low temperatures, or by (ii) comparable community sizes in both environments but higher specific respiration rates of psychrophiles relative to those of mesophiles at low temperatures. In the present study, both possibilities were investigated by quantifying sulfate reducers in two polar sediments as well as by comparing specific SRRs of new psychrophilic isolates to those of known mesophilic sulfate-reducing bacteria (SRB). Because the phylogeny and physiology of sulfate reducers living in polar sediments were previously unknown, we used the most-probable-number (MPN) method to count and subsequently isolate the most abundant cultivable sulfate reducers for further pure-culture studies.

Two permanently cold sediments, located off the coast of Svalbard, Hornsund (76°58'2"N, 15°34'5"E; in situ temperature, 2.6°C) and Storfjord (77°33'0"N, 19°05'0"E; in situ temperature, -1.7°C), were sampled during a cruise in September and October of 1995. For further information about sampling sites, see Kostka et al. (18). Sediment was collected with a multicorer, and one individual core (referred to as core A) was subsampled for enumeration of sulfate reducers by triplicate MPN series (2), SRR measurements by the whole-core method (11), and nucleic acid analysis (25). The subcores were sliced on the ship, and samples from five sediment layers between the surface and 30-cm depth (Fig. 1) were transferred to liquid medium (17) containing either lactate (20 mM) or acetate (15 mM). Additionally, single-dilution series with propionate (20 mM) or propanol (20 mM) were inoculated. The cultures were incubated at 4, 10, and 20°C in our laboratory, and growth of sulfate reducers was monitored by measuring sulfide production during the following 30 months.

At both sampling sites, the maximum MPN counts of SRB occurred in the top 6 cm of the sediment. In particular in Storfjord, the highest SRRs occurred at a deeper layer than the maximum cell counts (Fig. 1). Below that depth, cell numbers decreased sharply. Maximum cell numbers were generally detected in MPN series incubated at 10°C with lactate as the substrate (Fig. 1b and d). Higher cell numbers at 10°C than at 20°C indicate that the majority of cultivable sulfate reducers in the sediment are unable to grow at 20°C, thus providing the first microbiological evidence for a predominantly psychrophilic sulfate reducer community in a marine sediment. Maximum MPNs with acetate as the substrate were 10- to 100-fold lower than those with lactate as the substrate for cultures and were always highest at 20°C. These results are probably due to extremely slow growth of acetate oxidizers at 4 and 10°C and not to a mesophilic acetate-oxidizing SRB community. This conclusion is supported by the facts that the first positive enrichments of samples collected at Storfjord, incubated at 4 and 10°C on acetate, were detected after more than 6 months and that counts increased slowly during the following 2 years.


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  		FIG. 1.   Depth profile of SRRs in Hornsund (a) and Storfjord (c) at in situ temperatures and MPN counts of SRB in Hornsund (b) and Storfjord (d) sediments. MPN series were incubated at different temperatures with either lactate (, 20°C; , 10°C; , 4°C) or acetate (, 20°C; , 10°C; box-plus , 4°C). Horizontal bars represent 95% confidence intervals, and vertical bars indicate the depths of sediments used for MPN enrichments.

In contrast to this microbiological evidence for a community with a psychrophilic growth potential (optimum temperature, below 20°C), Sagemann et al. (24) measured the highest SRRs for Hornsund and Storfjord sediments at 27°C. These process rate measurements seem to contradict our results from MPN counts. However, Isaksen and Jørgensen (9) demonstrated that a moderately psychrophilic SRB had an optimum temperature for sulfate reduction (28°C) 10°C higher than that for growth (18°C). This result indicates that the observed maximum SRRs at 27°C in the Svalbard sediments might still be assigned to a psychrophilic community.

MPN counts yielded no evidence for a larger community size of cultivable sulfate reducers in Arctic sediments relative to temperate sediments since maximum cell counts, e.g. 4.3 × 105 cells cm-3 for Hornsund sediments (Fig. 1b), are in the range of those reported previously for temperate marine sediments (2 × 105 to 2 × 106 cells cm-3 (13, 20, 27). Furthermore, parallel slot blot hybridizations indicate that numbers of SRB in Hornsund and Storfjord are comparable to those in temperate sediments (25, 26). If the community size and the SRRs in Arctic and temperate habitats are similar, then SRRs per cell must be comparable too, irrespective of the temperature difference.

To test this possibility, pure cultures of Arctic SRB were isolated from the highest dilution steps of the MPN enrichments by the modified deep-agar dilution technique (10). At 20°C, only three pure cultures could be isolated because most enrichments did not continue to grow after a transfer to fresh medium. None of these isolates is able to grow at the in situ temperature of the sampling sites, providing further evidence that the community active in the sediments is psychrophilic. At 4 and 10°C, 30 different strains were isolated from the MPN enrichments. Based on a preliminary physiological and phylogenetic characterization, 19 psychrophilic strains were selected for further studies. All strains except LSv22 had optimum temperatures below 20°C, and only three isolates grew at 26°C (Table 1). More relevant, however, is that they are the first isolates that grow at a typical temperature for polar sediments, i.e., the freezing point of seawater, -1.8°C (Table 1). Doubling times at -1.8°C were 4 to 6 days for the lactate-grown strains LSv54, LSv514 and LSv21 but more than 5 weeks for the acetate- and propionate-grown strains ASv26 and PSv29 (16).

                              
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  		TABLE 1.   Growth characteristics and specific SRRs of psychrophilic SRB measured at the in situ temperatures of their habitats

To compare SRRs of psychrophiles and mesophiles at the temperatures of their respective habitats, the specific SRRs of psychrophilic SRB were measured at the in situ temperatures of the Arctic sediments (2.6 and -1.7°C) and SRRs for 9 mesophiles were measured at 4, 8, and 13°C, temperatures in the range normally encountered in temperate sediments. All cultures were grown to the exponential growth phase, and rates were measured with the radiotracer method as described elsewhere (16). Specific SRRs of psychrophiles at 2.6 and -1.7°C varied between 1 and 42 fmol cell-1 day-1 (Table 1). All mesophiles reduced sulfate at 4°C, although only Desulfobacter hydrogenophilus was able to grow at that temperature. Specific SRRs of all mesophiles except D. hydrogenophilus (Table 2) increased exponentially with increasing temperatures but were still comparable to those found for the psychrophiles at temperatures 6 to 10°C lower. Since it is difficult to directly compare rates for mesophiles and psychrophiles at low temperatures because their growth temperature ranges do not overlap, we fitted mean rates for mesophiles by the Arrhenius equation: rate = A · exp(-Ea · [R · T]-1), where A is a constant, Ea is apparent activation energy, R is the gas constant, and T is absolute temperature expressed in Kelvins. The fit was extrapolated to <0°C and compared to rates for psychrophiles (Fig. 2). Calculated rates for mesophiles at 2.6 and -1.7°C were three- to fourfold lower than the measured rates for psychrophiles at the same temperatures (Fig. 2). The comparison of biomass-specific SRRs yielded similar differences (data not shown). These differences indicate that psychrophilic SRB are adapted to low temperatures not only because their minimum growth temperatures are at or below in situ temperatures but also because their metabolic rates are comparable to those of mesophiles at temperatures 6 to 10°C higher. Many studies have demonstrated that organisms active at low temperature differ physiologically from their counterparts in warmer environments (reference 22 and references therein). Cell membranes of psychrophiles tend to contain more unsaturated fatty acids (3, 5) and short-chain fatty acids (3) than membranes of mesophiles. Changes in the membrane composition might lead to a more efficient solute uptake at low temperatures (23). Furthermore, psychrophiles synthesize enzymes with high catalytic activities at low temperatures (8) and produce more enzymes when the temperature decreases (7). Different enzymes or enzyme levels could be one explanation for the comparable SRRs for psychrophiles and mesophiles at different temperatures.

                              
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  		TABLE 2.   Specific SRRs of mesophilic SRB at different temperatures


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  		FIG. 2.   Mean values of specific SRRs of 10 mesophilic sulfate reducers (closed circles) determined at 4, 8, and 13°C, 14 psychrophiles from Hornsund sediments (open square), and 5 psychrophiles from Storfjord sediments (open triangle). Dashed line represents the Arrhenius fit of specific SRRs for mesophiles. Bars represent standard deviations of the means for all strains.

The calculated activation energy (Ea) of mesophilic SRB was 90.6 kJ/mol, which is within the range (23 to 132 kJ/mol) determined previously for sulfate reduction in temperate sediments (1, 6, 29) and close to the values (74 and 85 kJ/mol) calculated from specific SRR between 0 and 30°C for a Desulfovibrio desulfuricans strain (15). Thus, we suppose that the specific SRRs measured in pure cultures are representative for mesophilic sulfate reducers of temperate sediments. However, the possibility that measured rates for mesophiles were biased by the inability of most strains to grow at the low experimental temperatures cannot be ruled out. This problem could not be avoided in our use of culture collection strains because mesophilic marine sulfate reducers that are able to grow at temperature as low as 0°C are almost unknown.


    ACKNOWLEDGMENTS

We thank the cruise leader, Donald E. Canfield, and the crew of the RV Jan Mayen for a successful Svalbard cruise. We are grateful to Kerstin Sahm and Friedrich Widdel for help during the isolation of the studied strains and for critical discussions and to Bo Thamdrup for help with the computer software.

This work was supported by the Max Planck Society, Germany.


    FOOTNOTES

* Corresponding author. Mailing address: Max Planck Institute for Marine Microbiology, Celsiusstr. 1, D-28359 Bremen, Germany. Phone: 49 421 2028 653. Fax: 49 421 2028 690. E-mail: cknoblau{at}mpi-bremen.de.


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Applied and Environmental Microbiology, September 1999, p. 4230-4233, Vol. 65, No. 9
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.


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