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Organic nitrate chemistry and its implications for nitrogen budgets in an isoprene- and monoterpene-rich atmosphere: constraints from aircraft observations in the Southeast US
Formation of organic nitrates (RONO.sub.2) during oxidation of biogenic volatile organic compounds (BVOCs: isoprene, monoterpenes) is a significant loss pathway for atmospheric nitrogen oxide radicals (NO.sub.x ), but the chemistry of RONO.sub.2 formation and degradation remains uncertain. Here we i...
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Published in: | Atmospheric chemistry and physics 2016-05, Vol.16 (9), p.5969 |
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Main Authors: | , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , |
Format: | Article |
Language: | English |
Subjects: | |
Online Access: | Get full text |
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Summary: | Formation of organic nitrates (RONO.sub.2) during oxidation of biogenic volatile organic compounds (BVOCs: isoprene, monoterpenes) is a significant loss pathway for atmospheric nitrogen oxide radicals (NO.sub.x ), but the chemistry of RONO.sub.2 formation and degradation remains uncertain. Here we implement a new BVOC oxidation mechanism (including updated isoprene chemistry, new monoterpene chemistry, and particle uptake of RONO.sub.2) in the GEOS-Chem global chemical transport model with ââ¼ââ¯25â¯âÃââ¯25â¯km.sup.2 resolution over North America. We evaluate the model using aircraft (SEAC.sup.4 RS) and ground-based (SOAS) observations of NO.sub.x, BVOCs, and RONO.sub.2 from the Southeast US in summer 2013. The updated simulation successfully reproduces the concentrations of individual gas- and particle-phase RONO.sub.2 species measured during the campaigns. Gas-phase isoprene nitrates account for 25-50â¯% of observed RONO.sub.2 in surface air, and we find that another 10â¯% is contributed by gas-phase monoterpene nitrates. Observations in the free troposphere show an important contribution from long-lived nitrates derived from anthropogenic VOCs. During both campaigns, at least 10â¯% of observed boundary layer RONO.sub.2 were in the particle phase. We find that aerosol uptake followed by hydrolysis to HNO.sub.3 accounts for 60â¯% of simulated gas-phase RONO.sub.2 loss in the boundary layer. Other losses are 20â¯% by photolysis to recycle NO.sub.x and 15â¯% by dry deposition. RONO.sub.2 production accounts for 20â¯% of the net regional NO.sub.x sink in the Southeast US in summer, limited by the spatial segregation between BVOC and NO.sub.x emissions. This segregation implies that RONO.sub.2 production will remain a minor sink for NO.sub.x in the Southeast US in the future even as NO.sub.x emissions continue to decline. |
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ISSN: | 1680-7316 1680-7324 |