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16 The sulfur cycle in marine sediments. The cycle is energetically driven by deposited organic material and methane, both of which are used by sulfate reducing bacteria to produce H S. Much of the H S reacts chemically with 2 2 iron (oxyhydr)oxides to form FeS and a range of intermediate oxidation states including S 0 and FeS . The further 2 oxidation of these species back to sulfate is mediated by the vertical conveyer belt of bioturbation caused by burrowing macrofauna. Reoxidation of the solid phase sulfur species to sulfate at the sediment surface may be by oxygen, nitrate or manganese oxide. The same conveyer belt brings the oxidized iron back down towards the sulfide production zone where it reacts with further H S. A highly efficient recycling of sulfur is thereby achieved. (From 2 Jørgensen and Nelson 2004). 

16 The sulfur cycle in marine sediments. The cycle is energetically driven by deposited organic material and methane, both of which are used by sulfate reducing bacteria to produce H S. Much of the H S reacts chemically with 2 2 iron (oxyhydr)oxides to form FeS and a range of intermediate oxidation states including S 0 and FeS . The further 2 oxidation of these species back to sulfate is mediated by the vertical conveyer belt of bioturbation caused by burrowing macrofauna. Reoxidation of the solid phase sulfur species to sulfate at the sediment surface may be by oxygen, nitrate or manganese oxide. The same conveyer belt brings the oxidized iron back down towards the sulfide production zone where it reacts with further H S. A highly efficient recycling of sulfur is thereby achieved. (From 2 Jørgensen and Nelson 2004). 

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This chapter deals with the biogeochemical transformations of sulfur and methane in marine sediments during early diagenesis. The term ‘early diagenesis’ refers to the whole range of postdepositional processes that take place in aquatic sediments and are coupled either directly or indirectly to the degradation of organic matter. We focus on the pro...

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... sediments, the production of H S may 2 exceed the availability of reactive metal oxides and H S accumulates in the pore water (see Fig. 8.6, 2 8.12, 8.13, and 8.17). The H S diffuses upwards 2 along a concentration gradient that generally reaches zero at the bottom of the suboxic zone. Concurrently, the H S reacts with buried iron 2 oxides to form FeS, FeS , S 0 and a number of other 2 solid or dissolved intermediate products. Once the reduced sulfur is bound in the solid phase, e.g. as pyrite, its further oxidation depends on a slow reaction with further Fe(III) species or its transport up to near-surface layers with oxidants of higher redox potential. Pyrite transport in near-surface sediments generally takes place through the conveyer belt of bioturbation whereby burrowing macrofauna mix the sediment or directly move sediment particles as part of their deposit feeding behavior (Fig. 8.16). As the pyrite reaches up into the suboxic zone it may react with oxidants such as oxygen or manganese oxide and be converted into sulfate and iron oxides (or iron (oxyhydr)oxides). The iron oxides are in turn transported downwards through the same conveyer belt and thereby become available for further binding of sulfide and pyrite formation. The pyrite oxidation by manganese oxide has been implied from chemical profiles (Canfield et al. 1993) and demonstrated directly through experiments (Schippers and Jørgensen 2001, 2002). The process is interesting in that it involves the reaction between two mineral phases in the sediment that must be in close proximity for the oxidation to proceed. The initial reaction is purely chemical and was proposed to occur by a Fe(II)/Fe(III)-shuttle in the pore fluid between the mineral surfaces of FeS and MnO . The immediate 2 2 products of the oxidation are thiosulfate and polythionates. These can be further oxidized to sulfate by manganese reducing bacteria, ...
Context 2
... reactions do not cause a net oxidation of the sulfur species, yet they have a key function in sulfide oxidation. Disproportionation provides a shunt in the sulfur cycle whereby the H S formed by this reaction may be 2 oxidized again to the same sulfur intermediate by metal oxides. Manganese oxide, for example, rapidly oxidizes H S to S 0 without participation of 2 bacteria, but does not oxidize the S 0 further to sulfate (Burdige 1993). The elemental sulfur may, however, be disproportionated (Eq. 8.19) whereby a fourth of it is oxidized completely to sulfate while the remaining three fourths return to the sulfide pool. Through repeated partial oxidation of sulfide to elemental sulfur with manganese oxide and subsequent disproportionation of the elemental sulfur to sulfate and sulfide a complete oxidation of sulfide to sulfate by manganese oxide may be achieved (Fig. 8.16; Thamdrup et al. 1993; Böttcher and Thamdrup ...

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... MOBs were consistently present within the top decimeter of surface sediments (i.e., the section that we could target at Norskebanken and Hinlopen Trough). However, O 2 in marine sediments is typically consumed within the upper millimeters of the sediment surface (Jørgensen and Kasten, 2006). Unless that bio−irrigation through larger marine benthic organisms introduces O 2 to deeper sediment layers (Kristensen, 2000;Dauwe et al., 2001;Niemann et al., 2006), or that some of the detected MOBs can utilize electron acceptors other than O 2 (Kits et al., 2015;Martinez-Cruz et al., 2017;Su et al., 2023), it seems likely that MOBs in subsurface sediments at Norskebanken and Hinlopen Trough are mostly dormant in situ. ...
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... The continental margin is the active terrestrial-ocean interface that serves as a primary location for the biochemical and sedimentary cycling of organic carbon (OC), nitrogen (N), and sulfur (S) (Berner, 1982;Jørgensen and Kasten, 2006;Hu et al., 2011;DeLaune and White, 2012;Hu et al., 2014;Jørgensen et al., 2019;Chen et al., 2021). Dynamic physicochemical reactions along continental margins create complex OC-N-S cycles that can be affected by local climate; however, the mechanistic link of climate change to the OC-N-S cycles is not well understood (Mcleod et al., 2011;Liu Q. et al., 2018;Liu X. T., et al., 2018;Sun et al., 2020;Liu X. T., et al., 2021;Wang et al., 2021;Zhao et al., 2021;Liu et al., 2023). ...
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... This kind of behaviour was also seen in the KRE, where vertical profiles of dissolved Mn and Fe showed a sharp rise below the SWI across the estuary, but the intensity of mobilisation differed among the sites. In cores K2, K4, and K5, the increase of the dissolved Fe was at a lower depth (2-4 cm) than dissolved Mn (0-2 cm), which is consistent with the ideal redox sequence of the estuarine sediments [75]. At sites K1 and K3, however, the redox zones were more compressed, resulting in the Mn and Fe peaks in the same layer, just below the SWI (0-2 cm). ...
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... Determining the redox conditions in the sediments is essential to reconstruct metal speciation and mobility as well as biogeochemical processes. The redox zonation of marine sediments is dictated by conditions in the bottom waters, the magnitude and rates of organic matter mineralization and biological activity reworking the surface sediment (Jørgensen and Kasten, 2006). In general, the uppermost sediment layer is rich in oxygen diffusing from the overlying water column. ...
... Microorganisms rapidly consume the oxygen as an electron acceptor in the process of organic matter oxidation. Below the oxic zone, less thermodynamically favourable compounds (yielding lower energy gain for the microbes) are consumed in the following order: nitrate (NO 3 − ), manganese (oxy)hydroxides, iron (oxy)hydroxides and sulfate (SO 4 2− ) (Jørgensen and Kasten, 2006). This succession corresponds to a steep decrease in redox potential and the pH, initially steeply decreasing within the oxic zone as a result of aerobic respiration and reoxidation of reduced species, tends to increase with depth due to anaerobic alkalinity production (Silburn et al., 2017). ...
... This is visible in Fig. 4, where Mn bulges are located immediately above the Fe ones. By definition, the suboxic zone is followed by the anoxic zone of sulfate reduction (Jørgensen and Kasten, 2006). Consistent with the expected zonation, in our cores, we observe sulfate starting to decline below the Mn and Fe reduction zones. ...
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... 931The surface sediments at these sites are composed of silty 932 clay, clayey silt, and sandy silt( Figure 1). Sediment com-933 position was different between the sites, but the TOC/TS 934 contents remained below the predicted Holocene satura-935 tion line( Figure 5 F), indicating sulfate mineralization pro-936 cesses( Berner, 1982 ;Jørgensen and Kasten, 2006 ). Most 937 sites showed Hg profiles with enhanced contents at 10 and 938 20 cmbsf, and thus a relatively continuous sedimentation 939 with little disturbance. ...
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The present study aims to understand the impact of submarine groundwater discharge (SGD) on a coastal area with different lithology and degrees of SGD. Sampling cam- paigns took place in Puck Bay and the Gulf of Gdansk, southern Baltic Sea encompassing years between 2009 and 2021. The methodological approach combined geophysical characterization of the surface sediments with detailed spatial and temporal (isotope) biogeochemical investigations of pore and surface waters, and was supported by nearshore groundwater and river surveys. Acoustic investigations identified areas of disturbance that may indicate zones of preferential SGD release. The composition of porewater and the differences in the bay’s surface waters disclosed SGD as common phenomenon in the study area. Regional SGD was estimated through a radium mass balance. Local estimation of SGD, based on porewater profiles, revealed highest SGD fluxes at the sandy shoreline, but relatively low elemental fluxes. Though SGD was low at the muddy sites corresponding elemental fluxes of nutrients and dissolved carbon exceeded those determined at the sandy sites due to intense diagenesis in the top sediments. SGD appears to be sourced from different freshwater endmembers; however, diagenesis in surface sediments substantially modified the composition of the mixed solutions that are finally discharged to coastal waters. Overall, this study provides a better understanding of the SGD dynamics in the region by a multi-approach and emphasizes the need to understand the processes occurring at the sediment-water interface when estimating SGD.
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... The authors did not directly include information derived from 35 S-radiotracer measurements of sulfate reduction. They concluded that the earlier global estimate suggested by Jørgensen and Kasten (2006) of 75 Tmol SO 4 2yr − 1 was too high and was not realistic. ...
... This conclusion motivated us to re-evaluate these global numbers. The first, highly embarrassing observation was that the 75 Tmol SO 4 2yr − 1 published by Jørgensen and Kasten (2006) should read 65 Tmol SO 4 2yr − 1 , as it was taken directly from Canfield et al. (2005). In the Canfield et al. (2005) summary, sulfate reduction rates were taken from 35 S-radiotracer experiments on marine sediments derived from the literature. ...
... Rates were binned into regions (salt marshes, mangroves, etc.) and water depths, averaged, and then extrapolated to the global ocean based on the areas represented by these different regions. The global number of Canfield et al. (2005) and Jørgensen and Kasten (2006) included salt marshes, mangroves, seagrasses, macroalgae and coral reefs. The number by Bowles et al. (2014) did not, and the two global estimates are therefore not directly comparable. ...
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... In anoxic sediments, the carbon cycle is tightly coupled to sulfur/methane cycles (Jørgensen and Kasten 2006). The present dataset and model can be used to understand the impact of flood deposition on these coupled cycles. ...
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At the land-sea interface, the benthic carbon cycle is strongly influenced by the export of terrigenous particulate material across the river-ocean continuum. Episodic flood events delivering massive sedimentary materials can occur, but their short-term impact on carbon cycling is poorly understood. In this paper, we use a coupled data-model approach to estimate the temporal variations of sediment-water fluxes, biogeochemical pathways and their reaction rates during these abrupt phenomena. We studied one episodic depositional event in the vicinity of the Rhône River mouth (NW Mediterranean Sea) during the fall-winter of 2021–2022. The distribution of dissolved inorganic carbon (DIC), sulfate (SO42−) and methane (CH4) were measured in sediment porewater collected every 2 weeks before and after the deposition of a 25 cm sediment layer during the main winter flood event. Significant changes in the distribution of DIC, SO42− and CH4, concentrations were observed in the sediment porewaters. The use of an early diagenetic model (FESDIA) to calculate biogeochemical reaction rates and fluxes revealed that this type of flooding event can increase the total organic carbon mineralization rate in the sediment by 75 % a few days after deposition, essentially by increasing the sulfate reduction contribution to total mineralization relative to non-flood depositional period. It predicts a short-term decrease of the DIC flux out of the sediment from 100 to 55 mmol m−2 d−1 after the deposition of the new sediment layer with a longer-term increase by 4 %, therefore implying an initial internal storage of DIC in the newly deposited layer and a slow release over relaxation of the system. Furthermore, examination of the stoichiometric ratios of DIC and SO42− as well as model output over this five-months window shows a decoupling between the two modes of sulfate reduction following the deposition – organoclastic sulfate reduction (OSR) intensified in the newly deposited layer below the sediment surface, whereas anaerobic oxidation of methane (AOM) intensified at depth below the former buried surface. This depth-wise bifurcation of both pathways of sulfate reduction in the sediment column is clearly related to the deepening of the sulfate-methane transition zone (SMTZ) by 25 cm after the flood deposition. Our findings highlight the significance of short-term transient biogeochemical processes at the seafloor and provide new insights on the benthic carbon cycle in the coastal ocean.