Atmospheric N 2 O concentrations have increased substantially since the industrial revolution, making it an important greenhouse gas and the dominant ozone depleting agent after the Montreal Protocol phased out chlorofluorocarbon use (Myhre et al., 2013;Ravishankara et al., 2009). Approximately 25% of the N 2 O emission into the atmosphere comes from aquatic environments, including inland waters, estuaries, and the ocean (Tian et al., 2020). Notably, estuaries release a large and highly uncertain amount of N 2 O annually (0.06-5.7 Tg N yr −1 ) when their small area is compared to other aquatic systems (Bange et al., 1996;Murray et al., 2015;Seitzinger & Kroeze, 1998). However, there are large heterogeneities of N 2 O distribution within and across estuaries. For example, estuaries can transition from source to sink for N 2 O across the land use gradient (Reading et al., 2020;Wells et al., 2018). This transition is partly responsible for the substantial uncertainties in estimated global estuarine N 2 O fluxes (Bange et al., 1996;Kroeze et al., 2005;Murray et al., 2015). Previous studies on estuarine N 2 O have mainly focused on N 2 O production processes such as nitrification, nitrifier-denitrification, and canonical denitrification (Barnes & Upstill-Goddard, 2011;Ji et al., 2018;Lin et al., 2016) while the controlling factors on N 2 O consumption (i.e., reduction) are generally overlooked. Since the net N 2 O emission/flux is determined by the balance between production and reduction, an improved mechanistic understanding of N 2 O reduction is necessary to better estimate net N 2 O emissions from estuaries.