Abstract:The pattern of sulfur transformation in peat across the Everglades basin indicates that pyrite formation in organic-rich swamps depends on the use of organic oxysulfur compounds in dissimilatory respiration by sulfur-reducing bacteria. This paragenesis explains the primary distribution of sulfur compounds in low-sulfur coals and possibly in most coals and many organic-rich soils and sediments. It also accounts for the occurrence of framboidal pyrite bound in fossil tissue in coal and sediments.
“…Although the analytical methods used by Altschuler et al (1983) were substantially different from ours, many of the methods used by Casagrande et al ( 1977) were similar. Casagrande et al removed SOa2--S (using 0.1 M LiCl) and SO-S (using CHC13) before dividing their samples and subjecting one subsample to HI reduction and another subsample to the Zn-HCl procedure.…”
Section: Biogeochemical Transformationsmentioning
confidence: 99%
“…Values are means + SE. For comparison, data are also shown for freshwater peat from the Okefenokee Swamp (Casagrande et al 1977; values are the means of the Minnie's Lake and Chesser Prairie sites) and from the Florida Everglades (Altschuler et al 1983; values are the means of core 2, 20-25 cm, and core 8, 14-19 cm). of S from all of the inorganic S compounds except So (68% recovery) and FeS, (2% recovery).…”
Section: Biogeochemical Transformationsmentioning
confidence: 99%
“…In both salt marshes and coastal marine sediments, the cycling of sulfur and carbon is linked by the process of bacterial sulfate reduction, which may account for a considerable proportion of organic matter mineralization (Howarth and Teal 1979;Skyring et al 1978;Jorgensen 1982). Sulfur diagenesis in both freshwater and marine peats bears on the origin of sulfur in coal (Casagrande et al 1977;Altschuler et al 1983). In addition, the phenomenon of acid precipitation has led to the investigation of sulfur cycling in freshwater wetland (Gorham et al 1984), freshwater lake Kelly et al 1982;Mitchell et al 1984), terrestrial (Johnson et al 1982;Fitzgerald et al 1982;McFee 1983), and agronomic (Olson 1983;Mortvedt 1983) ecosystems.…”
Section: Biogeochemical Transformationsmentioning
confidence: 99%
“…Data from the Okefenokee Swamp (Casagrande et al 1977) and the Florida Everglades (Altschuler et al 1983) in Table 3 were obtained from the analysis of dried peat samples. Although the three sites differ considerably in total S concentration, in all sites most of the S (between 76 and 94%) is present in an organic form.…”
The specificity and efficiency of procedures for fractionating total S into inorganic and organic constituents were evaluated by analyzing a series of known standards. Acid volatilization was specific for FeS. Chromium reduction recovered over 90% of the S from FeS, S0, and FeS2. Acetone extraction followed by chromium reduction of the filtrate was specific for S0. Hydriodic acid reduction recovered > 90% of the S from FeS, SO42−, and p‐nitrophenyl sulfate, an organic aryl ester sulfate analog. The Zn‐HCl reduction procedure is of questionable value, only partially recovering S from SO42−, S0, and FeS2. None of these procedures affected l‐methionine. Analyses were performed on both moist and oven‐dried peat from Big Run Bog, West Virginia. Oven‐drying of peat samples increased estimates of ester sulfate S and SO42−‐S and decreased estimates of carbon‐bonded S, which was calculated by difference.
“…Although the analytical methods used by Altschuler et al (1983) were substantially different from ours, many of the methods used by Casagrande et al ( 1977) were similar. Casagrande et al removed SOa2--S (using 0.1 M LiCl) and SO-S (using CHC13) before dividing their samples and subjecting one subsample to HI reduction and another subsample to the Zn-HCl procedure.…”
Section: Biogeochemical Transformationsmentioning
confidence: 99%
“…Values are means + SE. For comparison, data are also shown for freshwater peat from the Okefenokee Swamp (Casagrande et al 1977; values are the means of the Minnie's Lake and Chesser Prairie sites) and from the Florida Everglades (Altschuler et al 1983; values are the means of core 2, 20-25 cm, and core 8, 14-19 cm). of S from all of the inorganic S compounds except So (68% recovery) and FeS, (2% recovery).…”
Section: Biogeochemical Transformationsmentioning
confidence: 99%
“…In both salt marshes and coastal marine sediments, the cycling of sulfur and carbon is linked by the process of bacterial sulfate reduction, which may account for a considerable proportion of organic matter mineralization (Howarth and Teal 1979;Skyring et al 1978;Jorgensen 1982). Sulfur diagenesis in both freshwater and marine peats bears on the origin of sulfur in coal (Casagrande et al 1977;Altschuler et al 1983). In addition, the phenomenon of acid precipitation has led to the investigation of sulfur cycling in freshwater wetland (Gorham et al 1984), freshwater lake Kelly et al 1982;Mitchell et al 1984), terrestrial (Johnson et al 1982;Fitzgerald et al 1982;McFee 1983), and agronomic (Olson 1983;Mortvedt 1983) ecosystems.…”
Section: Biogeochemical Transformationsmentioning
confidence: 99%
“…Data from the Okefenokee Swamp (Casagrande et al 1977) and the Florida Everglades (Altschuler et al 1983) in Table 3 were obtained from the analysis of dried peat samples. Although the three sites differ considerably in total S concentration, in all sites most of the S (between 76 and 94%) is present in an organic form.…”
The specificity and efficiency of procedures for fractionating total S into inorganic and organic constituents were evaluated by analyzing a series of known standards. Acid volatilization was specific for FeS. Chromium reduction recovered over 90% of the S from FeS, S0, and FeS2. Acetone extraction followed by chromium reduction of the filtrate was specific for S0. Hydriodic acid reduction recovered > 90% of the S from FeS, SO42−, and p‐nitrophenyl sulfate, an organic aryl ester sulfate analog. The Zn‐HCl reduction procedure is of questionable value, only partially recovering S from SO42−, S0, and FeS2. None of these procedures affected l‐methionine. Analyses were performed on both moist and oven‐dried peat from Big Run Bog, West Virginia. Oven‐drying of peat samples increased estimates of ester sulfate S and SO42−‐S and decreased estimates of carbon‐bonded S, which was calculated by difference.
“…Mitchell et al (198 1,1984) have shown that organic S usually constituted >80% of the total S in the sediments of three New York lakes. King and Klug (1982) found in hypereutrophic Wintergreen Lake sediments, where low redox conditions and high carbon levels would seem to favor pyrite formation, that organic S was still >80% of total S and that pyrite was < 10% oftotal S. Altschuler et al (1983) found organic S predominant in peat deposits across the Everglades basin and indicated that pyritic S formation in this reduced substrate was dependent on the use of organic S compounds in dissimilatory respiration by S-reducing bacteria. Mitchell et al (1984) and Landers and Mitchell (unpubl.…”
Organic and inorganic sulfur constituents in streams, the water column, seston, and sediments of an oligotrophic Adirondack lake were measured for 2 years (1981)(1982)(1983). Soluble organic S constituents (C-bonded S and ester sulfate) were l-18% of total S in streams, the water column, and lake outlet. Seston S (0.3-1.2% dry mass) in South Lake consisted of ester sulfate (44-59%), C-bonded S (32-43%), sulfate (10-l 6%), and nonsulfate inorganic S (~2%). Rates of S deposition measured in sediment traps were highest after spring turnover. The organic matter content (52-81% dry mass) of traps at 5, 8, and 15.5 m showed no significant differences.Net mineralization of seston inputs was 26% based on mass balance calculations, with 43% of the ester sulfate input mineralized. Because most ofthe S input to the sediments was not mineralized, organic S accumulated and constituted the major (74% of total S) S component of the sediment.Most studies of sulfur cycling in freshwater systems have focused on the dynamics of inorganic sulfate and sulfide for which transformations are regulated by redox reactions (Stuiver 1967; Berner 197 1; Cook 198 1). Organic S in freshwater lake sediments has been less studied. Hesse (1958) found that >90% of the total S in the sediments of Lake Victoria was in organic form. Nriagu (1968) found that organic S composed most of the total S in marl deposits and a small amount of total S in sludge sediments in Lake Mendota. Mitchell et al. (198 1,1984) have shown that organic S usually constituted >80% of the total S in the sediments of three New York lakes. King and Klug (1982) found in hypereutrophic Wintergreen Lake sediments, where low redox conditions and high carbon levels would seem to favor pyrite formation, that organic S was still >80% of total S and that pyrite was < 10% oftotal S. Altschuler et al. (1983) found organic S predominant in peat deposits across the Everglades basin and indicated that pyritic S formation in this reduced substrate was dependent on the use of organic S compounds in dissimilatory respiration by S-reducing bacteria. Mitchell et al. (1984) and Landers and Mitchell (unpubl. data) indicated that sed-1 Present address: Department of Forestry, Univ. Illinois, Urbana 6 180 1.iment S constituents and transformations show considerable temporal changes and that 35S as sulfate was rapidly converted into organic forms. For South Lake, on average 50 and 12% of the added 35S was transformed into ester sulfate and refractory S (C-bonded S and pyritic S) and 36% remained as sulfate (Landers and Mitchell unpubl. data). Less than 2% of the 35S was found as reduced, volatile inorganic S in their sediment core experiments. The uptake of 35S as sulfate was also shown to have significant temporal changes and differences among study lakes (Landers and Mitchell unpubl. data).Seston is the major contributor of material to sediments in most lakes. King and Klug (1982) found that seston S was mostly ester sulfate and C-bonded S. This may indicate that sedimented organic S is...
Sediments recovered at Integrated Ocean Drilling Program (IODP) Site C0020, in a fore‐arc basin offshore Shimokita Peninsula, Japan, include numerous coal beds (0.3–7 m thick) that are associated with a transition from a terrestrial to marine depositional environment. Within the primary coal‐bearing unit (∼2 km depth below seafloor) there are sharp increases in magnetic susceptibility in close proximity to the coal beds, superimposed on a background of consistently low magnetic susceptibility throughout the remainder of the recovered stratigraphic sequence. We investigate the source of the magnetic susceptibility variability and characterize the dominant magnetic assemblage throughout the entire cored record, using isothermal remanent magnetization (IRM), thermal demagnetization, anhysteretic remanent magnetization (ARM), iron speciation, and iron isotopes. Magnetic mineral assemblages in all samples are dominated by very low‐coercivity minerals with unblocking temperatures between 350 and 580°C that are interpreted to be magnetite. Samples with lower unblocking temperatures (300–400°C), higher ARM, higher‐frequency dependence, and isotopically heavy δ56Fe across a range of lithologies in the coal‐bearing unit (between 1925 and 1995 mbsf) indicate the presence of fine‐grained authigenic magnetite. We suggest that iron‐reducing bacteria facilitated the production of fine‐grained magnetite within the coal‐bearing unit during burial and interaction with pore waters. The coal/peat acted as a source of electron donors during burial, mediated by humic acids, to supply iron‐reducing bacteria in the surrounding siliciclastic sediments. These results indicate that coal‐bearing sediments may play an important role in iron cycling in subsiding peat environments and if buried deeply through time, within the subsequent deep biosphere.
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