On a global scale 3,800 Mg a −1 mercury (Hg) enter the ocean through atmospheric deposition and 300 Mg a −1 through riverine input (UNEP, 2019). Atmospheric wet deposition of divalent mercury (Hg II ) constitutes the main deposition pathway of total atmospheric Hg to the surface ocean (Zhang et al., 2014), while dry deposition of Hg II constitutes a minor fraction in the mid-latitude marine boundary layer (Holmes et al., 2009). Reduction of Hg II to gaseous elemental mercury (Hg 0 ) in the surface ocean leads to re-emission of Hg 0 from the ocean of approximately 2,900 Mg a −1 (Horowitz et al., 2017). However, these current air-sea Hg exchange estimates are associated with high uncertainty and a better constraint on the Hg 0 flux is crucial for two reasons: first, ocean emissions reduce the reservoir of Hg II available for methylation in the water column and subsequent bioaccumulation in marine biota (Lavoie et al., 2013). Second, ocean emissions increase the amount of Hg actively cycling between the atmosphere, marine and terrestrial ecosystems (Amos et al., 2013;Selin, 2009). Air-sea exchange of Hg 0 is a diffusion process driven by the concentration gradient between Hg 0 in the atmosphere (Hg 0 air ) and dissolved gaseous elemental Hg in seawater (DGM, hereinafter referred to as Hg 0 aq ). The two key factors that control the Hg 0 air-sea exchange are (a) the saturation of Hg 0 in surface water relative to equilibrium conditions expressed by Henry's law constant for Hg 0 and (b) the gas transfer velocity (k) (Qureshi et al., 2011). The Hg 0 flux is typically estimated based on a thin film gas exchange model (Liss & Merlivat, 1986;Wanninkhof, 1992) that uses in situ measurements of Hg 0 air and Hg 0 aq together with a wind speed dependent parameterization of k that was developed based on field experiments with volatile