Literature DB >> 9695180

Polycyclic aromatic hydrocarbons (PAH) and diesel engine emission (elemental carbon) inside a car and a subway train.

H Fromme1, A Oddoy, M Piloty, M Krause, T Lahrz.   

Abstract

Significant concentrations of potentially harmful substances can be present in the interior of vehicles. The main sources of PAHs and elemental carbon (EC) inside a car are likely to be combustion emissions, especially from coal and traffic. The same sources can also be important for the interior of a subway train for which there are specific sources in the tunnel system, for example diesel engines. Twice, in summer 1995 and winter 1996 polycyclic aromatic hydrocarbons (PAH) and diesel motor emission (estimated as elemental carbon) were determined in the interior of a car (a 2-year-old VW Golf with a three-way catalytic converter) and in the passenger compartment of a subway train (below ground). On each sampling day (in total 16 daily measurements in the car and 16 in the subway) the substances were determined in the breathing zone of the passengers from 07:00 h to 16:00 h under different meteorologic conditions (winter- and summertime). The car followed the route of the subway from the western Berlin borough of Spandau to the south-eastern borough of Neukölln, and back. The sampling represented a realistic exposure model for driving in a high traffic and polluted urban area. The electric subway train (also 2 years in use) connected the same parts of Berlin (31 km underground). The mean values obtained during the two measurement periods (summer/winter) inside the car were 1.0 and 3.2 ng/m3 for benzo[a]pyrene, 10.2 and 28.7 ng/m3 for total-measured-PAHs, 14.1 and 8.2 micrograms/m3 for EC and in the subway 0.7 and 4.0 ng/m3 for benzol[a]pyrene, 30.2 and 67.5 ng/m3 for total PAHs, 109 and 6.9 micrograms/m3 for EC. A comparison between subway and car exposures shows significantly higher concentrations of PAHs in the subway train, which can be explained by relatively high concentrations of fluoranthene and pyrene in the subway. So far a satisfactory explanation has not been found, but one source might be the wooden railway ties which were formerly preserved with tar based products. In wintertime in both transportation systems the concentrations of beno[a]pyrene are three to four times higher than in summer corresponding to the changing of the ambient air concentrations.

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Year:  1998        PMID: 9695180     DOI: 10.1016/s0048-9697(98)00189-2

Source DB:  PubMed          Journal:  Sci Total Environ        ISSN: 0048-9697            Impact factor:   7.963


  13 in total

1.  Concentration and characterization of airborne particles in Tehran's subway system.

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Journal:  Environ Sci Pollut Res Int       Date:  2014-02-27       Impact factor: 4.223

2.  Fine particulate-bound polycyclic aromatic hydrocarbons in vehicles in Rome, Italy.

Authors:  Paola Romagnoli; Catia Balducci; Angelo Cecinato; Nunziata L'Episcopo; Claudio Gariazzo; Maria Pia Gatto; Andrea Gordiani; Monica Gherardi
Journal:  Environ Sci Pollut Res Int       Date:  2016-11-22       Impact factor: 4.223

3.  Source attribution of personal exposure to airborne polycyclic aromatic hydrocarbon mixture using concurrent personal, indoor, and outdoor measurements.

Authors:  Hyunok Choi; John Spengler
Journal:  Environ Int       Date:  2013-12-04       Impact factor: 9.621

4.  Air quality and PM10-associated poly-aromatic hydrocarbons around the railway traffic area: statistical and air mass trajectory approaches.

Authors:  Nazrul Islam; Shahadev Rabha; Luis F O Silva; Binoy K Saikia
Journal:  Environ Geochem Health       Date:  2019-02-19       Impact factor: 4.609

5.  Identification of polycyclic aromatic hydrocarbons in unleaded petrol and diesel exhaust emission.

Authors:  Vinay Kumar Yadav; Sahdeo Prasad; Devendra K Patel; Altaf Husain Khan; Madhu Tripathi; Yogeshwer Shukla
Journal:  Environ Monit Assess       Date:  2009-07-23       Impact factor: 2.513

6.  Exposure to carcinogenic polycyclic aromatic compounds and health risk assessment for diesel-exhaust exposed workers.

Authors:  J-J Sauvain; T Vu Duc; M Guillemin
Journal:  Int Arch Occup Environ Health       Date:  2003-05-16       Impact factor: 3.015

7.  Comparison of polycyclic aromatic hydrocarbon emissions on gasoline- and diesel-dominated routes.

Authors:  Chung-Yih Kuo; Po-Shan Chien; Wan-Ching Kuo; Chien-Tai Wei; Jui-Yeh Rau
Journal:  Environ Monit Assess       Date:  2012-11-06       Impact factor: 2.513

Review 8.  Cancer risk assessment, indicators, and guidelines for polycyclic aromatic hydrocarbons in the ambient air.

Authors:  Carl-Elis Boström; Per Gerde; Annika Hanberg; Bengt Jernström; Christer Johansson; Titus Kyrklund; Agneta Rannug; Margareta Törnqvist; Katarina Victorin; Roger Westerholm
Journal:  Environ Health Perspect       Date:  2002-06       Impact factor: 9.031

9.  Black carbon and particulate matter (PM2.5) concentrations in New York City's subway stations.

Authors:  M J Ruzmyn Vilcassim; George D Thurston; Richard E Peltier; Terry Gordon
Journal:  Environ Sci Technol       Date:  2014-11-26       Impact factor: 9.028

10.  Monitoring of environmental exposure to polycyclic aromatic hydrocarbons: a review.

Authors:  K Srogi
Journal:  Environ Chem Lett       Date:  2007-11-01       Impact factor: 9.027

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