CH4 production, oxidation and emission in a U.K. ombrotrophic peat bog: Influence of SO42− from acid rain

https://doi.org/10.1016/0038-0717(95)00018-AGet rights and content

Abstract

Factors influencing the rates of production and emission of CH4, CH4 oxidation and rates of SO42− reduction, were measured in the peat of an ombrotrophic bog in New Galloway, Scotland. Vertical concentration profiles of CH4 and O2 showed that the water table essentially represented the oxic-anoxic boundary in the peat. This boundary was usually at the surface in the case of peat-bog hollows, but up to 20 cm of oxic peat occurred above the water table in peat-bog hummocks. Penetration of O2 into the peat increased under illumination when photosynthesis was active, but decreased in the dark. Emission of CH4 from the peat surface was faster from peat-bog hollows than from hummocks, where most CH4 was reoxidized before emission. CH4 emission rates also varied seasonally, being greatest during summer. For most of the year the amount of organic C oxidized to CO2 by SO42− reduction by anaerobic bacteria exceeded that being transformed to CH4 by methanogenic bacteria, except during summer when SO42− reduction became SO42− limited. Laboratory experiments showed that the addition of SO42− to peat inhibited CH4 formation, confirming that there was competitive inhibition of CH4 formation by active SO42− reduction, as demonstrated in other environments. The degree of acid rain deposition of SO42− onto peat bogs may therefore be extremely important in regulating the production and emission of CH4 from peat. CH4 formation was most active in the strata of peat 5–15 cm below the water table, although actual rates of CH4 formation were slower in the peat beneath hummocks than that below hollows. In contrast, CH4 oxidation occurred nearer the peat surface (only 3–7 cm below the water table) where the methanotrophic bacteria could intercept vertically migrating CH4. Surprisingly, the peak for CH4 oxidation potential occurred at about 5 cm below the water table, in peat which was apparently anoxic. This may reflect either a transiently oxic peat environment, in which aerobic CH4-oxidizing bacteria persisted, or the presence of a community of facultatively anaerobic CH4-oxidizing bacteria which, in anoxic conditions, metabolized substrates other than CH4. There was no evidence of anaerobic CH4 oxidation.

References (57)

  • G.M. King

    Dynamics and controls of methane oxidation in a Danish wetland sediment

    FEMS Microbiology Ecology

    (1990)
  • A. Martin

    Sulphur in the air and deposited from air and rain over Great Britain and Ireland

    Environmental Pollution

    (1980)
  • D.B. Nedwell

    Distribution and pool sizes of microbially available carbon in sediment measured by a microbiological assay

    FEMS Microbiology Ecology

    (1987)
  • R.S. Oremland et al.

    Sulfate reduction and methanogenesis in marine sediments

    Geochimica et Cosmochimica Acta

    (1978)
  • J.B. Yavitt et al.

    Methane consumption in decomposing sphagnum-derived peat

    Soil Biology & Biochemistry

    (1990)
  • H. Abdollahi et al.

    Seasonal temperature as a factor influencing bacterial sulfate reduction in a saltmarsh sediment

    Microbial Ecology

    (1979)
  • J.W. Abram et al.

    Inhibition of methanogenesis by sulphate reducing bacteria competing for transferred hydrogen

    Archives for Microbiology

    (1978)
  • J.W. Abram et al.

    Hydrogen as a substrate for methanogenesis and sulphate reduction in anaerobic saltmarsh sediment

    Archives for Microbiology

    (1978)
  • M.J. Alperin et al.

    Inhibition experiments on anaerobic methane oxidation

    Applied and Environmental Microbiology

    (1985)
  • G. Billen

    Modelling the process of organic matter degradation and nutrients recycling in sedimentary systems

  • J.D. Cline

    Spectrophotometric determination of hydrogen sulfide in natural waters

    Limnology and Oceanography

    (1969)
  • R.S. Clymo

    Peat

  • R.S. Clymo

    Models of peat growth

    Suo

    (1992)
  • R.S. Clymo et al.

    Productivity of Sphagnum (bog-moss) and peat accumulation

    Hydrobiologia

    (1971)
  • H. Dinel et al.

    A field study of the effect of depth on methane production in peatland waters: equipment and preliminary results

    Journal of Ecology

    (1988)
  • I. Fung et al.

    Three-dimensional model synthesis of the global methane cycle

    Journal of Geophysical Research

    (1991)
  • E. Gorham

    On the chemical composition of some waters from the Moor House nature reserve

    Journal of Ecology

    (1956)
  • R.C. Harriss et al.

    Methane flux from northern peatland

    Nature, London

    (1985)
  • Cited by (142)

    • High hydrogen sulfide emissions from subtropical forest soils based on field measurements in south China

      2019, Science of the Total Environment
      Citation Excerpt :

      As a predominant S species of biogenic S gases (Aneja et al., 1981, Aneja, 1990; Steudler and Peterson, 1984; Goldan et al., 1987), hydrogen sulfide (H2S) is both foul smelling and noxious (Barton et al., 2014), and has important impacts on atmospheric acid deposition, aerosol formation (Aneja, 1990; Bates et al., 1992; Cooper et al., 1987; Vet et al., 2014), and global climate change through its association with cloud formation and ‘solar dimming’ (Charlson et al., 1987; Lohmann and Feichter, 2005). The emission of H2S is also closely related to iron cycling, carbon mineralization, and methane emission (Johnston et al., 2014; Nedwell and Watson, 1995). H2S emitted from natural sources (4.42 Tg yr−1) is of the same order of magnitude as the anthropogenic emissions (3.30 Tg yr−1), and is one of the major sources of sulfur gases in the atmosphere (Watts, 2000), playing a significant role in the global sulfur cycle.

    • Intra-annual groundwater levels and water temperature patterns in raised bogs affected by human impact in mountain areas in Poland

      2018, Science of the Total Environment
      Citation Excerpt :

      Therefore, changes in vascular plant production and composition may be caused by even very small changes in the groundwater level (Wallen et al., 1988; Potvin et al., 2015). Increasing the groundwater level in peat soil will also increase its biological activity (Nedwell and Watson, 1995) and increase the diffusion of oxygen – O2 may penetrate as far as 2 cm below the water table (Benstead and Lloyd, 1994). From the discussion above, it can be concluded that the habitat degradation resulting from the drainage works on the peat-bogs in the Bieszczady Mts.

    View all citing articles on Scopus
    View full text