Abstract:There is growing evidence that fine airborne particulates could play the most important role in determining health effects. The aim of this work was to investigate the number concentration and size distributions of particulates in the exhausts of diesel vehicles (mainly buses) of different ages and make, operating under different loads. Particlesizing instruments used were the Scanning Mobility Particle Sizer (SMPS) and Aerodynamic Particle Sizer (APS). The average particle number concentration of the exhausts… Show more
“…The higher correlations of UFP number concentrations in the 60 < D p < 220 nm particle size range with PM-PAHs, BC, and particle surface area strongly reflect the dominant contribution of diesel vehicles to emissions of relatively larger particles (60 < D p < 220 nm) over the measurement period in our sampling area because PM-PAHs and BC are known to be emitted from diesel engines. Furthermore, as noted in the Introduction, the greater part of the particle number concentration from vehicle exhausts is in the 20-130 nm size range for diesel engines (Kittelson, 1998;Morawska et al, 1998) and in the 20-60 nm range for gasoline engines (Kittelson, 1998;Ristovski et al, 1998). Therefore, the linear relationships of the 60 < D p < 220 nm particle size range with PAHs and BC indicate the dominance of diesel exhaust emissions for relatively larger particles in our study area, although it was difficult to determine the relative contributions of vehicle emissions for smaller particles (6 < D p < 60 nm).…”
Section: Correlations Among Various Pollutantsmentioning
confidence: 97%
“…Among the anthropogenic particulate matter (PM) sources, emissions of industrial combustion processes and traffic-related emissions account for the highest contributions of both UFPs and FPs (Schauer et al, 1996;Shi et al, 1999;Cass et al, 2000;EPA, 2000;Harrison et al, 2000;Hitchins et al, 2000). For traffic-related emissions, the greater part of the particle number concentration from vehicle exhaust is in the 20-130 nm size range for diesel engines (Kittelson, 1998;Morawska et al, 1998) and in the 20-60 nm for gasoline engines (Kittelson, 1998;Ristovski et al, 1998). PM emissions from internal combustion engines have traditionally been regulated solely on the basis of total PM mass emissions (Kittelson et al, 2004a).…”
Spatial distributions of ultrafine particles (UFPs; 6 < D p < 560 nm) and related gaseous and particulate pollutants were estimated from on-road measurements undertaken on busy roadways of Seoul, Korea, using a mobile laboratory (ML). The objectives of the study were to determine the spatial variations in UFP size distributions and concentrations of associated gaseous and particulate pollutants and to observe the relationships of UFP number concentrations with other pollutants on roadways in an urban area in Korea. The pollutants associated with diesel vehicles such as black carbon (BC) and particlebound polycyclic aromatic hydrocarbons (PM-PAHs) exhibited a high determination coefficient (r 2 = 0.65), indicating the influence of diesel vehicles on emissions in the study area. Further supporting evidence for the influence of diesel vehicles on emissions was given by the higher determination coefficients of PM-PAHs and BC concentrations with larger sizeclassified particles, ranging from 60 < D p < 220 nm, than with total UFP number concentrations or smaller particles in the 6 < D p < 60 nm size range. Peak concentrations of measured pollutants were observed mostly at intersections, reflecting the relationships of transient driving modes (i.e., deceleration and acceleration) with emissions of UFPs, associated pollutants, and concentrated traffic volumes at such locations.
“…The higher correlations of UFP number concentrations in the 60 < D p < 220 nm particle size range with PM-PAHs, BC, and particle surface area strongly reflect the dominant contribution of diesel vehicles to emissions of relatively larger particles (60 < D p < 220 nm) over the measurement period in our sampling area because PM-PAHs and BC are known to be emitted from diesel engines. Furthermore, as noted in the Introduction, the greater part of the particle number concentration from vehicle exhausts is in the 20-130 nm size range for diesel engines (Kittelson, 1998;Morawska et al, 1998) and in the 20-60 nm range for gasoline engines (Kittelson, 1998;Ristovski et al, 1998). Therefore, the linear relationships of the 60 < D p < 220 nm particle size range with PAHs and BC indicate the dominance of diesel exhaust emissions for relatively larger particles in our study area, although it was difficult to determine the relative contributions of vehicle emissions for smaller particles (6 < D p < 60 nm).…”
Section: Correlations Among Various Pollutantsmentioning
confidence: 97%
“…Among the anthropogenic particulate matter (PM) sources, emissions of industrial combustion processes and traffic-related emissions account for the highest contributions of both UFPs and FPs (Schauer et al, 1996;Shi et al, 1999;Cass et al, 2000;EPA, 2000;Harrison et al, 2000;Hitchins et al, 2000). For traffic-related emissions, the greater part of the particle number concentration from vehicle exhaust is in the 20-130 nm size range for diesel engines (Kittelson, 1998;Morawska et al, 1998) and in the 20-60 nm for gasoline engines (Kittelson, 1998;Ristovski et al, 1998). PM emissions from internal combustion engines have traditionally been regulated solely on the basis of total PM mass emissions (Kittelson et al, 2004a).…”
Spatial distributions of ultrafine particles (UFPs; 6 < D p < 560 nm) and related gaseous and particulate pollutants were estimated from on-road measurements undertaken on busy roadways of Seoul, Korea, using a mobile laboratory (ML). The objectives of the study were to determine the spatial variations in UFP size distributions and concentrations of associated gaseous and particulate pollutants and to observe the relationships of UFP number concentrations with other pollutants on roadways in an urban area in Korea. The pollutants associated with diesel vehicles such as black carbon (BC) and particlebound polycyclic aromatic hydrocarbons (PM-PAHs) exhibited a high determination coefficient (r 2 = 0.65), indicating the influence of diesel vehicles on emissions in the study area. Further supporting evidence for the influence of diesel vehicles on emissions was given by the higher determination coefficients of PM-PAHs and BC concentrations with larger sizeclassified particles, ranging from 60 < D p < 220 nm, than with total UFP number concentrations or smaller particles in the 6 < D p < 60 nm size range. Peak concentrations of measured pollutants were observed mostly at intersections, reflecting the relationships of transient driving modes (i.e., deceleration and acceleration) with emissions of UFPs, associated pollutants, and concentrated traffic volumes at such locations.
“…In Brisbane, Australia, the concentration of submicrometer particles correlated strongly with the concentrations of NO x and CO Morawska et al, 1998b), suggesting that motor vehicle emissions constituted the main source of ultrafine particles. Under varying conditions, the number of emitted particles increased with increasing engine load, whereas the mean particle diameter decreased (Franz et al, 2000;Morawska et al, 1998a). In cities, cars are usually not driven at a constant speed; there is continuous acceleration and deceleration.…”
Abstract. Aerosol number size distributions have been measured since 5 May 1997 in Helsinki, Finland. The presented aerosol data represents size distributions within the particle diameter size range 8-400 nm during the period from May 1997 to March 2003. The daily, monthly and annual patterns of the aerosol particle number concentrations were investigated. The temporal variation of the particle number concentration showed close correlations with traffic activities. The highest total number concentrations were observed during workdays; especially on Fridays, and the lowest concentrations occurred during weekends; especially Sundays. Seasonally, the highest total number concentrations were observed during winter and spring and lower concentrations were observed during June and July. More than 80% of the number size distributions had three modes: nucleation mode (D p <30 nm), Aitken mode (20-100 nm) and accumulation mode (D p >90 nm). Less than 20% of the number size distributions had either two modes or consisted of more than three modes. Two different measurement sites were used; in the first (Siltavuori, 5.5.1997(Siltavuori, 5.5. -5.3.2001, the arithmetic means of the particle number concentrations were 7000 cm −3 , 6500 cm −3 , and 1000 cm −3 respectively for nucleation, Aitken, and accumulation modes. In the second site (Kumpula, 6.3.2001(Kumpula, 6.3. -28.2.2003) they were 5500 cm −3 , 4000 cm −3 , and 1000 cm −3 . The total number concentration in nucleation and Aitken modes were usually significantly higher during workdays than during weekends. The temporal variations in the accumulation mode were less pronounced. The lower concentrations at Kumpula were mainly due to building construction and also the slight overall decreasing trend during these years. During the site changing a period of simultaneous measurements over two weeks were performed showing nice correlation at both sites.
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