Processes influencing secondary aerosol formation in the San Joaquin Valley during winter.
Air quality data collected in the California Regional PM10/ PM(2.5) Air Quality Study (CRPAQS) are analyzed to qualitatively assess the processes affecting secondary aerosol formation in the San Joaquin Valley (SJV). This region experiences some of the highest fine particulate matter (PM(2.5)) mass concentrations in California (< or = 188 microg/m3 24-hr average), and secondary aerosol components (as a group) frequently constitute over half of the fine aerosol mass in winter. The analyses are based on 15 days of high-frequency filter and canister measurements and several months of wintertime continuous gas and aerosol measurements. The phase-partitioning of nitrogen oxide (NO(x))-related nitrogen species and carbonaceous species shows that concentrations of gaseous precursor species are far more abundant than measured secondary aerosol nitrate or estimated secondary organic aerosols. Comparisons of ammonia and nitric acid concentrations indicate that ammonium nitrate formation is limited by the availability of nitric acid rather than ammonia. Time-resolved aerosol nitrate data collected at the surface and on a 90-m tower suggest that both the daytime and nighttime nitric acid formation pathways are active, and entrainment of aerosol nitrate formed aloft at night may explain the spatial homogeneity of nitrate in the SJV. NO(x) and volatile organic compound (VOC) emissions plus background O3 levels are expected to determine NO(x) oxidation and nitric acid production rates, which currently control the ammonium nitrate levels in the SJV. Secondary organic aerosol formation is significant in winter, especially in the Fresno urban area. Formation of secondary organic aerosol is more likely limited by the rate of VOC oxidation than the availability of VOC precursors in winter.
Lurmann
Frederick W
FW
Sonoma Technology, Inc., Petaluma, CA 94954, USA. fred@sonomatech.com
Brown
Steven G
SG
McCarthy
Michael C
MC
Roberts
Paul T
PT
D000336:Aerosols / Q000032:analysis*; D000393:Air Pollutants / Q000032:analysis*; D000641:Ammonia / Q000032:analysis; D002140:California; D004784:Environmental Monitoring; D006801:Humans; D049449:Luminescence; D008962:Models, Theoretical; D009566:Nitrates / Q000032:analysis; D017942:Nitric Acid / Q000032:analysis; D010083:Oxidants, Photochemical; D052638:Particulate Matter / Q000032:analysis*; D010777:Photochemistry; D012621:Seasons; D013816:Thermodynamics; D013997:Time Factors; D014835:Volatilization
D000336:Aerosols; D000393:Air Pollutants; D009566:Nitrates; D010083:Oxidants, Photochemical; D052638:Particulate Matter; D017942:Nitric Acid; D000641:Ammonia; C006568:ammonium nitrate