Abstract:Public housing developments across the United States are being demolished, potentially increasing local concentrations of particulate matter (PM) in communities with high burdens of severe asthma. Little is known about the impact of demolition on local air quality. At three public housing developments in Chicago, IL, PM with an aerodynamic diameter Ͻ10 m (PM 10 ) and Ͻ2.5 m were measured before and during high-rise demolition. Additionally, size-selective sampling and real-time monitoring were concurrently per… Show more
“…All such building activities 46 are known to release significant amounts of coarse particles into the local 47 environment. For instance, Dorevitch et al (2006) found a 74% increase in PM 10 48 (particulate matter with 10 m aerodynamic diameter) concentrations 100 m 49 downwind of a high-rise building demolition site in Chicago, USA. Likewise, 50 Fuller et al (2002) showed that fugitive PM 10 emissions produced from building 51 works at Marylebone Road in London during September 1999 contributed to daily 52 mean PM 10 concentrations in excess of 50 g m -3 .…”
10Building activities are recognised to produce coarse particulate matter but less is 11 known about the release of airborne ultrafine particles (UFPs; those below 100 nm 12 in diameter). For the first time, this study has investigated the release of particles 13 in the 5-560 nm range from three simulated building activities: the crushing of 14 concrete cubes, the demolition of old concrete slabs, and the recycling of concrete 15 debris. A fast response differential mobility spectrometer (Cambustion DMS50) 16 was used to measure particle number concentrations (PNC) and size distributions 17(PNDs) at a sampling frequency of 10 Hz in a confined laboratory room providing 18 controlled environment and near-steady background PNCs. The sampling point 19 was intentionally kept close to the test samples so that the release of new UFPs 20 during these simulated processes can be quantified. Tri-modal particle size 21distributions were recorded for all cases, demonstrating different peak diameters 22 in fresh nuclei (<10 nm), nucleation (10-30 nm) and accumulation (30-300 nm) 23 modes for individual activities. The measured background size distributions 24showed modal peaks at about 13 and 49 nm with average background PNCs 25 ~1.4710 4 cm -3 . These background modal peaks shifted towards the larger sizes 26 during the work periods (i.e. actual experiments) and the total PNCs increased 27 between 2 and 17 times over the background PNCs for different activities. After 28 adjusting for background concentrations, the net release of PNCs during cube 29 crushing, slab demolition, and "dry" and "wet" recycling events were measured as 30 ~0.77, 19.1, 22.7 and 1.76 (×10 4 ) cm -3 , respectively. The PNDs were converted 31 into particle mass concentrations (PMCs). While majority of new PNC release 32 was below 100 nm (i.e. UFPs), the bulk of new PMC emissions were constituted 33 by the particles over 100 nm; ~95, 79, 73 and 90% of total PNCs, and ~71, 92, 93 34 and 91% of total PMCs, for cube crushing, slab demolition, dry recycling and wet 35 recycling, respectively. The results of this study firmly elucidate the release of 36UFPs and raise a need for further detailed studies and designing health and safety 37 related exposure guidelines for laboratory workplaces and operational building 38 sites. 39
“…All such building activities 46 are known to release significant amounts of coarse particles into the local 47 environment. For instance, Dorevitch et al (2006) found a 74% increase in PM 10 48 (particulate matter with 10 m aerodynamic diameter) concentrations 100 m 49 downwind of a high-rise building demolition site in Chicago, USA. Likewise, 50 Fuller et al (2002) showed that fugitive PM 10 emissions produced from building 51 works at Marylebone Road in London during September 1999 contributed to daily 52 mean PM 10 concentrations in excess of 50 g m -3 .…”
10Building activities are recognised to produce coarse particulate matter but less is 11 known about the release of airborne ultrafine particles (UFPs; those below 100 nm 12 in diameter). For the first time, this study has investigated the release of particles 13 in the 5-560 nm range from three simulated building activities: the crushing of 14 concrete cubes, the demolition of old concrete slabs, and the recycling of concrete 15 debris. A fast response differential mobility spectrometer (Cambustion DMS50) 16 was used to measure particle number concentrations (PNC) and size distributions 17(PNDs) at a sampling frequency of 10 Hz in a confined laboratory room providing 18 controlled environment and near-steady background PNCs. The sampling point 19 was intentionally kept close to the test samples so that the release of new UFPs 20 during these simulated processes can be quantified. Tri-modal particle size 21distributions were recorded for all cases, demonstrating different peak diameters 22 in fresh nuclei (<10 nm), nucleation (10-30 nm) and accumulation (30-300 nm) 23 modes for individual activities. The measured background size distributions 24showed modal peaks at about 13 and 49 nm with average background PNCs 25 ~1.4710 4 cm -3 . These background modal peaks shifted towards the larger sizes 26 during the work periods (i.e. actual experiments) and the total PNCs increased 27 between 2 and 17 times over the background PNCs for different activities. After 28 adjusting for background concentrations, the net release of PNCs during cube 29 crushing, slab demolition, and "dry" and "wet" recycling events were measured as 30 ~0.77, 19.1, 22.7 and 1.76 (×10 4 ) cm -3 , respectively. The PNDs were converted 31 into particle mass concentrations (PMCs). While majority of new PNC release 32 was below 100 nm (i.e. UFPs), the bulk of new PMC emissions were constituted 33 by the particles over 100 nm; ~95, 79, 73 and 90% of total PNCs, and ~71, 92, 93 34 and 91% of total PMCs, for cube crushing, slab demolition, dry recycling and wet 35 recycling, respectively. The results of this study firmly elucidate the release of 36UFPs and raise a need for further detailed studies and designing health and safety 37 related exposure guidelines for laboratory workplaces and operational building 38 sites. 39
“…For example, Dorevitch et al (2006) measured PM10 during the demolition of a reinforced concrete building and found 6h averaged concentrations up to about 10-times higher compared with predemolition levels which are background concentrations in this case. Likewise, Beck et al (2003) found ambient levels of PM10 to increase by between 8 and 3000-times during implosion of a building compared with pre-demolition levels, depending on the distance of measurement point from the source.…”
Section: Particle Mass Concentrationsmentioning
confidence: 77%
“…As a consequence, it is essential to determine the exposure levels of operatives involved in building refurbishment as well as understanding the It has now been established that various size of particles arising from vehicle exhaust and non-vehicle exhaust sources enhance their concentrations in certain areas (Dall'Osto et al, 2011;Hopke et al, 1980;Kumar et al, 2010Kumar et al, , 2011bKumar et al, , 2013b. A few studies have also reported the particle number and mass emissions arising from the demolition of buildings and transport structures (Dorevitch et al, 2006;Hansen et al, 2008), concrete recycling and road works (Fuller et al, 2002;Fuller and Green, 2004).…”
Understanding of the emissions of coarse (PM10 ≤10 μm), fine (PM2.5 ≤2.5 μm) and ultrafine particles (UFP <100 nm) from refurbishment activities and their dispersion into the nearby environment is of primary importance for developing efficient risk assessment and management strategies in the construction and demolition industry. This study investigates the release, occupational exposure and physicochemical properties of particulate matter, including UFPs, from over 20 different refurbishment activities occurring at an operational building site. Particles were measured in the 5-10,000 nm size range using a fast response differential mobility spectrometer and a GRIMM particle spectrometer for 55 hours over 8 days.The UFPs were found to account for >90% of the total particle number
“…Subjects were recruited by community asthma educators in three Chicago public housing developments in which high rise demolition was taking place (Dorevitch et al, 2006 Eligible subjects had physician-diagnosed asthma, or were non-asthmatic family members of asthmatic subjects. Exclusion criteria were smoking, age less than 8 years, lung disease other than asthma, or daily use of oral corticosteroids.…”
The measurement of exhaled nitric oxide and carbon monoxide concentrations is an emerging method of monitoring airway inflammation longitudinally in community-based studies. Inhaled concentrations of these monoxides influence exhaled concentrations. Little is known about the degree to which inhaled concentrations distort temporal trends in, or estimated effects of air pollutants on, exhaled monoxides. We sought to evaluate whether estimated effects of air pollutants on exhaled monoxides are distorted by trends in indoor and outdoor monoxides, and to characterize determinants of exhaled monoxide concentrations among residents of public housing. In a panel study, 42 residents of public housing provided over 1000 exhaled breath samples. Samples from all subjects were analyzed for nitric oxide; samples from 27 of these subjects were also analyzed for carbon monoxide. The effects of indoor and outdoor monoxide concentrations on exhaled concentrations were quantified. Confounding of associations between particulate matter concentrations and exhaled nitric oxide concentrations was explored. Determinants of exhaled monoxide concentrations among public housing residents are similar to those of other populations. Exhaled monoxide concentrations are more strongly associated with indoor than with outdoor monoxide concentrations. Approximately half of the variability in exhaled monoxide concentrations over time can be explained by changes in indoor monoxide concentrations. Indoor monoxide concentrations can markedly distort both temporal trends in exhaled concentrations as well as estimated effects of particulate matter on exhaled monoxides. Prior estimated effects of particulate matter on exhaled nitric oxide concentrations may have been confounded by nitric concentrations indoors at the time of exhaled air collection. To prevent distortions of longitudinal trends in airway inflammation and estimated health effects of air pollutants, inspiratory scrubber use is necessary but not sufficient to remove the confounding effect of indoor monoxides, and analyses should adjust exhaled monoxide concentrations for concentrations indoors.
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