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Evolution of Atmospheric Aerosols Along Trajectories Crossing the Los Angeles Basin February 15, 2001 Lara H. Gertler (UC-Riverside) Jonathan O. Allen (Arizona State University) Sylvia H. Pastor (UC-Riverside) Glen R. Cass (Georgia Inst. of Technology) Kimberly A. Prather (UC-Riverside)
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Problems Models used to predict particle population to aid design of effective control programs –Experimental data difficult to obtain: want size distribution of chemical composition and at single particle level within same air parcel over time to evaluate trajectory model for externally mixed aerosol
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Research Objectives Acquire field experimental data documenting particle chemical evolution over time within individual air parcels –Data specifically for use in future air quality model evaluation studies
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Approach to gathering trajectory-based size and chemical composition data: Choose air monitoring sites along a typical air parcel trajectory Pair conventional samplers with aerosol time- of-flight mass spectrometry (ATOFMS) instruments collecting single particle data After sampling, identify air parcel trajectories that successively passed over multiple sites Examine particle population changes during transport along these trajectories
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Vehicle-Oriented Trajectory Study August, 1997 Focused on air parcels exposed to motor vehicle primary emissions
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Nitrate-Oriented Trajectory Study September-November, 1997 Examined particulate ammonium nitrate formation with exposure to large NH 3 (g) source
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Instrumentation Filter-based sampling –PM 10 (D a < 10 m) –Fine particulate matter (D a < 1.8 m) Electrical aerosol analyzer (EAA) Laser optical particle counter (OPC) Pair of micro-orifice impactors (MOI) Aerosol time-of-flight mass spectrometry (ATOFMS) instrument
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Vehicle-Oriented Trajectory August 27-28, 1997 8/27 14:00-18:00 8/27-28 18:00-01:00 01:00-06:00 06:00-10:00
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Fine PM Mass Balance Central Los Angeles Aug 27-28, 1997 Strong diurnal cycle, maximum during daylight Carbon dominates fine PM mass 240612182406121824 0 20 40 60 Concentration ( g m -3 ) 27-Aug28-Aug Central Los Angeles
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Impactor Mass Balances Central Los Angeles Aug 28, 1997 06:00-10:00 PDT14:00-18:00 PDT Elemental carbon peaks during morning traffic Decrease in fine carbon particles later in day Shift in carbon peak NO 3 - mainly present >1.0 m, as NaNO 3
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Fine PM Mass Balance Along Trajectory Local quarry source in Azusa Increase in EC, org. matter with rush hour Little change in other species 240612182406121824 0 20 40 60 Concentration ( g m -3 ) 21-Aug22-Aug Los Angeles Azusa
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Nitrogen Balance Along Trajectory Little ammonium nitrate formation NO, NO 2 increase with morning rush hour
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Single-Particle Evolution Along Trajectory 1.8 – 3.5 m Azusa before 06:00 very similar to Central LA Increase in carbon-containing particles, “complex” particles with rush hour Central LA 8/21 14:00-18:00 PDT Azusa 8/22 06:00-10:00 PDT
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Single-Particle Evolution Along Trajectory 1.0 – 1.8 m Azusa dust presence from local quarry source Increased ammonium presence Central LA 8/21 14:00-18:00 PDT Azusa 8/22 06:00-10:00 PDT
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Single-Particle Evolution Along Trajectory 0.56 – 1.8 m Higher presence of “carbon-only” particles in Central LA during evening rush hour More “complex” carbon particles in Azusa Central LA 8/21 14:00-18:00 PDT Azusa 8/22 06:00-10:00 PDT
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Nitrate-Oriented Trajectory Study Diamond Bar - Mira Loma October 31-November 1. 1997 10/31 06:00-10:00 10/31-11/1 18:00-01:00
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Fine PM Mass Balance Diamond Bar Oct 31-Nov 1, 1997 EC peak weekday rush hour, not weekend Air sampled in 1400-1800 minimum spent 1-2 fewer days over land
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Impactor Mass Balances Diamond Bar Oct 31, 1997 10:00-14:00 PST 14:00-18:00 PDT Aerosol NH 4 NO 3 in particles > 0.3 m Morning: NH 4 NO 3 production, air stagnated northeast Afternoon: relatively clean, air stagnated west
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Nitrogen Balance Along Trajectory Ammonium nitrate HNO 3 -limited in Diamond Bar Gas-phase ammonia concentration increases 5 240612182406121824 0 50 100 150 200 Concentration ( g N m -3 ) 31-Oct01-Nov Diamond Bar Mira Loma
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Fine PM Mass Balance Along Trajectory Note Federal Ambient Air Quality Standard: 65 g m -3 240612182406121824 0 50 100 150 Concentration ( g m -3 ) 31-Oct01-Nov Diamond Bar Mira Loma
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11/1 01:00-06:00 10/31 01:00-06:00 Nitrate-Oriented Trajectory Study Mira Loma - Riverside October 31-November 1, 1997
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Nitrogen Balance Along Trajectory Air parcel over land ~3 days before Mira Loma NH 3 concentration decrease with distance from dairy “point source” 240612182406121824 0 50 100 150 200 Concentration ( g N m -3 ) 31-Oct01-Nov Mira Loma Riverside
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Fine PM Mass Balance Along Trajectory Ammonium and nitrate concentrations similar 240612182406121824 0 50 100 150 Concentration ( g m -3 ) 31-Oct01-Nov Mira Loma Riverside
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Change in Particle Population with Wind Shift 1.8 – 3.5 m Number of fine particles decreases by 86% After shift, population dominated by dust and “uncomplex” particles Riverside 11/1 01:00-06:00 PST Wind from West Riverside 11/1 10:00-14:00 PST Wind from North
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Further Work Trajectory-based data on particle evolution designed for use in air quality model evaluation –Impactor data along Sept 24-25,1996 Long Beach - Fullerton - Riverside trajectory already utilized this way –Next use impactor data from Vehicle- and Nitrate-Oriented Trajectory studies
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Simultaneous operation of impactors and ATOFMS instruments allows calculation of ATOFMS counting efficiencies and ion sensitivities –Counting efficiencies and NO 3 - and NH 4 + ion sensitivities determined for 1996 data –Further counting efficiency and ion sensitivity investigation using 1997 data –Investigation of “matrix effects”
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Thanks for funding from: California Air Resources Board Coordinating Research Council, Inc. U.S. DOE Office of Heavy Vehicle Technologies Thanks for assistance and contributions from: Dr. Kimberly Prather’s UC-Riverside research group Dr. Mike Kleeman (UC-Davis) Lynn Salmon (Caltech) Dr. Michael Ames (MIT) Nehzat Motallebi (CARB) Joe Cassmassi (SCAQMD) Rudy Eden (SCAQMD) Kevin Durkee (SCAQMD) Leon Dolislager (CARB) Clinton Taylor (CARB)
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