Journal of Geophysical Research Atmospheres · 1994 · 230 citations · 33 references
Natural SciencesChemistryEarth SciencesAtmospheric ChemistryAtmospheric ScienceEnvironmental ChemistryAir PollutantsAir Pollution ChemistryAtmospheric Composition ChangeAtmospheric Oxidation ProcessesOzone ChemistryReactive Oxygen SpeciesAtmospheric Oxidation MechanismsFree Radical GenerationOzone PhotochemistryPhotochemical Formation PathwaysPhotochemical Ozone FormationPhotochemical ProductionPhotochemical ReactionsRadical Budget Analysis
Trace gas measurements pertinent to understanding the transport and photochemical formation of O 3 were made at a surface site in rural Georgia as part of the Southern Oxidant Study during the summer of 1991. It was found that there was a strong correlation between O 3 and the oxidation products of NO x : O 3 (ppb) = 27 + 11.4 (NO y (ppb) − NO x (ppb)), r 2 = 0.78. This fit is similar to that observed at other rural sites in eastern North America and indicates a nominal background O 3 level of 27 ppb; values higher than 27 ppb are due to photochemical production in the recent past, which varied from near zero to ≈50 ppb. The origin of the O 3 above background was investigated by using a free radical budget equation to calculate an in situ O 3 production rate in terms of measured concentrations of NO and free radical precursors (O 3 , HCHO, peroxides, and other carbonyls). A comparison of observed and predicted diurnal trends in O 3 indicates significant O 3 production in the afternoon at a time when O 3 concentration is either steady or decreasing. The afternoon near‐surface layer is thereby a source region for O 3 which can be exported. In situ production accounts for approximately one half of the morning increase in O 3 concentration on days with high O 3 ; the remainder is due to entrainment of dirty air aloft by the growing convective boundary layer. Additional evidence for the role of vertical transport in controlling the hour‐to‐hour changes in O 3 is found in the diurnal cycles of SO 2 and HNO 3 which also have rapid increases in the morning. The day‐to‐day variability of O 3 was investigated using a back trajectory model. NO y concentration at the measurement site could be reasonably accounted for by considering NO x emission sources located within 1‐day transport distance. In as much as there is a strong correlation between O 3 and NO y , the coincidence between trajectory location and NO x emission sources appears to be an important factor influencing midday O 3 concentration. Hydrocarbon measurements are consistent with NO x being the limiting factor for formation of O 3 .
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