Abstract
The mechanisms, pathways, and rates of CO2 and CH4 production are central to understanding carbon cycling and greenhouse gas flux in wetlands. Thawing permafrost regions are of particular interest because they are disproportionally affected by climate warming and store large reservoirs of organic C that may be readily converted to CO2 and CH4 upon thaw. This conversion is accomplished by a community of microorganisms interacting in complex ways to transform large organic compounds into fatty acids and ultimately CO2 and CH4. While the central role of microbes in this process is well-known, geochemical rate models rarely integrate microbiological information. Herein, we expanded the geochemical rate model of Neumann et al., (2016, Biogeochemistry 127: 57–87) to incorporate a Bayesian probability analysis and applied the result to quantifying rates of CO2, CH4, and acetate production in closed-system incubations of peat collected from three habitats along a permafrost thaw gradient. The goals of this analysis were twofold. First, we integrated microbial community analyses with geochemical rate modeling by using microbial data to inform the best model choice among equally mathematically feasible model variants. Second, based on model results, we described changes in organic carbon transformation among habitats to understand the changing pathways of greenhouse gas production along the permafrost thaw gradient. We found that acetoclasty, hydrogenotrophy, CO2 production, and homoacetogenesis were the important reactions in this system, with little evidence for anaerobic CH4 oxidation. There was a distinct transition in the reactions across the thaw gradient. The collapsed palsa stage presents an initial disequilibrium where the abrupt (physically and temporally) change in elevation introduces freshly fixed carbon into anoxic conditions and the fermentation products build up over time as the system transitions through the acid phase and electron acceptors are depleted. In the bog, fermentation slows, while methanogenesis increases. In the fully-thawed fen, most of the terminal electron acceptors are depleted and the system becomes increasingly methanogenic. This suggests that as permafrost regions thaw and dry palsas transition into wet fens, CH4 emissions will rise, increasing the warming potential of these systems and accelerating climate warming feedbacks.
Highlights
More than 1650 Pg of organic carbon (OC) is currently sequestered in boreal regions, where it is frozen in permafrost unavailable for microbial decomposition (Hugelius et al, 2013)
The 16S rRNA copy-corrected relative abundances of microbial community members taxonomically affiliated with hydrogenotrophic methanogens, acetoclastic methanogens, methanotrophs, and homoacetogens were summed in the incubations and compared over time within incubations and across habitats (Figure 6 and Supplementary Table S2). quantitative polymerase chain reaction (qPCR) confirmed that 16S rRNA gene copy numbers – a proxy for cell abundances – did not vary appreciably among habitats, and remained within the same order of magnitude over time in each
While OTUs belonging to aerobic methane oxidizers from Methylocystaceae and Methylococcaceae were present in the incubations, at approximately constant or slightly declining relative abundances over time, the highly anoxic conditions of the incubations almost certainly precluded any aerobic methane oxidation activity
Summary
More than 1650 Pg of organic carbon (OC) is currently sequestered in boreal regions, where it is frozen in permafrost unavailable for microbial decomposition (Hugelius et al, 2013). Thawing of palsa directly adjacent to a fen, or the rapid thawing of palsas surrounding a collapse pool, can connect the collapse feature to the surrounding water table before ingrowth of Sphagnum can occur. All of these processes lead to increasing minerotrophy as the site transitions into a poor and a rich fen, leading to a shift in vegetation to sedges and other aquatic macrophytes, characteristic of fens (Zoltai, 1993; Vitt et al, 1994; Jorgenson et al, 2001; Malmer et al, 2005) (Figure 1)
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