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(Reference retrieved automatically from Google Scholar through information on FAPESP grant and its corresponding number as mentioned in the publication by the authors.)

Emission of polycyclic aromatic hydrocarbons from gasohol and ethanol vehicles

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Author(s):
de Abrantes, Rui [1] ; de Assuncao, Joao Vicente [2] ; Pesquero, Celia Regina [2] ; Bruns, Roy Edward [3] ; Nobrega, Raimundo Paiva [2]
Total Authors: 5
Affiliation:
[1] Cetesb, Vehicular Emiss Lab, Sao Paulo - Brazil
[2] Univ Sao Paulo, Sch Publ Hlth, BR-05508 Sao Paulo - Brazil
[3] Univ Estadual Campinas, Campinas, SP - Brazil
Total Affiliations: 3
Document type: Journal article
Source: Atmospheric Environment; v. 43, n. 3, p. 648-654, Jan. 2009.
Field of knowledge: Engineering - Sanitary Engineering
Web of Science Citations: 25
Abstract

The exhaust emission of the polycyclic aromatic hydrocarbons (PAHs) considered toxic to human health were investigated on two spark ignition light duty vehicles, one being gasohol (Gasohol, in Brazil, is the generic denomination for mixtures of pure gasoline plus 20–25% of anhydrous ethyl alcohol fuel (AEAF).)-fuelled and the other a flexible-fuel vehicle fuelled with hydrated ethanol. The influence of fuel type and quality, aged lubricant oil type and use of fuel additives on the formation of these compounds was tested using standardized tests identical to US FTP-75 cycle. PAH sampling and chemical analysis followed the basic recommendations of method TO-13 (United States. Environmental Protection Agency, 1999. Compendium Method TO-13A – Determination of polycyclic Aromatic hydrocarbons (PAH) in Ambient Air Using Gas Chromatography/Mass Spectrometry (CG/MS). Center for environmental research information, Cincinnati, p. 78), with the necessary modification for this particular application. Results showed that the total PAH emission factor varied from 41.9 μg km−1 to 612 μg km−1 in the gasohol vehicle, and from 11.7 μg km−1 to 27.4 μg km−1 in the ethanol-fuelled vehicle, a significant difference in favor of the ethanol vehicle. Generally, emission of light molecular weight PAHs was predominant, while high molecular weights PAHs were not detected. In terms of benzo(a)pyrene toxicity equivalence, emission factors varied from 0.00984 μg TEQ km−1 to 4.61 μg TEQ km−1 for the gasohol vehicle and from 0.0117 μg TEQ km−1 to 0.0218 μg TEQ km−1 in the ethanol vehicle. For the gasohol vehicle, results showed that the use of fuel additive causes a significant increase in the emission of naphthalene and phenanthrene at a confidence level of 90% or higher; the use of rubber solvent on gasohol showed a reduction in the emission of naphthalene and phenanthrene at the same confidence level; the use of synthetic oil instead of mineral oil also contributed significantly to a decrease in the emission of naphthalene and fluorene. In relation to the ethanol vehicle, the same factors were tested and showed no statistically significant influence on PAH emission. (AU)