A platform for research: civil engineering, architecture and urbanism
Number concentration and size distribution of ultrafine particles on the roadside of the Tateyama-Kurobe Alpine route, Japan
Measurements of ultrafine particles (UFPs) with diameters smaller than 100 nm were made with a Scanning Mobility Particle Sizer on the roadside of the Tateyama-Kurobe Alpine route on the western slope of Mt. Tateyama, Japan, in the summer and autumn of 2007 and 2008. The number concentrations of nanoparticles (NPs) with diameters smaller than 50 nm increased sharply in the morning. This increase agreed with that of the NO concentration, which is a good indicator of vehicle emissions. Although the peak concentration of NO was also detected in the late afternoon, the concentrations of NPs did not increase. The vehicle emission of UFPs may vary considerably with the driving conditions. The emission of NPs might have been accelerated under a high engine-load condition. The NP concentrations in October were much higher than those in August, although there were more buses in August than in October. The number size distribution in the morning was bimodal, with the first peak around 20–30 nm and the second one around 70–80 nm. The first peak became small during the daytime. The first peak disappeared, and a small second peak remained through midnight.
Number concentration and size distribution of ultrafine particles on the roadside of the Tateyama-Kurobe Alpine route, Japan
Measurements of ultrafine particles (UFPs) with diameters smaller than 100 nm were made with a Scanning Mobility Particle Sizer on the roadside of the Tateyama-Kurobe Alpine route on the western slope of Mt. Tateyama, Japan, in the summer and autumn of 2007 and 2008. The number concentrations of nanoparticles (NPs) with diameters smaller than 50 nm increased sharply in the morning. This increase agreed with that of the NO concentration, which is a good indicator of vehicle emissions. Although the peak concentration of NO was also detected in the late afternoon, the concentrations of NPs did not increase. The vehicle emission of UFPs may vary considerably with the driving conditions. The emission of NPs might have been accelerated under a high engine-load condition. The NP concentrations in October were much higher than those in August, although there were more buses in August than in October. The number size distribution in the morning was bimodal, with the first peak around 20–30 nm and the second one around 70–80 nm. The first peak became small during the daytime. The first peak disappeared, and a small second peak remained through midnight.
Number concentration and size distribution of ultrafine particles on the roadside of the Tateyama-Kurobe Alpine route, Japan
Watanabe, Koichi (author) / Honoki, Hideharu (author) / Endo, Fuminori (author) / Murakami, Takashi (author) / Yoshida, Yuki (author) / Iida, Hajime (author) / Uehara, Yoshitoshi (author) / Kume, Atsushi (author)
Journal of Environmental Science and Health, Part A ; 46 ; 921-930
2011-07-15
10 pages
Article (Journal)
Electronic Resource
Unknown
Online Contents | 1983
|Size Distribution and Characterization of Ultrafine Particles in Roadside Atmosphere
Online Contents | 2004
|Hydroelectric stations on the azusa and kurobe rivers in Japan
Springer Verlag | 1970
|Hydroelectric stations on the azusa and kurobe rivers in Japan
Online Contents | 1970
|