Abstract

Sulfate (SO42- and nitrate (NO3-) account for half of the fine particulate matter mass over the eastern United States. Their wintertime concentrations have changed little in the past decade despite considerable precursor emissions reductions. The reasons for this have remained unclear because det... Show moreSulfate (SO42- and nitrate (NO3-) account for half of the fine particulate matter mass over the eastern United States. Their wintertime concentrations have changed little in the past decade despite considerable precursor emissions reductions. The reasons for this have remained unclear because detailed observations to constrain the wintertime gas-particle chemical system have been lacking. We use extensive airborne observations over the eastern United States from the 2015 Wintertime Investigation of Transport, Emissions, and Reactivity (WINTER) campaign; ground-based observations; and the GEOS-Chem chemical transport model to determine the controls on winter SO42- and NO3-. GEOS-Chem reproduces observed SO42--NO3--NH4+ particulate concentrations (2.45 mu g sm(-3)) and composition (SO42-: 47%; NO3-: 32%; NH4+: 21%) during WINTER. Only 18% of SO2 emissions were regionally oxidized to SO42- during WINTER, limited by low [H2O2 ] and [OH]. Relatively acidic fine particulates (pH similar to 1.3) allow 45% of nitrate to partition to the particle phase. Using GEOS-Chem, we examine the impact of the 58% decrease in winter SO2 emissions from 2007 to 2015 and find that the H2O2 limitation on SO2 oxidation weakened, which increased the fraction of SO2 emissions oxidizing to SO42-. Simultaneously, NOx emissions decreased by 35%, but the modeled NO3- particle fraction increased as fine particle acidity decreased. These feedbacks resulted in a 40% decrease of modeled [SO42-] and no change in [NO3-], as observed. Wintertime [SO42-] and [NO3-] are expected to change slowly between 2015 and 2023, unless SO2 and NOx emissions decrease faster in the future than in the recent past. Show less