Organic soils develop under waterlogged conditions, leading to a reduced decomposition of biomass. Over the last millennia this led to the development of a large carbon (C) pool in the global C cycle. Drainage, necessary for agriculture and forestry, triggers rapid decomposition of soil organic matter (SOM). While undisturbed organic soils are C-sinks, drainage transforms them into C-sources. Climate, drainage depth and land-use are considered the main factors controlling SOM decomposition. However, there is still a large variation in decomposition rates among organic soils, even when climate, drainage and land-use conditions are similar. This thesis investigates the role of SOM composition on peat decomposability in a variety of differently managed drained organic soils. Peat samples from 21 organic soils managed as cropland, grassland and forest soils situated in Switzerland were incubated at 10 and 20 °C for more than 6 months. During incubation, we monitored CO2 emissions and related them to soil characteristics, including bulk density, soil pH, soil organic carbon (SOC) content, and elemental ratios (C/N, H/C and O/C). The incubated samples lost between 0.6 to 1.9% of their SOC at 10 °C and between 1.2 to 42% at 20 °C over the course of 10,000 h (>1 yr). This huge variation occurring under controlled conditions suggests that, besides drainage depth, climate and management, SOM composition is an underestimated factor that determines CO2 fluxes measured in field experiments. In contrast, correlations between the investigated soil characteristics and CO2 emissions were weak. Furthermore, there were no land-use effects. Such effects were expected based on the measured SOM characteristics and IPCC data. Temperature sensitivity of decomposition decreased with depth, indicating an enrichment of recalcitrant SOM in topsoils. This finding stands in contrast to findings in studies of undisturbed organic soils and Further it suggests that future C loss from agriculturally managed organic soils will be similar considering warmer climate conditions. Cultivation of organic soils is accompanied by inputs of young organic carbon (YOC) from plant residues. The amount of YOC inputs, their potential to compensate for oxidative peat loss as well as their lability are unknown. Studying the δ13C signatures in the topsoil of a managed organic soil revealed that at least 19 ± 2.4% of the SOC originate from YOC being accumulated recently. Yet, the accumulation rates are substantially smaller than average peat loss rates on the studied soils. Remarkably, the percentage of YOC in decomposing SOC was 53 ± 0.1%, indicating that YOC is more labile than bulk SOC. These findings are supported by the 14C age of emitted CO2 being younger than that of SOC. Inputs of fresh organic matter (FOM) to soil are known to induce priming effects, i.e. an altered decomposition of resident SOM. The effect of FOM addition on peat decomposition of agriculturally used organic soils has seldom been quantified experimentally. Therefore, we incubated soil samples from managed organic soils over three weeks with and without adding corn straw as FOM. The 13C and 14C signatures of SOC and emitted CO2 enabled us to apportion the amount of decomposed corn, as well as to estimate relative effects of corn addition on the decomposition of SOC from old peat and from YOC. FOM addition induced negative, positive and neutral priming of SOC decomposition. Further, the relative contribution of peat SOC to the overall CO2 release consistently decreased after FOM addition, suggesting that young and old C pools in managed organic soils respond differently to the addition of fresh plant residues. A combination of those two findings indicates that FOM addition can effectively reduce the decomposition of old peat. The results of this thesis suggest that agricultural use of organic soils has a tremendous effect on the composition and decomposability of SOC in organic soils. Furthermore, they show that also crop species known for their carbon sequestration potential are not likely to counteract peat losses caused by drainage. Therefore, agricultural management of organic soils without the risk of losing vast amounts of SOC seems unrealistic and thus, CO2 emissions from organic soils are not likely to decrease in the future. This means that they remain a big issue of concern for future generations in order to counteract climate change.