Abstract. Isotopic compositions of Mercury (Hg) in atmospheric particles (HgPM) are probably the mixed results of emission sources and atmospheric processes. Here, we present Hg isotopic compositions in daily fine particles (PM2.5) collected from an industrial site (Chunxiao – CX) and a nearby mountain site (Daimeishan – DMS) in a coastal area of East China, and in surface seawater close to the industrial area, to reveal the influence of anthropogenic emission sources and atmospheric transformations on Hg isotopes. The PM2.5 samples displayed a significant spatial difference in δ202Hg. For the CX site, the negative δ202Hg values are similar to those of source materials, and the HgPM contents were well correlated with chemical tracers, indicating the dominant contributions of local industrial activities to HgPM2.5, whereas the observed positive δ202Hg at the DMS site was likely associated with regional emissions and extended atmospheric processes during transport. The Δ199Hg values in PM2.5 from the CX and DMS sites were comparably positive. The unity slope of Δ199Hg versus Δ201Hg over all data suggests that the odd mass independent fractionation (MIF) of HgPM2.5 was primarily induced by the
photoreduction of Hg2+ in aerosols. The positive Δ200Hg
values with a minor spatial difference were probably associated with the
photooxidation of Hg0, which is generally enhanced in the coastal
environment. Total Hg in offshore surface seawater was characterized by
negative δ202Hg and near-zero Δ199Hg and Δ200Hg values, which are indistinguishable from Hg isotopes of source
materials. Overall, the PM2.5 collected from industrial areas had
comparable δ202Hg values but more positive Δ199Hg
and Δ200Hg as compared to surface seawater. The results
indicate that atmospheric transformations would induce the significant
fractionation of Hg isotopes and obscure the Hg isotopic signatures of
anthropogenic emissions.