Inland waters play an important role in the global carbon cycle, contributing significant greenhouse gas (GHG) emissions to the atmosphere (Bastviken et al., 2011; Cole et al., 2007; Raymond et al., 2013). River networks are generally conceptualized as active biogeochemical reactors that mix, store, and evade GHGs and constituents transported from upstream together with those generated from in-stream production (Cole et al., 2007; see also; Raymond et al., 2016; Zarnetske et al., 2018). Ultimately, inland waters store, evade, and transport over half of the carbon that they receive from the terrestrial ecosystem before reaching the oceans (Hotchkiss et al., 2015), thereby playing a fundamental role in global carbon processes. Running inland waters (hereafter termed 'rivers') are generally supersaturated with GHGs and exhibit a net evasive flux of these gases from water to air (Cole & Caraco, 2001; Jones et al., 2003). This flux [M/L 2 T] is relatively easy to calculate with in situ knowledge of the gas concentration gradient between the water [gas] water and the air [gas] air [M/L 3 ] and the gas transfer velocity k [L/T] (Equation 1).