Peatlands are important carbon (C) stores with an estimated stock of 540 Pg C, while only covering about 3%-4% of the global land surface area (Gorham et al., 2012;Yu, 2011). They also emit approximately 36 Tg CH 4 -C (equivalent to approx. 10% Total ) to the global atmospheric budget (Abdalla et al., 2016;Mikaloff Fletcher et al., 2004;Wuebbles, 2002;Yu, 2011). This dual role is due to fundamental differences in the microbial decomposition in water-saturated peatland ecosystems compared to mineralization in drained soils. Decomposition also happens here to a large extent under aerobic conditions in the unsaturated layer of the acrotelm, but proceeds, albeit slowed, under waterlogged, anoxic conditions in the catotelm, yielding CO 2 and potentially CH 4 . Many controls on decomposition in peatlands have been identified, such as temperature, pH, and the availability of terminal electron acceptors (TEAs) for microbial processes that produce both CH 4 and CO 2 as their end products