A B S T R A C T Arctic regions are generally nutrient limited, receiving an extensive part of their bio-available nitrogen from the deposition of atmospheric reactive nitrogen. Reactive nitrogen oxides, as nitric acid (HNO 3 ) and nitrate aerosols (p-NO 3 ), can either be washed out from the atmosphere by precipitation or dry deposited, dissolving to nitrate (NO À 3 ). During winter, NO À 3 is accumulated in the snowpack and released as a pulse during spring melt. Quantification of NO À 3 deposition is essential to assess impacts on Arctic terrestrial ecology and for ice core interpretations. However, the individual importance of wet and dry deposition is poorly quantified in the high Arctic regions where in-situ measurements are demanding. In this study, three different methods are employed to quantify NO and p-NO 3 using atmospheric concentrations and stability observations, resulting in a total combined nitrate dry deposition of Á10.7691.26 mg m (2 . The model indicates that deposition primarily occurs via HNO 3 with only a minor contribution by p-NO 3 . Modelled median deposition velocities largely explain this difference: 0.63 cm s (1 for HNO 3 while p-NO 3 was 0.0025 and 0.16 cm s (1 for particle sizes 0.7 and 7 mm, respectively.Overall, the three methods are within two standard errors agreement, attributing an average 14% (total range of 2Á44%) of the total nitrate deposition to dry deposition. Dry deposition events were identified in association with elevated atmospheric concentrations, corroborating recent studies that identified episodes of rapid pollution transport and deposition to the Arctic.