Gelişmiş Arama

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dc.contributor.authorGaga, Eftade Emine
dc.contributor.authorArı, Akif
dc.contributor.authorAkyol, Nesimi
dc.contributor.authorÜzmez, Özlem Özden
dc.contributor.authorKara, Melik
dc.contributor.authorChow, Judith C.
dc.contributor.authorOdabaşı, Mustafa
dc.date.accessioned2019-10-21T20:11:04Z
dc.date.available2019-10-21T20:11:04Z
dc.date.issued2018
dc.identifier.issn0048-9697
dc.identifier.issn1879-1026
dc.identifier.urihttps://dx.doi.org/10.1016/j.scitotenv.2018.06.227
dc.identifier.urihttps://hdl.handle.net/11421/20070
dc.descriptionWOS: 000444625900119en_US
dc.descriptionPubMed ID: 30189545en_US
dc.description.abstractA field study was performed in a rural tunnel to determine pollutant concentrations, sources and on road vehicle emission factors (EFs) of particulate matter, trace metals, elemental carbon (EC), organic carbon (OC), benzene, toluene, ethyl benzene and xylenes (BTEX), and polycyclic aromatic hydrocarbons (PAHs). Emission factors (EFs) for polychlorinated naphthalenes (PCNs) and polychlorinated biphenyls (PCBs) were also determined. A 12-day extensive sampling campaign during morning and afternoon periods at inlet and exit stations of the tunnel was conducted. Morphology of the particles was also investigated by Scanning Electron Microcopy (SEM). Correlation analysis, factor analysis and diagnostic PAH ratios were utilized to identify emission sources of trace metals. Identified sources include brake wear (33%), resuspension of road dust (15%), tyre wear (12%), exhaust emissions (10%), and lubricants (9%). Based on the PAH diagnostic ratios, major sources of PAHs were estimated as diesel emissions. EFs were comparable with the literature and varied from 31.5 to 295.4 mg vehicle(-1) km(-1) with an average of 129.2 +/- 80 mg vehicle(-1) km(-1) for PM2.5. PM2.5-10 EFs varied between 15.9 and 236.1 mg vehicle(-1) km(-1) with an average of 96 +/- 30 mg vehicle(-1) km(-1). Average EC EFs were 40.3 +/- 9.8 mg vehicle(-1) km(-1) for PM2.5 samples and 19.5 +/- 0.5 mg vehicle(-1) km(-1) for PM2.5-10 samples while OC EFs were 33.7 +/- 18 and 15.5 +/- 8.4 mg vehicle(-1) km(-1) for fine and coarse particles, respectively. EFs of elements were generally 2 (Al) to 59 (Mg) times higher than those previously reported in the literature. Compared to literature, relatively higher EFs for Sigma(13)PAHs (range: 48.1-168 mu g vehicle(-1) km(-1), average: 84.3 +/- 46.4 mu g vehicle(-1) km(-1)) were obtained. BTEX emission factors were in the range of 4.2 +/- 4.7 mg vehicle(-1) km(-1) (m + p-xylene) and 16.7 +/- 10.5 mg vehicle(-1) km(-1) (toluene). Average EFs for Sigma PCBs and Sigma PCNs were 12.06 +/- 5.3 mu g vehicle(-1) km(-1) and 88.9 +/- 70.4 ng vehicle(-1) km(-1), respectivelyen_US
dc.description.sponsorshipAnadolu University Research Fund [1103F065]en_US
dc.description.sponsorshipThis study was supported by Anadolu University Research Fund (1103F065). The authors wish to thank the General Directorate of Highways for letting us perform our measurements and the tunnel staff for their help during field measurements. We also thank to Mete Gaga for his kind help in this work.en_US
dc.language.isoengen_US
dc.publisherElsevier Science BVen_US
dc.relation.isversionof10.1016/j.scitotenv.2018.06.227en_US
dc.rightsinfo:eu-repo/semantics/closedAccessen_US
dc.subjectEmission Factorsen_US
dc.subjectTunnelen_US
dc.subjectPahsen_US
dc.subjectPcbsen_US
dc.subjectPcnsen_US
dc.subjectEcen_US
dc.subjectOcen_US
dc.subjectTrace Elementsen_US
dc.titleDetermination of real-world emission factors of trace metals, EC, OC, BTEX, and semivolatile organic compounds (PAHs, PCBs and PCNs) in a rural tunnel in Bilecik, Turkeyen_US
dc.typearticleen_US
dc.relation.journalScience of the Total Environmenten_US
dc.contributor.departmentAnadolu Üniversitesi, Mühendislik Fakültesi, Çevre Mühendisliği Bölümüen_US
dc.identifier.volume643en_US
dc.identifier.startpage1285en_US
dc.identifier.endpage1296en_US
dc.relation.publicationcategoryMakale - Uluslararası Hakemli Dergi - Kurum Öğretim Elemanıen_US
dc.contributor.institutionauthorGaga, Eftade Emine


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