As the derivatives of ammonia (NH 3 ), gaseous amines are a class of organic vapors containing a basic nitrogen atom with a lone pair, where one or more hydrogen atoms are substituted by organic functional groups, for example, an alkyl or aryl group (Qiu & Zhang, 2013). Since ambient concentration of amines (typically in the range of ppt) is 1-3 orders of magnitude lower than that of ammonia (NH 3 ;Kuhn et al., 2011), this poses a significant analytical challenge for environmental monitoring (Szulejko & Kim, 2014), resulting in scarce information on the occurrence of amines in the atmosphere. For a long time, agriculture is considered as the dominant source for both ammonia (NH 3 ) and amines (Ge et al., 2011a). For example, the concentration of amines with low molecular weight (e.g., monomethylamine or MMA, dimethylamine or DMA, and trimethylamine or TMA) can reach as high as several hundreds of ppm in the vicinity of concentrated animal feeding operations . Additionally, amines can be emitted from various natural (such as ocean organisms [Altieri et al., 2016], protein degradation [Lidbury et al., 2017], and wildfire burning [Ito et al., 2015]) and anthropogenic (such as automobiles [Cadle & Mulawa, 1980], industries [Yao et al., 2016], CO 2 sequestration process [Yamada, 2021], and treatment of sewage and waste [Chang et al., 2021]) sources.Currently, there are 24 carcinogenic amines banned by global legislatures for use in industrial production (e.g., textile dyeing) (Lee & Wexler, 2013). Moreover, amines have much stronger basicity than NH 3 and are more likely