Mercury (Hg) is a neurotoxin with a long lifetime in the Earth system, which exchanges between the atmosphere, continents, and oceans (Driscoll et al., 2013;Lyman et al., 2020; Obrist et al., 2018). A large range of human activities result in emissions of mercury to the atmosphere, predominantly (80%-90%) as elemental mercury (Hg 0 ) (AMAP/ UN, 2019;Gustin et al., 2015), characterized by a low chemical reactivity. Atmospheric mercury deposits to ecosystems after oxidation to form water-soluble Hg I,II species (Horowitz et al., 2017) as well as in elemental form (Jiskra et al., 2021). Therefore, understanding the atmospheric mercury cycling between Hg 0 and oxidized monovalent Hg I and divalent Hg II forms is key for accurate assessments of its global transport and input into ecosystems via surface deposition. In current mechanistic and modeling research it is assumed that only highly reactive bromine atoms (Br) or radicals (OH) can initiate the oxidative chain of gas-phase ambient mercury (