2007
DOI: 10.3155/1047-3289.57.5.551
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Particulate Emissions from U.S. Department of Defense Artillery Backblast Testing

Abstract: There is a dearth of information on dust emissions from sources that are unique to the U.S. Department of Defense testing and training activities. However, accurate emissions factors are needed for these sources so that military installations can prepare accurate particulate matter (PM) emission inventories. One such source, coarse and fine PM (PM 10 and PM 2.5 ) emissions from artillery backblast testing on improved gun positions, was characterized at the Yuma Proving Ground near Yuma, AZ, in October 2005. Fu… Show more

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Cited by 15 publications
(21 citation statements)
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“…Predictability and source characterization of entrained dust impacts would benefit from implementation of parameterized sources within air quality models. Efforts to better characterize the dust emission potential of military operations have recently been applied for artillery [1], tracked and wheeled vehicles [2,3], and rotorcraft operations near the surface [4]. Source characterization of a rotor wake is especially challenging because of the complex interaction of the wake with the ground and atmospheric surface layer (ASL).…”
Section: M-omentioning
confidence: 99%
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“…Predictability and source characterization of entrained dust impacts would benefit from implementation of parameterized sources within air quality models. Efforts to better characterize the dust emission potential of military operations have recently been applied for artillery [1], tracked and wheeled vehicles [2,3], and rotorcraft operations near the surface [4]. Source characterization of a rotor wake is especially challenging because of the complex interaction of the wake with the ground and atmospheric surface layer (ASL).…”
Section: M-omentioning
confidence: 99%
“…The strategy of the experiment was similar to that used to measure dust entrainment from other sources related to military operation such as artillery blasts [1] and tracked/wheeled vehicle movement over desert terrain [2]. The flight course was aligned normal to the wind direction, and dust measurement equipment was positioned downwind along an array parallel to the flight-course.…”
Section: M-omentioning
confidence: 99%
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“…US EPA regulations protecting visibility at Class I national parks, forests, and wilderness areas, mandate reductions in PM emissions. Some military activities are unique dust emission sources not found in the civilian environment, and previously not adequately characterized or accurately quantified (Cooke et al, 1999;Gillies et al, 2007;Moosmüller et al, 2005). The nature of the ground surface/atmosphere interface determines in part the amount of dust being emitted and transported to impacted areas.…”
Section: Introductionmentioning
confidence: 99%
“…Even so, samplers were at different distances from nearby sources which might affect their particle collection. Anemometers and wind vanes were installed on masts (Ecotech, 2011;Thermo Scientific, 2011;Tisch, 2011;Watson and Chow, 2011)  PM 10 FRM sampler draws air into a G1200 inlet (anodized spun aluminum with a single stage of opposing jet) at 1133 L/min with a cut point of 9.7 ± 1.5 µm  A carbon-vane blower is used to pull air through a 20.32 × 25.4 cm QMA (Whatman Clifton, NJ, USA) quartz-fiber filter  The inlet housing consists of a clamshell that can be opened to grease and clean the impaction plate  The sampler is switched on and off with a timer http://www.tisch-env.com/  BAMs draw air through a louvered PM 10 FRM inlet at 16.7 L/min then through a glass-fiber filter tape  A radioactive source (low-level C 14 ) generates a stream of electrons (beta rays) through the sample spot as the particle deposit accumulates  As the filter spots load up, the penetrated electron count decreases proportionally to the sample loading  Filter tape advances as it reaches selected mass loadings (E-BAM uses a scintillation probe detector)  Uses a dual-diaphragm pump  Optional wind sensors can be installed at 1 m above ground level (agl) (Kuhns et al, 2001;Kuhns et al, 2005;Etyemezian et al, 2006;Gillies et al, 2007)  A light-scattering nephelometer using a longwavelength laser (λ = 780 nm) calibrated with Arizona road dust  Air is sampled through a PM 10 inlet at 1. (Peters et al, 2006;Heim et al, 2008;Hoffmann et al, 2008;Grimm, 2009;Grimm and Eatough, 2009)  Individual particles pass through the sensing cells, operated at 1.2 L/min, are illuminated by a λ = 795 nm diode laser with size bins from 0.3-20 µm  Mass concentrations are estimated by assuming spherical particles and uniform particle densities for each size bin, and summing the size bins up to obtain PM 2.5 or PM 10 http://www.grimm-aerosol.com/  Weight: 2.4 kg  Dimensions a : 24 × 12 × 6  Powered by 12V rechargeable battery (9 hr) or 110/220V AC with external power supply .…”
Section: Methodsmentioning
confidence: 99%