Abbreviations: CWC, cold water carbon; DOE, day of experiment; DI, deionized water; HWC, hot water carbon; GLM, general linear model; N 2 OR, nitrous oxide reductase; SWLR, structure-dependent water-induced linerar reduction model; WFPS, water-filled pore space. N itrous oxide is a potent greenhouse gas (GHG) that contributes to climate change, and it is projected to be the dominant ozone-depleting substance emitted in the 21st century (Ravishankara et al., 2009). Increases in atmospheric N 2 O concentrations are linked to N-based fertilizer inputs and excretal returns from grazing ruminant livestock to agricultural soils. High inputs of N from these sources can cause soil N concentrations to be greater than plant requirements. This excess soil N is available for microbial processes such as nitrification, denitrification, and nitrifier-denitrification, the latter two processes dominate the production of N 2 O (Wrage et al., 2001;Davidson, 2009;Kool et al., 2010;Zhu et al., 2013).Nitrous oxide is produced from denitrification and nitrifier-denitrification when soil O 2 is low (Goreau et al., 1980;Firestone and Davidson, 1989;Venterea, 2007;Zhu et al., 2013). Soil O 2 distribution in situ is variable (Butterbach-Bahl et al., 2013) as even soils considered aerobic can have anaerobic microsites where N 2 O production may occur (Robertson et al., 1989;Laughlin and Stevens, 2002;
Core Ideas• Heavy irrigation, surface flooding, and urine decrease soil oxygen.• When soil oxygen decreases, N 2 O fluxes rapidly increase when nitrogen is available.• Nitrous oxide fluxes are explained well using relative soil gas diffusivity.