Factors Influencing Stable Isotope Ratios in CH₄ and CO₂ Within Subenvironments of Freshwater Wetlands: Implications for δ-Signatures of Emissions

Abstract

Much uncertainty still exists regarding spatial and temporal variability of stable isotope ratios (¹³C/¹²C and D/H) in different CH₄-emission sources. Such variability is especially prevalent in freshwater wetlands where a range of processes can influence stable isotope compositions, resulting in variations of up to ∼50‰ for δ¹³C-CH₄ and ∼150‰ for δD-CH₄ values. Within a temperate-zone bog and marsh situated in southwestern Ontario, Canada, gas bubbles in pond sediments exhibit only minor seasonal and spatial variation in δ¹³C-CH₄, δD-CH₄ and δ¹³C-CO₂ values. In pond sediments, CO₂ appears to be the main source of carbon during methanogenesis either directly via CO₂ reduction or indirectly through dissimilation of autotrophic acetate. In contrast, CH₄ production occurs primarily via acetate fermentation at shallow depths in peat soils adjacent to ponds at each wetland. At greater depths within soils, σCO₂ and H₂O increasingly exert an influence on δ¹³C- and δD-CH₄ values. Secondary alteration processes (e.g., methanotrophy or diffusive transport) are unlikely to be responsible for depth-related changes in stable isotope values of CH₄. Recent models that attempt to predict δD-CH₄ values in freshwater environments from D/H ratios in local precipitation do not adequately account for such changes with depth. Subenvironments (i.e., soil-forming and open water areas) in wetlands should be considered separately with respect to stable isotope signatures in CH₄ emission models.