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Sulfide in sediments

Kvenvolden KA, Rapp JB, Hostettler FD, Morton JL, King JD, Claypool GE, Petroleum associated with polymetallic sulfide in sediment from Gorda Ridge, Science 234 1231-1234, 1986. [Pg.124]

FeOOH) indicated that a Clostridium species released 55% of the coprecipitated nickel after 40 hours. Similarly, precipitated nickel sulfides in sediment can be mobilized through sulfur oxidation by Thiobacilli (Wood 1987). In this case, the oxidized sulfur may produce H2SO4 and decrease the pH. [Pg.191]

The strong coupling between sulfur and iron chemistry becomes obvious in this example. Conservation of alkalinity within the system is achieved only if the sulfide formed is prevented from reoxidation, a process that would restore the acidity. Prevention of reoxidation occurs through the ultimate storage of sulfide in sediments, either as organic sulfur or as iron sulfides (12, 13). The overall reaction of pyrite formation proceeds via formation of FeS ... [Pg.372]

Thus highly anoxic waters are commonly sources of hydrogen sulfide, H2S, from sulfate reduction and of methane (marsh gas). The formation of sulfide in sediments has led to precipitation of metal sulfides over geological time, causing accumulations of sulfide minerals of many elements, e.g. PbS, ZnS, HgS, etc. [Pg.335]

Leventhal J. S. (1995) Carbon-sulfur plots to show diagenetic and epigenetic sulfidation in sediments. Geochim. Cosmochim. Acta 59, 1207-1211. [Pg.3618]

If metals, particularly iron, are not available to precipitate the biogenic sulfide, then dissolved sulfide builds up in the pore waters and may even reach toxic levels. When iron is present the dissolved sulfide is significantly lower in concentration. The concentration profiles for dissolved sulfide in sediments often show a depletion in the upper layers and a maximum at a depth of a meter or less. The depletion is interpreted by Goldhaber and Kaplan (1974) to reflect reactions between iron oxide and dissolved sulfide to yield iron sulfides. As a consequence of different reactivities of iron oxides to aqueous sulfide, a depth may be reached where the sulfide production rate exceeds removal as iron sulfide. Volkov et al. (1972) reported that, in sediments off the Japan Depression, the free hydrogen sulfide concentration reaches as high as 150 mg h which is roughly 50% higher than that found in the Black Sea and is comparable to the maximum concentration observed at Saanich Inlet, British Columbia, by Nissenbaum et al. (1972). The... [Pg.341]

Wang, F. and Chapman, P.M. (1999) Biological implications of sulfide in sediment - a review focusing on sediment toxicity. Environ. Toxicol. Chem., 16, 2526-2532. [Pg.162]

Apart from iron, the availability of sulfate can also limit the production of iron sulfides in sediments, once the rate of sulfate consumption exceeds the diffusive supply, especially in environments of rapid sediment accumulation. However, the measured sulfate concentrations... [Pg.451]

As is the case with assessments of the toxicity of dissolved trace metals, the development of sediment quality criteria (SQC) must be based on the fraction of sediment-associated metal that is bioavailable. Bulk sediments consist of a variety of phases including sediment solids in the silt and clay size fractions, and sediment pore water. Swartz et al. (1985) demonstrated that the bioavailable fraction of cadmium in sediments is correlated with interstitial water cadmium concentrations. More recent work (e.g., Di Toro et al, 1990 Allen et al., 1993 Hansen et al, 1996 Ankley et ai, 1996, and references therein) has demonstrated that the interstitial water concentrations of a suite of trace metals is regulated by an extractable fraction of iron sulfides. [Pg.400]

The role of iron sulfides in regulating sediment interstitial water concentrations is shown by the following reactions (Di Toro et ai, 1990) ... [Pg.400]

Figure 15-12 is a schematic illustration of a technique known as acid volatile sulfides/ simultaneously extracted metals analysis (AVS/SEM). Briefly, a strong acid is added to a sediment sample to release the sediment-associated sulfides, acid volatile sulfides, which are analyzed by a cold-acid purge-and-trap technique (e.g., Allen et ai, 1993). The assumption shown in Fig. 15-12 is that the sulfides are present in the sediments in the form of either FeS or MeS (a metal sulfide). In a parallel analysis, metals simultaneously released with the sulfides (the simultaneously extracted metals) are also quantified, for example, by graphite furnace atomic absorption spectrometry. Metals released during the acid attack are considered to be associated with the phases operationally defined as "exchangeable," "carbonate," "Fe and Mn oxides," "FeS," and "MeS."... [Pg.400]

Nelson, M. B., Davis, J. A., Benjamin, M. M. and Leckie, J. O. (1977). The Role of Iron Sulfides in Controlling Trace Heavy Metals in Anaerobic Sediments Oxidative Dissolution of Ferrous Monosulfides and the Behavior of Associated Trace Metals." Air Force Weapons Laboratory, Technical Report 425. [Pg.417]

Sulfides and disulfides can be produced by bacterial reactions in the marine environment. 2-Dimeth-ylthiopropionic acid is produced by algae and by the marsh grass Spartina alternifolia, and may then be metabolized in sediment slurries under anoxic conditions to dimethyl sulfide (Kiene and Taylor 1988), and by aerobic bacteria to methyl sulfide (Taylor and Gilchrist 1991). Further details are given in Chapter 11, Part 2. Methyl sulfide can also be produced by biological methylation of sulfide itself (HS ). Carbon radicals are not the initial atmospheric products from organic sulfides and disulfides, and the reactions also provide an example in which the rates of reaction with nitrate... [Pg.21]

The pH of hydrothermal solution in sediment-hosted sites is higher than that of the other volcanic rock-hosted sites. This might be due to the interaction of hydrothermal solution with sediments (probably carbonates). If pH increases by the interaction with sediments, sulfides tend to precipitate at the subsurface environment due to an increase in pH. The low concentration of base metals in hydrothermal solution in sediment-hosted deposits could be explained by such subsurface depositions. [Pg.357]

Sediment Trap hydrogen sulfide in sodium hydroxide sulfide reacts with AW-dimethyl-p-phenylene-diamine to from methylene blue. Colorimetry 0.01 pmol/gram NR Allen et al. 1994... [Pg.162]

Allen HE, Fu G, Boothman W, et al. 1994. Determination of acid volatile sulfide and selected simultaneously extractable metals in sediment. PB94-183852. [Pg.175]

Dunnette DA, Chynoweth DP, Mancy KH. 1985. The source of hydrogen sulfide in anoxic sediment. Water Res 19 875-884. [Pg.182]

The sulfides of trace elements in soils and sediments are also of importance in controlling the availability and mobility of trace elements, especially for land disposal of sulfide-rich sediments or anaerobic digested sludge. Due to the oxic nature in arid soils, most of the sulfur is present as sulfate thus, this problem may not be pressing. In most current SSD schedules, the majority of the sulfide forms are included in the organic bound or residual fractions. [Pg.129]

Shannon R.D., White J.R. The selectivity of a sequential extraction procedure for the determination of iron oxyhydroxides and iron sulfides in lake sediments. Biogeochem 1991 14 193-208. [Pg.350]

Benoit JM, Gilmour CC, Mason RP, Heyes A (1999) Sulfide controls on mercury speciation and bioavailability to methylating bacteria in sediment pore waters. Environ Sci Technol 33 951-957... [Pg.255]

Copper concentrations in sediment interstitial pore waters correlate positively with concentrations of dissolved copper in the overlying water column and are now used to predict the toxicity of test sediments to freshwater amphipods (Ankley et al. 1993). Sediment-bound copper is available to deposit-feeding clams, especially from relatively uncontaminated anoxic sediments of low pH (Bryan and Langston 1992). The bioavailability of copper from marine sediments, as judged by increased copper in sediment interstitial waters, is altered by increased acid volatile sulfide (AYS)... [Pg.132]


See other pages where Sulfide in sediments is mentioned: [Pg.164]    [Pg.161]    [Pg.134]    [Pg.270]    [Pg.344]    [Pg.331]    [Pg.127]    [Pg.563]    [Pg.628]    [Pg.651]    [Pg.20]    [Pg.244]    [Pg.164]    [Pg.161]    [Pg.134]    [Pg.270]    [Pg.344]    [Pg.331]    [Pg.127]    [Pg.563]    [Pg.628]    [Pg.651]    [Pg.20]    [Pg.244]    [Pg.50]    [Pg.416]    [Pg.80]    [Pg.257]    [Pg.598]    [Pg.59]    [Pg.22]    [Pg.144]    [Pg.165]    [Pg.241]    [Pg.251]    [Pg.449]    [Pg.459]   
See also in sourсe #XX -- [ Pg.338 , Pg.341 , Pg.345 ]




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Hydrogen sulfide in freshwater sediments

In sediment

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