2003
DOI: 10.1007/s00420-003-0439-4
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Exposure to carcinogenic polycyclic aromatic compounds and health risk assessment for diesel-exhaust exposed workers

Abstract: The 15 NTP PACs represent a small but non-negligible part of lung-cancer risk with regard to diesel exposure. From this point of view, the dibenzopyrene family are important compounds to be considered.

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Cited by 70 publications
(55 citation statements)
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“…The theoretical lung-cancer risk due to inhalation of p-PAHs and BC was then calculated by multiplying the B(a)Peq and BC concentrations by the corresponding unit risk factors, here defined as the risk corresponding to a lifetime (70 years per 24-h per day) exposure to 1 µg/m 3 of B(a)Peq or BC. The lifetime unit risk factor estimates considered in this work were obtained from both epidemiological studies and research conducted on rats (Sauvain et al, 2003), and compared reasonably well with those reported by the World The results of these rather simplified risk calculations (Table 3) highlight two important points. First, the lungcancer risk at the Wilmington site is highest during rush hour traffic (at 08:00; Risk[BC]=3.82×10 −5 for the rodentbased estimate to 1.77×10 −3 for the epidemiologic estimate; Risk[p-PAHs]=2.63×10 −7 for the rodent-based estimate to 4.94×10 −6 for the epidemiologic estimate) and lowest in the afternoon (at 17:00, Risk[BC]=5.94×10 −6 to 2.76×10 −4 ; Risk[p-PAHs]=8.59×10 −8 to 1.61×10 −6 ).…”
Section: Lung-cancer Risk In the Wilmington Areasupporting
confidence: 68%
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“…The theoretical lung-cancer risk due to inhalation of p-PAHs and BC was then calculated by multiplying the B(a)Peq and BC concentrations by the corresponding unit risk factors, here defined as the risk corresponding to a lifetime (70 years per 24-h per day) exposure to 1 µg/m 3 of B(a)Peq or BC. The lifetime unit risk factor estimates considered in this work were obtained from both epidemiological studies and research conducted on rats (Sauvain et al, 2003), and compared reasonably well with those reported by the World The results of these rather simplified risk calculations (Table 3) highlight two important points. First, the lungcancer risk at the Wilmington site is highest during rush hour traffic (at 08:00; Risk[BC]=3.82×10 −5 for the rodentbased estimate to 1.77×10 −3 for the epidemiologic estimate; Risk[p-PAHs]=2.63×10 −7 for the rodent-based estimate to 4.94×10 −6 for the epidemiologic estimate) and lowest in the afternoon (at 17:00, Risk[BC]=5.94×10 −6 to 2.76×10 −4 ; Risk[p-PAHs]=8.59×10 −8 to 1.61×10 −6 ).…”
Section: Lung-cancer Risk In the Wilmington Areasupporting
confidence: 68%
“…Estimating the potential health risk from these species and comparing the results to those obtained in other metropolitan areas is instructive, despite the large uncertainties involved in these calculations. Following the procedure adopted by Sauvain et al (2003) we determined the lungcancer risk associated with exposure to p-PAHs and BC from diesel combustion particles (DCPs). The most common approach for estimating health-risks posed by multi-component p-PAH exposure is based on the individual compound's po- Slopes and intercepts of all regression equations, and molecular formulas and structures of each individual species are also reported tency equivalence factor (PEF) relative to Benzo (a) pyrene (B(a)p; considered as a toxicological prototype for all other p-PAHs).…”
Section: Lung-cancer Risk In the Wilmington Areamentioning
confidence: 99%
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