The sedimentary Mn cycle in Long Island Sound: Its role as intermediate oxidant and the influence of bioturbation, O 2 , and C org flux on diagenetic reaction balances

The potential importance of sedimentary Mn as a secondary oxidant and redox intermediate between O2 and Corg is often discounted in nearshore sediments. Study of the Mn cycle at 19 stations in Long Island Sound (LIS) demonstrates that sedimentary Mn can be a significant redox intermediate, accounting in many cases for 30-50% of the benthic O2 flux (annual mean - 40 + 35%). At some sites and times, the import of solid oxidant as Mn in suspended matter is also apparently greater than the dissolved O2 flux to the bottom. The relative importance of the Mn cycle as redox intermediate varies substantially both seasonally (summer > fall > spring > winter) and spatially as a function of biogenic reworking, Corg flux, and O2 concentration in the overlying water. During warmer seasons, the net flux of Mn++ from the bottom decreases ( -5-10x) generally from west to east, correlating directly with the benthic flux of planktonic debris and storage of residual Corg. Average fluxes are -0.003,0.43-0.94,2.2, and 0.43 mmol Mn/m2/d during winter, spring, summer, and fall respectively. Mn++ fluxes are relatively elevated during the spring bloom despite low temperatures. At most sites and times, surface sediments are enriched in excess Mn (4-17 kmol/g) above lithogenic background, with exponentially decreasing concentrations to 2-3 cm depth. A regular seasonal and spatial cycle of excess Mn occurs. Excess Mn inventories are often -5-10 tr,mol/cm2 but range from -0-25 umol/cm2. The highest inventories are found in mid LIS, in the transition area between high Corg flux and seasonally low O2 regions of the western Sound and the lower Corg flux, better oxygenated regions of central LIS. Excess Mn decreases at most sites following the spring plankton bloom and is lost entirely from westernmost sediments of highest Corg flux, several months before noticeable O2 depletion in overlying water. The bloom is a major factor in mobilization of metals into suspended matter and promotes lateral redistribution of Mn. Destratification and oxygenation of the water column in the fall results in the capture and reestablishment of excess sedimentary Mn in all regions of the Sound. Bioturbation transports Mn and Corg into anoxic sediment zones. When overlying water is well-oxygenated, the resulting Mn ++ is efficiently irreversibly adsorbed or reoxidized ( -SO-90%, during summerfall), closing the sedimentary Mn cycle and inhibiting net Mn ++ fluxes. The internal Mn cycle is therefore most important as an intermediate oxidant during warm periods of high bioturbation, well-oxygenated overlying water, and moderate Corg flux. S species apparently dominate the direct reduction of Mn.

[1]  S. Emerson,et al.  The oxidation state of manganese in surface sediments of the deep sea , 1984 .

[2]  M. L. Peterson,et al.  Biogeochemical processes affecting total arsenic and arsenic species distributions in an intermittently anoxic fjord , 1983 .

[3]  D. Heggie,et al.  Cobalt in pore waters of marine sediments , 1984, Nature.

[4]  H. Bokuniewicz,et al.  Estimates of sediment fluxes in Long Island Sound , 1991 .

[5]  A. C. Myers Summer and winter burrows of a mantis shrimp, Squilla empusa, in Narragansett Bay, Rhode Island (U.S.A.)☆ , 1979 .

[6]  D. Lovley Dissimilatory Fe(III) and Mn(IV) reduction , 1991, Microbiological reviews.

[7]  C. Hunt Variability in the benthic Mn flux in coastal marine ecosystems resulting from temperature and primary production , 1983 .

[8]  D. Rhoads,et al.  SEAFLOOR STABILITY IN CENTRAL LONG ISLAND SOUND: Part II. Biological Interactions And Their Potential Importance for Seafloor Erodibility , 1978 .

[9]  L. Balistrieri,et al.  The oxidation state of manganese in marine sediments and ferromanganese nodules , 1984 .

[10]  M. Bender,et al.  Manganese in seawater and the marine manganese balance , 1977 .

[11]  Per O.J. Hall,et al.  The effect of oxygen on release and uptake of cobalt, manganese, iron and phosphate at the sediment-water interface , 1986 .

[12]  J. Trefry,et al.  Manganese fluxes from Mississippi Delta sediments , 1982 .

[13]  R. Jahnke,et al.  Early diagenesis in differing depositional environments: The response of transition metals in pore water , 1990 .

[14]  L. Balistrieri,et al.  The surface chemistry of sediments from the Panama Basin: The influence of Mn oxides on metal adsorption , 1986 .

[15]  R. Aller,et al.  The Effects of Macrobenthos on Chemical Properties of Marine Sediment and Overlying Water , 1982 .

[16]  M. Bender,et al.  Does upward diffusion supply the excess manganese in pelagic sediments , 1971 .

[17]  E. Bonatti,et al.  Mobility of manganese in diagenesis of deep-sea sediments☆ , 1965 .

[18]  G. Billen,et al.  Behaviour of manganese in the Rhine and Scheldt estuaries. I. Physico-chemical aspects , 1979 .

[19]  A. C. Campbell,et al.  Manganese geochemistry in the Guaymas Basin, Gulf of California , 1988 .

[20]  R. Aller,et al.  Open-incubation, diffusion methods for measuring solute reaction rates in sediments , 1989 .

[21]  C. Reimers,et al.  Carbon fluxes and burial rates over the continental slope and rise off central California with impli , 1992 .

[22]  R. Aller,et al.  Diffusion coefficients in nearshore marine sediments1 , 1982 .

[23]  Charles A. Parker,et al.  Oxygen depletion in Long Island Sound: A historical perspective , 1991 .

[24]  N. Silverberg,et al.  Pathways of manganese in an open estuarine system , 1981 .

[25]  R. Aller,et al.  Complete oxidation of solid phase sulfides by manganese and bacteria in anoxic marine sediments , 1988 .

[26]  Influence of colonizing benthos on physical properties and chemical diagenesis of the estuarine seafloor , 1975 .

[27]  D. Canfield,et al.  The anaerobic degradation of organic matter in Danish coastal sediments: iron reduction, manganese reduction, and sulfate reduction. , 1993, Geochimica et cosmochimica acta.

[28]  R. Aller Diagenetic Processes Near the Sediment-Water Interface of Long Island Sound. I.: Decomposition and Nutrient Element Geochemistry (S, N, P) , 1980 .

[29]  A. Stone Microbial metabolites and the reductive dissolution of manganese oxides: Oxalate and pyruvate , 1987 .

[30]  D. Hammond,et al.  Early oxidation of organic matter in pelagic sediments of the eastern equatorial Atlantic: suboxic diagenesis , 1979 .

[31]  J. Mackin,et al.  Organic matter decomposition pathways and oxygen consumption in coastal marine sediments , 1989 .

[32]  W. E. Ricker,et al.  Computation and uses of central trend lines , 1984 .

[33]  K. Goto,et al.  Rapid colorimetric determination of manganese in waters containing iron , 1962 .

[34]  E. Jenne Controls on Mn, Fe, Co, Ni, Cu, and Zn Concentrations in Soils and Water: the Significant Role of Hydrous Mn and Fe Oxides , 1968 .

[35]  G. King Effects of added manganic and ferric oxides on sulfate reduction and sulfide oxidation in intertidal sediments , 1990 .

[36]  T. J. Hart Oceanography of Long Island Sound , 1960, Nature.

[37]  K. Nealson,et al.  Microbial reduction of manganese and iron: new approaches to carbon cycling , 1992, Applied and environmental microbiology.

[38]  G. R. Holdren,et al.  Model for the control of dissolved manganese in the interstitial waters of Chesapeake Bay , 1975 .

[39]  Cindy Lee,et al.  Spatial and temporal distributions of sedimentary chloropigments as indicators of benthic processes in Long Island Sound , 1994 .

[40]  C. Edwards,et al.  A note on the enumeration of manganese‐oxidizing bacteria in estuarine water and sediment samples , 1985 .

[41]  E. Sholkovitz,et al.  The Geochemistry of Rare Earth Elements in the Seasonally Anoxic Water Column and Porewaters of Chesapeake Bay , 1992 .

[42]  J. Kelly,et al.  Manganese cycling in coastal regions: response to eutrophication , 1988 .

[43]  Li Yuan-hui,et al.  Diffusion of ions in sea water and in deep-sea sediments , 1974 .

[44]  B. Tebo,et al.  Manganese ii oxidation in the suboxic zone of the black sea , 1991 .

[45]  E. Grill The effect of sediment-water exchange on manganese deposition and nodule growth in Jervis Inlet, British Columbia , 1978 .

[46]  O. Bricker,et al.  Oxidation effect on the analysis of iron in the interstitial water of recent anoxic sediments , 1974, Nature.

[47]  K. Turekian,et al.  Effects of biological sediment mixing on the210Pb chronology and trace metal distribution in a Long Island Sound sediment core , 1979 .

[48]  W. Baeyens,et al.  Tight coupling between enrichment of iron and manganese in North Sea suspended matter and sedimentary redox processes: Evidence for seasonal variability , 1989 .

[49]  B. L. Welsh,et al.  Mechanisms controlling summertime oxygen depletion in western Long Island Sound , 1991 .

[50]  T. Church Marine Chemistry in the Coastal Environment , 1975 .

[51]  R. Aller,et al.  Spatial and temporal patterns of dissolved ammonium, manganese and silica fluxes from bottom sediments of Long Island Sound, U.S.A. , 1981 .

[52]  N. Revsbech In Situ Measurement of Oxygen Profiles of Sediments by use of Oxygen Microelectrodes , 1983 .

[53]  K. Turekian The fate of metals in the oceans , 1977 .

[54]  R. Chester,et al.  A chemical technique for the separation of ferro-manganese minerals, carbonate minerals and adsorbed trace elements from pelagic sediments , 1967 .

[55]  R. Aller,et al.  Bioturbation and manganese cycling in hemipelagic sediments , 1990, Philosophical Transactions of the Royal Society of London. Series A, Mathematical and Physical Sciences.

[56]  J. Chanton,et al.  Biogeochemical cycling in an organic-rich coastal marine basin. 7. Sulfur mass balance, oxygen uptake and sulfide retention , 1987 .

[57]  W. Balzer,et al.  Early diagenesis of trace metals used as an indicator of past productivity changes in coastal sediments , 1993 .

[58]  B. Sundby,et al.  Manganese fluxes in the benthic boundary layer , 1985 .

[59]  W. Peterson The Effects of Seasonal Variations in Stratification on Plankton Dynamics in Long Island Sound , 1986 .

[60]  C. Martens,et al.  Biogeochemical cycling in an organic-rich coastal marine basin—I. Methane sediment-water exchange processes , 1980 .

[61]  R. Aller,et al.  Tracking particle-associated processes in nearshore environments by use of 234Th/238U disequilibrium , 1980 .

[62]  D. Burdige,et al.  Determination of bacterial manganese oxidation rates in sediments using an in-situ dialysis technique I. Laboratory studies , 1983 .

[63]  H. Edenborn,et al.  Bacterial contribution to manganese oxidation in a deep coastal sediment , 1985 .

[64]  P. McCall SPATIAL-TEMPORAL DISTRIBUTIONS OF LONG ISLAND SOUND INFAUNA: THE ROLE OF BOTTOM DISTURBANCE IN A NEARSHORE MARINE HABITAT , 1978 .

[65]  B. Jørgensen The sulfur cycle of a coastal marine sediment (Limfjorden, Denmark)1 , 1977 .

[66]  W. Martin,et al.  The measurement of sediment irrigation rates: A comparison of the Br− tracer and 222Rn/226Ra disequilibrium techniques , 1992 .

[67]  R. Berner,et al.  Sulfate reduction, diffusion, and bioturbation in Long Island Sound sediments; report of the FOAM Group , 1977 .

[68]  L. Eugene Cronin,et al.  Chemistry, biology, and the estuarine system , 1975 .