Variations in the OM/OC ratio of urban organic aerosol next to a major roadway

被引:34
作者
Brown, Steven G. [1 ,2 ,3 ]
Lee, Taehyoung [3 ]
Roberts, Paul T. [2 ]
Collett, Jeffrey L., Jr. [3 ]
机构
[1] Sonoma Technol Inc, Aerometr Data Anal Grp, Petaluma, CA 94954 USA
[2] Sonoma Technol Inc, Petaluma, CA 94954 USA
[3] Colorado State Univ, Dept Atmospher Sci, Ft Collins, CO 80523 USA
关键词
MASS-SPECTROMETER; HIGH-RESOLUTION; AIR-POLLUTION; PARTICULATE MATTER; ELEMENTAL CARBON; PARTICLE-PHASE; DIESEL EXHAUST; AMBIENT; EMISSIONS; SECONDARY;
D O I
10.1080/10962247.2013.826602
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Understanding the organic matter/organic carbon (OM/OC) ratio in ambient particulate matter (PM) is critical to achieve mass closure in routine PM measurements, to assess the sources of and the degree of chemical processing organic aerosol particles have undergone, and to relate ambient pollutant concentrations to health effects. Of particular interest is how the OM/OC ratio varies in the urban environment, where strong spatial and temporal gradients in source emissions are common. We provide results of near-roadway high-time-resolution PM1 OM concentration and OM/OC ratio observations during January 2008 at Fyfe Elementary School in Las Vegas, NV, 18 m from the U.S. 95 freeway soundwall, measured with an Aerodyne high-resolution time-of-flight aerosol mass spectrometer (HR-AMS). The average OM/OC ratio was 1.54 ( 0.20 standard deviation), typical of environments with a low amount of secondary aerosol formation. The 2-min average OM/OC ratios varied between 1.17 and 2.67, and daily average OM/OC ratios varied between 1.44 and 1.73. The ratios were highest during periods of low OM concentrations and generally low during periods of high OM concentrations. OM/OC ratios were low (1.52 0.14, on average) during the morning rush hour (average OM = 2.4 mu g/m(3)), when vehicular emissions dominate this near-road measurement site. The ratios were slightly lower (1.46 +/- 0.10) in the evening (average OM = 6.3 mu g/m(3)), when a combination of vehicular and fresh residential biomass burning emissions was typically present during times with temperature inversions. The hourly averaged OM/OC ratio peaked at 1.66 at midday. OM concentrations were similar, regardless of whether the monitoring site was downwind or upwind of the adjacent freeway throughout the day, though they were higher during stagnant conditions (wind speed < 0.5 m/sec). The OM/OC ratio generally varied more with time of day than with wind direction and speed. Implications: Day-to-day variability in the fine particle OM/OC ratio is quite large, suggesting that using a fixed OM/OC value in PM mass closure calculations, even one that changes seasonally, may be insufficient to achieve accurate mass closure on individual days. Health studies that rely on OC measurements may under- or overestimate exposure to OM, and converting OC to OM with a fixed OM/OC ratio represents a significant source of uncertainty; thus, air quality managers may not have sufficient information about the importance of OM contributions to PM2.5 to make optimal regulatory decisions. Supplemental Materials: Supplemental materials are available for this paper. Go to the publisher's online edition of the Journal of the Air & Waste Management Association.
引用
收藏
页码:1422 / 1433
页数:12
相关论文
共 74 条
  • [21] A two-dimensional volatility basis set - Part 2: Diagnostics of organic-aerosol evolution
    Donahue, N. M.
    Kroll, J. H.
    Pandis, S. N.
    Robinson, A. L.
    [J]. ATMOSPHERIC CHEMISTRY AND PHYSICS, 2012, 12 (02) : 615 - 634
  • [22] A new time-of-flight aerosol mass spectrometer (TOF-AMS) - Instrument description and first field deployment
    Drewnick, F
    Hings, SS
    DeCarlo, P
    Jayne, JT
    Gonin, M
    Fuhrer, K
    Weimer, S
    Jimenez, JL
    Demerjian, KL
    Borrmann, S
    Worsnop, DR
    [J]. AEROSOL SCIENCE AND TECHNOLOGY, 2005, 39 (07) : 637 - 658
  • [23] HOSPITAL ADMISSIONS FOR ASTHMA IN PRESCHOOL-CHILDREN - RELATIONSHIP TO MAJOR ROADS IN BIRMINGHAM, UNITED-KINGDOM
    EDWARDS, J
    WALTERS, S
    GRIFFITHS, RK
    [J]. ARCHIVES OF ENVIRONMENTAL HEALTH, 1994, 49 (04): : 223 - 227
  • [24] Traffic air pollution and mortality rate advancement periods
    Finkelstein, MM
    Jerrett, M
    Sears, MR
    [J]. AMERICAN JOURNAL OF EPIDEMIOLOGY, 2004, 160 (02) : 173 - 177
  • [25] Health assessment of polycyclic aromatic hydrocarbon mixtures: Current practices and future directions
    Flowers, L
    Rieth, SH
    Cogliano, VJ
    Foureman, GL
    Hertzberg, R
    Hofmann, EL
    Murphy, DL
    Nesnow, S
    Schoeny, RS
    [J]. POLYCYCLIC AROMATIC COMPOUNDS, 2002, 22 (3-4) : 811 - 821
  • [26] Characterization of organic ambient aerosol during MIRAGE 2006 on three platforms
    Gilardoni, S.
    Liu, S.
    Takahama, S.
    Russell, L. M.
    Allan, J. D.
    Steinbrecher, R.
    Jimenez, J. L.
    De Carlo, P. F.
    Dunlea, E. J.
    Baumgardner, D.
    [J]. ATMOSPHERIC CHEMISTRY AND PHYSICS, 2009, 9 (15) : 5417 - 5432
  • [27] Hand J. L., 2011, SPATIAL SEASONAL PAT
  • [28] A simplified description of the evolution of organic aerosol composition in the atmosphere
    Heald, C. L.
    Kroll, J. H.
    Jimenez, J. L.
    Docherty, K. S.
    DeCarlo, P. F.
    Aiken, A. C.
    Chen, Q.
    Martin, S. T.
    Farmer, D. K.
    Artaxo, P.
    [J]. GEOPHYSICAL RESEARCH LETTERS, 2010, 37
  • [29] Health Effects Institute Panel on the Health Effects of Traffic-Related Air Pollution, 2010, TRAFF REL AIR POLL C
  • [30] The role of a mitochondrial pathway in the induction of apoptosis by chemicals extracted from diesel exhaust particles
    Hiura, TS
    Li, N
    Kaplan, R
    Horwitz, M
    Seagrave, JC
    Nel, AE
    [J]. JOURNAL OF IMMUNOLOGY, 2000, 165 (05) : 2703 - 2711