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Introduction to the A&WMA 2002 Critical Review Visibility: Science and Regulation

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... Ultrafine (<100 nm) and fine (<2.5 m) suspended particulate matter (PM) fractions affect human health ( Mauderly & Chow, 2008; Pope & Dockery, 2006), visibility (Chow et al., 2002; Watson, 2002), and the earth's radiation balance (MacCracken, 2008; Princiotta, 2009). Because ultrafine particles contribute little to aerosol mass, PM 2.5 and PM 10 (particles with aerodynamic diameters less than 2.5 and 10 m, respectively) may not be appropriate indices for evaluating the effects of aerosols on human health (Biswas & Wu, 2005; Chow, Watson, Savage, et al., 2005; Seigneur, 2009). ...
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Size distributions of ambient aerosols at the Fresno Supersite were measured with four commerciallyavailable scanning mobility particle sizers (SMPS). TSI nano, TSI standard, Grimm, and MSP instrumentswere collocated at the Fresno Supersite and particle size distributions were measured continuously fromAugust 18 through September 18, 2005. For particles with diameters between 10 and 200 nm, differencesamong hourly-average ambient particle concentrations ranged from 0% between the TSI nano and Grimmin the 30-50nm size range to 39% between the Grimm and MSP in the 10-30nm size range. MSP concentrationswere 10-33% lower than those measured with the TSI standard for particles smaller than 200 nm.The TSI nano and TSI standard agreed to within 5% in their overlapping size range (10-84 nm). The TSInano and Grimm agreed to within 40% for 5-10nm particles.
... Atmospheric haze is common in the region. Visible plumes from industrial stacks, diesel trucks, twostroke motorcycles, smoke-belching cars, coal-burning, fire-places and stoves reveal many of the sources that cause regional haze (Chow et al., 2002; Watson 2002a, b). For example, the annual emissions of PM 10 , NO x , and SO 2 were as high as 258, 564 and 596 kt, respectively, in 1997 in PRDR (Hong Kong Environmental Protection Department, 2002). ...
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The concentrations of organic carbon (OC) and elemental carbon (EC) in atmospheric particles were investigated at eight sites in four cities (Hong Kong, Guangzhou, Shenzhen and Zhuhai) of the Pearl River Delta Region (PRDR), China, during winter and summer 2002. The comparison of summer and winter results was made in order to investigate spatial and seasonal variations. PM2.5 and PM10 samples were collected on pre-fired quartz filters with mini-volume samplers and analyzed by the thermal optical reflectance (TOR) method following the Interagency Monitoring of PROtected Visual Environments (IMPROVE) protocol. During summer, the average OC and EC concentrations in PM2.5 were 9.2 and 4.1 μg m–3, while those in PM10 were 12.3 and 5.2 μg m–3. Carbonaceous aerosol accounted for 38.0% of the PM2.5 and 32.9% of the PM10. The daily average OC, EC, PM2.5 and PM10 concentrations in PRDR were higher in winter than in summer. The average OC/EC ratio was 2.5 for PM2.5 and PM10, suggesting the presence of secondary organic aerosols. The estimated secondary organic carbons in PM2.5 and PM10 were 4.1 and 5.6 μg m–3, respectively. The OC and EC were found to be correlated in winter (correlation coefficient r=0.82) and summer (r=0.64), which implied that motor vehicle sources contributed to the ambient carbonaceous particles. The distribution of eight carbon fractions in OC and EC at eight sites was first reported in ambient samples in Asia, which also indicated that motor vehicle exhaust was the dominant contributor to carbonaceous particles.
... Source samples were taken from 09/23/99, through 02/25/00, to represent: (1) Texas fugitive dust (e.g., paved roads, unpaved roads, and soil) (termed geological material), (2) motor vehicle exhaust from gasoline-and diesel-fueled vehicles operated in Texas and Mexico, (3) wildfires simulated by controlled burns of wood and grass typical of Big Bend National Park, (4) coal-fired power station effluent and coal fly ash, (5) a refinery fluidized bed catalyst cracker, (6) cement kilns fired by coal, coke, scrap tires, and used oil filters, and (7) residential meat cooking. Hot stack, dilution stack, airborne plume, groundbased source-dominated, and grab/resuspension sampling methods have been applied to source profile characterization (Gordon et al., 1984; Chow et al., 1988; Hildemann et al., 1989; Houck, 1991; Watson and Chow, 2001; Watson et al., 2001a, 2002). Dilution stack, ground-based source-dominated, and grab/resuspension methods were used for these profiles. ...
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Representative PM2.5 and PM10 source emissions were sampled in Texas during the Big Bend Regional Aerosol Visibility and Observa (BRAVO) study. Chemical source profiles for elements, ions, and carbon fractions of 145 samples are reported for paved and unpaved road dust, soil dust, motor vehicle exhaust, vegetative burning, four coal-fired power stations, an oil refinery catalytic cracker, two cement kilns, and residential meat cooking. Several samples were taken from each emitter and source type, and these were averaged by source type, and in source subgroups based on commonality of chemical composition. The standard deviation represents the variability of the chemical mass fractions. BRAVO profiles differed in some respects from profiles measured elsewhere. High calcium abundances in geological dust, high selenium abundances in coal-fired power stations, and high antimony abundances in oil refinery catalytic cracker emissions were found. Abundances of eight thermally evolved carbon fractions [Atmos. Environ. 28 (15) (1994) 2493] differ among combustion sources, and a Monte Carlo simulation demonstrates that these differences are sufficient to differentiate among several carbon-emitters.
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The spatiotemporal distribution and chemical composition of atmospheric fine particles in areas around the Taiwan Strait were firstly investigated. Fine particles (PM2.5) were simultaneously collected at two sites on the west-side, one site at an offshore island, and three sites on the east-side of the Taiwan Strait in 2013–2014. Field sampling results indicated that the average PM2.5 concentrations at the west-side sampling sites were generally higher than those at the east-side sampling sites. In terms of chemical composition, the most abundant water-soluble ionic species of PM2.5 were SO42−, NO3−, and NH4+, while natural crustal elements dominated the metallic content of PM2.5, and the most abundant anthropogenic metals of PM2.5 were Pb, Ni and Zn. Moreover, high OC/EC ratios of PM2.5 were commonly observed at the west-side sampling sites, which are located at the downwind of major stationary sources. Results from CMB receptor modeling showed that the major sources of PM2.5 were anthropogenic sources and secondary aerosols at the both sides, and natural sources dominated PM2.5 at the offshore site. A consistent decrease of secondary sulfate and nitrate contribution to PM2.5 suggested the transportation of aged particles from the west-side to the east-side of the Taiwan Strait.
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