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dc.contributor.authorOndracek, J.en_US
dc.contributor.authorSchwarz, J.en_US
dc.contributor.authorZdimal, V.en_US
dc.contributor.authorAndelova, L.en_US
dc.contributor.authorVodicka, R.en_US
dc.contributor.authorBizek, V.en_US
dc.contributor.authorTsai, C. -J.en_US
dc.contributor.authorChen, S. -C.en_US
dc.contributor.authorSmolik, J.en_US
dc.date.accessioned2014-12-08T15:27:27Z-
dc.date.available2014-12-08T15:27:27Z-
dc.date.issued2011-09-01en_US
dc.identifier.issn1352-2310en_US
dc.identifier.urihttp://dx.doi.org/10.1016/j.atmosenv.2011.06.036en_US
dc.identifier.urihttp://hdl.handle.net/11536/19725-
dc.description.abstractTwo measurement campaigns near busy freeway and suburban crossroad (different traffic intensity) were carried out in Prague city. Both of the two traffic related campaigns were supported with simultaneous measurements at suburban background site to compare measured values with corresponding city background. Extensive set of aerosol instrumentation was used during both campaigns at both measurement sites. Two aerosol spectrometer sets (SMPS and APS) were used to monitor aerosol particle number size distribution. Two BLPI provided information about mass size distribution and chemical composition of collected size resolved aerosol samples. The crossroad campaign was also supported by two EC/OC field analysers providing information about elemental and organic carbon concentrations. Consequent chemical analysis of collected size resolved samples comprised of ion chromatography (water soluble ions), PIXE (elements) and RBS (carbon). Results obtained from spectrometers and BLPIs showed that the main contribution of traffic in ultrafine size range can be attributed to direct exhaust emissions, while the coarse fraction was dominated mainly by regional background aerosol with small traces of brake and tyre abrasion as well as the resuspension of the road dust. Chemical analysis demonstrated that most of the water soluble ions can be found in fine fraction of mass distribution and mostly comes from regional background and long range transport. Most of major elements were found in coarse fraction of mass size distribution and it can be attributed to three different sources: abrasion of different vehicle parts (Fe, Cu, Mn and Zn), resuspension of the road dust (Si, Al, Ca) and long range transport or regional background (Ca and K). Elemental carbon concentration (diesel engine emissions) was found to be proportional to traffic intensity. (C) 2011 Elsevier Ltd. All rights reserved.en_US
dc.language.isoen_USen_US
dc.subjectRoad traffic aerosolen_US
dc.subjectNumber and mass size distributionen_US
dc.subjectChemical compositionen_US
dc.titleContribution of the road traffic to air pollution in the Prague city (busy speedway and suburban crossroads)en_US
dc.typeArticleen_US
dc.identifier.doi10.1016/j.atmosenv.2011.06.036en_US
dc.identifier.journalATMOSPHERIC ENVIRONMENTen_US
dc.citation.volume45en_US
dc.citation.issue29en_US
dc.citation.spage5090en_US
dc.citation.epage5100en_US
dc.contributor.department環境工程研究所zh_TW
dc.contributor.departmentInstitute of Environmental Engineeringen_US
dc.identifier.wosnumberWOS:000294091200003-
dc.citation.woscount11-
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