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dc.contributor.authorTao, Madankui
dc.contributor.authorFiore, Arlene M
dc.contributor.authorKarambelas, Alexandra
dc.contributor.authorMiller, Paul J
dc.contributor.authorValin, Lukas C
dc.contributor.authorJudd, Laura M
dc.contributor.authorTzortziou, Maria
dc.contributor.authorWhitehill, Andrew
dc.contributor.authorTeora, Amanda
dc.contributor.authorTian, Yuhong
dc.contributor.authorCiverolo, Kevin L
dc.contributor.authorTong, Daniel
dc.contributor.authorMa, Siqi
dc.contributor.authorAdamo, Susana B
dc.contributor.authorHolloway, Tracey
dc.date.accessioned2025-10-09T16:09:26Z
dc.date.available2025-10-09T16:09:26Z
dc.date.issued2025-05-12
dc.identifier.urihttps://hdl.handle.net/1721.1/163109
dc.description.abstractEstimating tropospheric ozone (O3) production from observations is challenging but possible given the close coupling of O3 with formaldehyde (HCHO) and nitrogen dioxide (NO2), two remotely sensed air pollutants. The previous reliance on once-daily satellite overpasses highlights the need to study diurnal changes and surface-column relationships. Using surface observations, Pandora spectrometer retrievals, and a high-resolution (1.33 km) air quality model (WRF-CMAQ), we characterize diurnal patterns of HCHO and NO2 at seven locations along an upwind-downwind pathway through New York City during June–August 2018. Diurnal patterns of limited surface HCHO measurements suggest biogenic emission influence, while a bimodal surface NO2 pattern indicates the impact of local anthropogenic nitrogen oxides emissions. Details of these patterns vary by site: an afternoon NO2 spike at New Haven (CT) indicates traffic emissions, while a delayed daily HCHO peak at Westport (CT) relative to other sites likely reflects sea breeze dynamics. Peak column concentrations generally lag surface peaks by about four hours, occurring at 9–10 a.m. for morning NO2 (from Pandora and WRF-CMAQ) and around 4 p.m. for midday HCHO (from WRF-CMAQ). TROPOMI overpass time at 1:30 p.m. misses peak column HCHO and NO2 concentrations. A box model (F0AM) constrained with site-level observations and WRF-CMAQ fields indicates 1–9 ppb hr−1 higher noontime local O3 production rates on three sets of paired high- versus mid-to-low-O3 days. F0AM sensitivity analyses on these six days suggest a predominantly transitional O3 formation regime at urban and downwind sites, differing at some sites from the NOx-saturated regime diagnosed for summertime average conditions via the weekday-weekend effect.en_US
dc.language.isoen
dc.publisherWileyen_US
dc.relation.isversionofhttps://doi.org/10.1029/2024JD040922en_US
dc.rightsCreative Commons Attribution-Noncommercialen_US
dc.rights.urihttps://creativecommons.org/licenses/by-nc/4.0/en_US
dc.sourceWileyen_US
dc.titleInsights Into Summertime Surface Ozone Formation From Diurnal Variations in Formaldehyde and Nitrogen Dioxide Along a Transect Through New York Cityen_US
dc.typeArticleen_US
dc.identifier.citationTao, M., Fiore, A. M., Karambelas, A., Miller, P. J., Valin, L. C., Judd, L. M., et al. (2025). Insights into summertime surface ozone formation from diurnal variations in formaldehyde and nitrogen dioxide along a transect through New York City. Journal of Geophysical Research: Atmospheres, 130, e2024JD040922.en_US
dc.contributor.departmentMassachusetts Institute of Technology. Department of Earth, Atmospheric, and Planetary Sciencesen_US
dc.relation.journalJournal of Geophysical Research: Atmospheresen_US
dc.eprint.versionFinal published versionen_US
dc.type.urihttp://purl.org/eprint/type/JournalArticleen_US
eprint.statushttp://purl.org/eprint/status/PeerRevieweden_US
dc.date.updated2025-10-09T16:02:04Z
dspace.orderedauthorsTao, M; Fiore, AM; Karambelas, A; Miller, PJ; Valin, LC; Judd, LM; Tzortziou, M; Whitehill, A; Teora, A; Tian, Y; Civerolo, KL; Tong, D; Ma, S; Adamo, SB; Holloway, Ten_US
dspace.date.submission2025-10-09T16:02:06Z
mit.journal.volume130en_US
mit.journal.issue9en_US
mit.licensePUBLISHER_CC


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