2006
DOI: 10.5194/acp-6-2215-2006
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Aerosol and NO<sub>x</sub> emission factors and submicron particle number size distributions in two road tunnels with different traffic regimes

Abstract: Abstract. Measurements of aerosol particle number size distributions (18-700 nm), mass concentrations (PM2.5 and PM10) and NO x were performed in the Plabutsch tunnel, Austria, and in the Kingsway tunnel, United Kingdom. These two tunnels show different characteristics regarding the roadway gradient, the composition of the vehicle fleet and the traffic frequency. The submicron particle size distributions contained a soot mode in the diameter range D=80-100 nm and a nucleation mode in the range of D=20-40 nm. I… Show more

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Cited by 44 publications
(16 citation statements)
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“…In contrast, the traffic-induced nucleation particles behave inversely, with lower concentration during the day in Ústí compared to Annaberg. This is explained by the fact that semivolatile material condenses preferably on the large surface area of the pre-existing soot particles (Imhof et al, 2006). If there is only a small surface area available, which is the case for Annaberg, new particles are formed by homogeneous nucleation.…”
Section: Sources Of Ultrafine Particlesmentioning
confidence: 99%
“…In contrast, the traffic-induced nucleation particles behave inversely, with lower concentration during the day in Ústí compared to Annaberg. This is explained by the fact that semivolatile material condenses preferably on the large surface area of the pre-existing soot particles (Imhof et al, 2006). If there is only a small surface area available, which is the case for Annaberg, new particles are formed by homogeneous nucleation.…”
Section: Sources Of Ultrafine Particlesmentioning
confidence: 99%
“…New secondary particle formation in ambient air is mostly attributed to nucleation and cluster/particle growth by condensation of photo-oxidised vapours (Morawska et al, 2008;Dunn et al, 2004) occurring some time after the emission (hours to days). The outcome of UFP depends widely on the pollutants concentrations in the air, thus when the urban atmosphere is highly polluted, the semi-volatile species condense onto pre-existing particles (Wichmann et al, 2000;Zhang et al, 2004;Imhof et al, 2006); however, when low PM pollution levels occur, the semi-volatile species may result in large numbers of nucleation-derived aerosols (Hämeri et al, 1996;Rönkkö et al, 2006). As previously reported, urban areas with high solar radiation intensities are favourable scenarios for nucleation processes (Johnson et al, 2005;Moore et al, 2007;Pey et al, 2008Pey et al, , 2009Fernández-Camacho et al, 2010;Cheung et al, 2010).…”
Section: Introductionmentioning
confidence: 99%
“…All the revisions of NAAQs call for more stringent controls of NO x emissions, especially in high-emitting sectors that include on-road vehicles Zhang et al, 2012). Among the different vehicle categories, attention has been focused on heavy-duty diesel vehicles (HDDVs, including buses and trucks) due to their significantly higher NO x emission factors and higher travel mileage relative to gasoline cars (Imhof et al, 2006;Liu et al, 2009;Thornhill et al, 2010). The Ministry of Environmental Protection (MEP) reported the first-ever total national NO x emissions from on-road vehicles of 5.3 Tg in 2009, of which diesel vehicles (dominated by heavy-duty trucks and buses) contributed 60 % (MEP, 2010).…”
Section: Y Wu Et Al: the Challenge To No X Emission Control For Heamentioning
confidence: 99%