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Characterization of Aerosol Physical, Optical and Chemical Properties During the B ig Bend R egional A erosol and V isibility O bservational S tudy (BRAVO) Jenny Hand* Eli Sherman*, Sonia Kreidenweis*, Jeff Collett, Jr.*, Taehyoung Lee*, Derek Day and Bill Malm
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Characterization of Aerosol Physical, Optical and Chemical Properties During the Big Bend Regional Aerosol and Visibility Observational Study (BRAVO) Jenny Hand* Eli Sherman*, Sonia Kreidenweis*, Jeff Collett, Jr.*, Taehyoung Lee*, Derek Day and Bill Malm Colorado State University *Atmospheric Science CIRA/National Park Service Funding by National Park Service
OUTLINE • Motivation for participating in BRAVO • Chemical measurements and preliminary results • Fine (PM2.5) and Coarse (PM10- PM2.5) species • Size distribution measurements • Experimental set-up and instrument calibration • Alignment method: retrieved refractive index and density • Comparisons between chemical and physical properties • Optical properties: column and point measurements • bsp (fine and coarse), aer, Ångstrom exponent • Summary
BRAVO STUDY • July - October 1999 • Big Bend NP has some of the poorest visibility of any monitored Class 1 area in the western U.S. • Seasonal trends • Sulfates: highest in summer • Organic carbon: highest in spring • Blowing soil: highest in July (Saharan dust episodes) • (Gebhart et al., 2000) • Recent work in Grand Canyon NP demonstrated that discrepancies of up to 50% or more exist between measured and reconstructed extinction (Malm and Day, 2000) • Particle absorption or coarse scattering?
Aerosol Chemistry Measurements • PM2.5 composition • CSU: daily samples, on-site analyses of major ionic species and particle acidity • IMPROVE: daily samples: major ionic species, plus soil, organic and elemental carbon • PM10 composition • IMPROVE: daily samples: major ionic species, plus soil, organic and elemental carbon Coarse composition (PM10 - PM2.5) • Ionic species’ particle size distribution: MOUDI samples • Aethalometer- black carbon
Aerosol Size Distribution Measurements • Dry size distributions were measured continuously ranging from 0.05< Dp< 20 µm • Instruments: • TSI Differential Mobility Analyzer (DMA): • 0.05 < Dp < 0.87 µm (21 bins) • PMS Optical Particle Counter (OPC): • 0.1 < Dp < 2 µm (8 bins) • TSI Aerodynamic Particle Sizer 3320 (APS): • 0.5 < Dp < 20 µm (51 bins) • Pre-, during-, and post-study calibration were performed using PSL, ammonium sulfate and oleic acid.
Instrument Calibration • Empirical equations determined from instrument calibration relate real refractive index to OPC channel diameter (Dopt Dp) • Channel collection efficiencies were determined • Effective density (e) was related to APS channel diameter (Dae Dp) by the following equation: • where
Examples of Aligned and Unaligned DMA and OPC Volume Distributions Unaligned Aligned
Example of Combined Volume Distribution BRAVO 991008
Comparisons between • chemical and physical properties • Refractive index and density: retrieved from alignment method and calculated from chemical composition • Total (PM10) reconstructed mass and M = Vtot from size distributions, assuming X=1.2 • MOUDI mass size distributions and volume distributions • EC and aethalometer measurements
Accumulation Mode Parameters Dgv g
Coarse Mode Parameters Dgv g
Refractive Index and Density • Real refractive index and effective density were retrieved from size distribution alignment method • Values based on chemistry were calculated using a volume weighted method: • and • Species included: • (NH4)2SO4: m = 1.53, = 1.76 g cm-3 • OC: m = 1.55, = 1.4 g cm-3 • EC: m = 1.96 - 0.66i, = 2.0 g cm-3 • NH4NO3: m = 1.554, = 1.725 g cm-3 • Soil: SiO2, Al2O3, Fe2O3, CaO, TiO2 (IMPROVE)
Total Mass Comparisons • PM10 total mass concentration • M = Vtot, assuming X = 1.2
Calculations of Light Scattering Coefficient (bsp) • bsp was calculated using combined volume distributions and converged values of refractive index • Qspis the Mie scattering efficiency assuming spherical particles. • bsp was calculated for the accumulation and coarse particle modes
Dry Mass Scattering Efficiency Accumulation Mode Coarse Mode
Calculation of Aerosol Optical Depth (aer) • USDA UV-B radiation monitoring program has a fully instrumented site approximately 30 miles from BRAVO site in Big Bend National Park • YES visible Multi-Filter Rotating Shadowband Radiometer measures irradiance with seven wavelength channels: 415, 500, 610, 665, 860, and 940 nm (Bigelow et al., 1998) • Rayleigh and ozone optical depths were removed from column measurements of total optical depth • Clouds and high sun angle measurements were removed • Point measurements of aer were determined by assuming a well-mixed layer and estimates of boundary layer heights
Aerosol Optical Depth at 500 nm August 15, 1999 October 12, 1999
Ångstrom Wavelength Exponent () • Calculated for both point and column measurements over the wavelength range from 415 nm - 860 nm (Eck et al., 1999 & Reid et al., 1999) • Two days were chosen for comparison, demonstrating very different aerosol physical, chemical and optical properties Column: Point:
Ångstrom wavelength exponent (415 - 860 nm) August 15, 1999 October 12, 1999
Correlations between bsp and aer were found for several days:
Correlations between bext and aer were found for all months:
Correlations between CSUand UVB were found for all months:
Summary • Sulfate was typically the major chemical species in the fine mode, although soil and OC were important during certain events • Size distributions suggested that high coarse mode volume contributed significantly to total volume, especially during suspected Saharan dust events • A new alignment method allowed for retrieving refractive index and effective density, in agreement with calculated values • Calculated light scattering coefficients agreed well with measured values, and demonstrated periods when coarse scattering was important, often during suspected Saharan dust events
Summary, continued • Time resolved sulfate measurements were observed to trend with light scattering coefficients, suggesting sulfate was the major contributor to visibility degradation during the study • MOUDI mass distributions compared well with measured volume distributions • Column and point measurements of aerosol optical depth were observed to be correlated for several days investigated • Angstrom wavelength exponents agreed well between the two methods, and reflected the different aerosol types observed