Dissimilatory sulfate reduction and methane production in Gotland Deep sediments (Baltic Sea) during a transition period from oxic to anoxic bottom water (1993-1996)

During a transition period from oxic to anoxic conditions in the bottom water, rates of sulfate reduction and methane production, methane fluxes, as well as concentration profiles of sulfate, sulfide and methane were measured in sediments at a central site of the Gotland Deep (Stn AL 93, 241 m depth), which is regarded as representative for the deepest part of this basin. During this period from 1993 to 1996 oxic conditions in the bottom water prevailed from spring 1994 until summer 1995 with oxygen concentrations decreasing progressively with time. In the sediments methane production occurred primarily in layers below 1 m depth and flux rates of methane to the sediment surface were characterized by a steep concentration gradient from approx. 5 mM at 4 m depth to values close to 30 μM at the surface, determined by diffusion processes and anaerobic oxidation of methane. Both processes were independent of changes at the sediment surface. Differences in the flux rates of methane between the deeper part with a mean value of 259 μmol m-2 d-1 and the upper layers with a mean of 47.7 μmol m-2 d-1 indicate that a considerable proportion of the methane is oxidized within the anoxic horizon of the sediment (71 to 86% in the layer from 40 to 70 cm). Low rates of methane production found within the top 20 cm of the sediment during periods of oxic bottom water increased after depletion of oxygen and resulted in a clear maximum of the methane concentration in the top 2 cm. Sulfate concentrations declined exponentially from values of 11.5 mM in June 1994 and 8.5 mM in October 1995 at the sediment surface to values of 2.5 mM at 20 cm depth and of less than 0.5 mM at 50 to 60 cm depth. High sulfate reduction rates (150 to 250 nmol cm-3 d-1) in the upper part of the sediment (8 to 13 cm) coincided with maxima of sulfide concentrations. During the time period of this investigation an increase of maximum sulfide concentrations in the sediment from 1 to 10 mM was measured together with decreasing oxygen concentrations in the deep water. At the same time sulfate reduction established a small but distinct maximum at the top layer of the sediment (0 to 2 cm). The relative importance of sulfate reduction and methanogenesis in the carbon budget of the Gotland Deep sediments is calculated on the basis of the actual measurements.

[1]  B. Jørgensen,et al.  Measurement of bacterial sulfate reduction in sediments: Evaluation of a single-step chromium reduction method , 1989 .

[2]  D. Postma,et al.  Pyrite formation in anoxic environments of the Baltic , 1988 .

[3]  J. Fritz,et al.  Anion chromatography with low-conductivity eluents , 1979 .

[4]  T. Blackburn,et al.  Seasonal Rates of Methane Oxidation in Anoxic Marine Sediments , 1981, Applied and environmental microbiology.

[5]  Bo Barker Jørgensen,et al.  Anaerobic methane oxidation rates at the sulfate‐methane transition in marine sediments from Kattegat and Skagerrak (Denmark) , 1985 .

[6]  Tori M. Hoehler,et al.  Field and laboratory studies of methane oxidation in an anoxic marine sediment: Evidence for a methanogen‐sulfate reducer consortium , 1994 .

[7]  T. D. Brock,et al.  Electron flow via sulfate reduction and methanogenesis in the anaerobic hypolimnion of Lake Mendota1 , 1982 .

[8]  I. Brettar,et al.  Denitrification in the Central Baltic: evidence for H2S-oxidation as motor of denitrification at the oxic-anoxic interface , 1991 .

[9]  B. Namsaraev,et al.  Bacterial methanogenesis in holocene sediments of the Baltic sea , 1981 .

[10]  R. Y. Morita,et al.  Field Observations of Methane Concentrations and Oxidation Rates in the Southeastern Bering Sea , 1982, Applied and environmental microbiology.

[11]  A comparison of methods for the quantification of bacterial sulfate reduction in coastal marine sediments , 1978 .

[12]  B. Jørgensen,et al.  Pathways and Microbiology of Thiosulfate Transformations and Sulfate Reduction in a Marine Sediment (Kattegat, Denmark) , 1991, Applied and environmental microbiology.

[13]  B. Jørgensen,et al.  Sulfate reduction and the formation of 35S-labeled FeS, FeS2, and S0 in coastal marine sediments , 1989 .

[14]  C. Hoede,et al.  Theoretical, experimental and field studies concerning molecular diffusion of radioisotopes in sediments and suspended solid particles of the sea Part A: Theories and mathematical calculations , 1967 .

[15]  G. E. Fogg,et al.  Methods for the Study of Marine Benthos. , 1972 .

[16]  J. Imhoff,et al.  The distribution of methane and hydrogen sulfide in basin sediments of the central and southern Baltic Sea , 1998 .

[17]  R. Schmaljohann Methane dynamics in the sediment and water column of Kiel Harbour (Baltic Sea) , 1996 .

[18]  B. Jørgensen,et al.  Oxygen uptake, bacterial distribution, and carbon-nitrogen-sulfur cycling in sediments from the baltic sea - North sea transition , 1989 .

[19]  Bess B. Ward,et al.  Black Sea methane geochemistry , 1991 .

[20]  R. Berner,et al.  The role of sedimentary organic matter in bacterial sulfate reduction: The G model tested1 , 1984 .

[21]  T. Blackburn,et al.  Anaerobic mineralization in marine sediments from the Baltic Sea-North Sea transition , 1990 .

[22]  W. Reeburgh Anaerobic methane oxidation: Rate depth distributions in Skan Bay sediments , 1980 .

[23]  D. M. Ward,et al.  Interactions between methanogenic and sulfate-reducing bacteria in sediments , 1985 .

[24]  J. Sahores DIFFUSION OF LIGHT PARAFFIN HYDROCARBONS IN WATER FROM 2°C TO 80°C , 1970 .

[25]  A. Devol Methane oxidation rates in the anaerobic sediments of Saanich Inlet1 , 1983 .

[26]  W. Reeburgh,et al.  Microbial methane consumption reactions and their effect on methane distributions in freshwater and marine environments1 , 1977 .

[27]  Robert A. Berner,et al.  An idealized model of dissolved sulfate distribution in recent sediments , 1964 .

[28]  G. W. Skyring,et al.  Sulfate reduction in coastal ecosystems , 1987 .