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In-Vehicle Levels of Naphthalene and Monocyclic Aromatic Compounds According to Vehicle Type
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  • Journal title : Environmental Engineering Research
  • Volume 14, Issue 3,  2009, pp.180-185
  • Publisher : Korean Society of Environmental Engineering
  • DOI : 10.4491/eer.2009.14.3.180
 Title & Authors
In-Vehicle Levels of Naphthalene and Monocyclic Aromatic Compounds According to Vehicle Type
Jo, Wan-Kuen; Lee, Jong-Hyo;
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Only limited information is available as regards to the exposure levels of naphthalene (polycyclic aromatic hydrocarbons, PAHs) and monocyclic aromatic hydrocarbons(MAHs) in the interiors of diesel-fueled passenger cars, while many studies investigated the exposure levels of various volatile organic compounds(VOCs) in the interiors of gasoline-fueled passenger cars or public buses. Present study was performed to supplement this deficiency by measuring naphthalene (as a representative of PAHs) and MAHs levels inside five diesel-fueled and five gasoline-fueled passenger cars while morning and evening commuting on real roadways. Each car was surveyed five times on different sampling days. The in-vehicle naphthalene levels were higher for the diesel-fueled cars as compared to gasoline-fueled cars, whereas the results were reversed for the in-vehicle MAH levels. The median cabin levels of diesel-fueled cars were 1.3, 7, 13, 4, and 6 for naphthalene, benzene, toluene, ethyl benzene, and m,pxylene, respectively. With respect to gasoline-fueled cars, their respective levels were 0.7, 11, 21, 7, and 9 . The median MAHs concentration ratios of gasoline-fueled cars to diesel-fueled cars ranged from 1.50 to 1.75, while the median naphthalene concentration ratio was estimated to be 0.54. In addition, there was no significant difference of both naphthalene and MAHs between the diesel-fueled cars, but the in-vehicle levels were significantly different between gasoline-fueled cars. The concentration levels of both naphthalene and MAHs were higher in the passenger cars than other non-industrial microenvironments. Consequently, it was confirmed that the cabins of both diesel-fueled and gasoline-fueled passenger cars are an important microenvironment associated with the exposure to naphthalene and MAHs.
Naphthalene;Gasoline;Diesel;Passenger car;Commuting;
 Cited by
무기흡착제가 적용된 친환경 수성 코팅제의 특성 연구,신종섭;이정희;곽은미;윤종국;김현범;

폴리머, 2012. vol.36. 5, pp.622-627 crossref(new window)
Health Risk Assessment and Source Apportionment of PAHs in Industrial and Bitumen Contaminated Soils of Kermanshah Province; NW Iran,;;;

Toxicology and Environmental Health Sciences, 2016. vol.8. 3, pp.201-212 crossref(new window)
Health risk assessment and source apportionment of PAHs in industrial and bitumen contaminated soils of Kermanshah province; NW Iran, Toxicology and Environmental Health Sciences, 2016, 8, 3, 201  crossref(new windwow)
Jo, W. K. and Yu, C. H., “Public bus and taxicab driver's work-time exposure to aromatic volatile organic compounds,” Environ. Res., 86, 66-72 (2001). crossref(new window)

Chan, A. T. and Chung, M. W., “Indoor-outdoor air quality relationships in vehicle: effect of driving environment and ventilation modes,” Atmos. Environ., 37, 3795-3808 (2003). crossref(new window)

Som, D., Dutta, C., Chatterjee, A., Mallick, D., Jana, T. K., and Sen, S., “Studies on commuters' exposure to BTEX in passenger cars in Kolkata, India,” Sci. Total Environ., 372, 426-432 (2007). crossref(new window)

Kim, H. S., Kim, J. G., and Kim, K. S., “Study on atmospheric behavior of polycyclic aromatic hydrocarbons in urban area, jeonju,” Environ. Eng. Res., 12, 118-127 (2007). crossref(new window)

ATSDR (Agency for Toxic Substances and Disease Registry), ToxFAQs for Naphthalene, 1-Methylnaphthalene, and 2-Methylnaphthalene, Atlanta, GA, U.S. Department of Health and Human Services, Public Health Service (2005).

Kim, H. S., Shin, Y. S., Lee, D. S., Song, B. J., and Kim, J. G., “Estimation of rain scavenging ratio for particle bound polycyclic aromatic hydrocarbons and polychlorinated biphenyls,” Environ. Eng. Res., 11, 33-44. crossref(new window)

Li, .A, Schoonover, T. M., Zou, Q., Norlock, F., Conroy, L. M., Scheff, P. A., and Wadden, R. A., “Polycyclic aromatic hydrocarbons in residential air of ten Chicago area homes: Concentrations and influencing factors,” Atmos. Environ., 39, 3491-3501 (2005). crossref(new window)

Reisen, F. and Arey, J., “Atmospheric reactions influence seasonal PAH and nitro-PAH concentrations in the Los Angles,” Environ. Sci. Technol., 39, 64-73 (2005). crossref(new window)

Zuraimi, M. S., Roulet, C. A., Tham, K. W., Sekhar, S. C., David Cheong, K. W., Wong, N. H., and Lee, K. H., “A comparative study of VOCs in Singapore and European office buildings,” Build. Environ., 41, 316-329 (2006). crossref(new window)

USEPA (United States of Environmental Protection Agency), Health effects support document for naphthalene. EPA 822- R-03-005, Office of Water, Health and Ecological Criteria Division, Washington DC (2003).

IARC (International Agency for Research on Cancer), Monographs on the Evaluation of Carconogenic Risks to Humans, vol. 82, IARC, Lyon, France, p. 367 (2002).

Rodes, C., Sheldon, L., Whitaker. D., Clayton, A., Fitzgerald, K., Flanagan, J., DiGenova, F., Hering, S., and Frazier, C., “Measuring Concentrations of Selected Air Pollutants Inside California Vehicles,” Final report, ARB ContractNo. 95-339, California Air Resources Board, CA (1998).

Quynh Truc, V. T. and Kim Oanh, N. T., “Roadside BTEX and other gaseous air pollutants in relation to emission sources,” Atmos. Environ., 41, 7685-7697 (2007). crossref(new window)

USEPA (United States of Environmental Protection Agency), Cancer risk from outdoor exposure to air toxics. PA-450/ 1-90-004a (1990).

Liu, Y. and Fechter, L., “Toluene disrupts outer hair cell morphometry and intracellular calcium homeostasis in cochlear cells of guinea pigs,” Toxicol. Appl. Pharmacol., 142, 270-277 (1997). crossref(new window)

Fernandez-Bremauntz, A. A. and Ashmore, M. R., “Exposure of commuters to carbon monoxide in Mexico city- I. Measurement of in-vehicle concentrations,” Atmos. Environ., 29, 525-532 (1995). crossref(new window)

Rhead, M. M. and Pemberton, R. D., “Sources of naphthalene in diesel exhaust emissions,” Ener. Fuels, 10, 837-843 (1996). crossref(new window)

Marr, L. C., Kirchstetter, T. W., Harley, R. A., Miguel, A. H., Hering, S. V., and Hammond, S. K., “Characterization of polycyclic aromatic hydrocarbons in motor vehicle fuels and exhaust emissions,” Environ. Sci. Technol., 33, 3091- 3099 (1997). crossref(new window)

Lioy, P. J., Weisel, C. P., Jo, W. K., Pellizzari, E., and Raymer, J. H., “Microenvironmental and personal measurements of methyl-tertiary butyl ether (MTBE) associated with automobile use activities,” J. Exp. Anal. Environ. Epidemiol., 4, 427-441 (1994).

Kim, K. H., Shon, Z. H., Kim, M. Y., Sunwoo, Y., Jeon, E. C., and Hong, J. H., “Major aromatic VOC in the ambient air in the proximity of an urban landfill facility,” J. Hazard. Mater., 150, 754-764 (2008). crossref(new window)

Na, K., Kim, Y. P., and Moon, K. C., “Diurnal characteristics of volatile organic compounds in the Seoul atmosphere,” Atmos. Environ., 37, 733-742 (2003). crossref(new window)

Derwent, R. G., Middleton, D. R., Field, R. A., Goldstone, M. E., Lester, J. N., and Perry, R., “Analysis and interpretation of air quality data from an urban roadside location in central London over the period from July 19911 to July 1992,” Atmos. Environ., 29, 923-946 (1995). crossref(new window)

Rappenglück, B. and Fabian, P., “Nonmethane hydrocarbons (NMHC) in the Greater Munich Area/Germany,” Atmos. Environ., 33, 3843-3857 (1999). crossref(new window)

Baek, S. O., Kim, S. R., and Kim, B. K., “Variation of and affecting factors on the atmospheric concentrations of volatile organic compounds in an urban area,” J. Korean Soc. Environ. Eng., 24, 1391-1404 (2002).

Brocco, D., Fratarcangeli, R., Lepore, L., petricca, M., and Ventrone, I., “Determination of aromatic hydrocarbons in urban area of Rome,” Atmos. Environ., 31, 557-566 (1997). crossref(new window)