The temporal and spatial variations in greenhouse gas (GHG) emission estimates in wetlands impede our ability to predict and upscale total emissions; thus, a scalar parameter is needed to predict GHG emissions. We investigated the importance of soil organic carbon (SOC) in the prediction of methane (CH 4) and nitrous oxide (N 2 O) emissions in rewetted agricultural peatlands, positing that both CH 4 and N 2 O production are explained by the quantity and turnover of SOC. Field CH 4 and N 2 O fluxes, along with other edaphic and environmental variables, were monitored in rewetted peatlands with a range of SOC (6%, 11%, and 23%) that were recently converted from row crops to flooded rice cultivation to reverse soil subsidence. Nitrogen (N) fertilization reduced annual CH 4 emission by 77.2% in the 6% C field, but this effect was not found in other fields. Annual N 2 O emissions were not affected by N fertilization and averaged 8.9, 5.2, and 1.9 kg N 2 ON ha-1 for the 6%, 11%, and 23% C fields, respectively. SOC was the dominant factor controlling both CH 4 and N 2 O emissions. The annual emission for both CH 4 and N 2 O was accurately described by a decaying power regression with increasing SOC contents (R 2 > 0.49). This relationship was also observed after splitting total annual emission of CH 4 and N 2 O into growing and fallow seasons. Nitrogen fertilization and the seasonality in CH 4 and N 2 O emissions did not change the relationships. The inverse correlation between SOC and CH 4 and N 2 O emissions was likely caused by different chemical composition of SOC in various soils. Our results suggest that SOC can be a potential proxy to predict CH 4 and N 2 O emissions in rewetted peatlands to better define GHG predictions of wetland restoration efforts.