PURPOSE: This study was performed to investigate polycyclic aromatic hydrocarbons (PAHs) exposure in the area around a cement factory with kilns using waste, including refuse plastic fuel. METHODS: Atmospheric total suspended particulates (TSPs) for each of an exposed area and a non-exposed area were collected. Similarly, urine samples were collected from 330 subjects in the exposed area and 126 subjects in the non-exposed area. Gas chromatography with mass spectrometry was used to analyze PAHs in the collected TSP samples and the PAH metabolites, urinary 2-naphthol (2-NAP) and 1-hydroxypyrene (1-OHP), of the residents. The concentrations of urinary 2-NAP and 1-OHP were adjusted by creatinine concentrations. RESULTS: The atmospheric concentrations of PAHs, including naphthalene and pyrene, were higher in the exposed area than those in the non-exposed area. The geometric means (GMs) of the urinary 2-NAP concentrations in the exposed and non-exposed groups without work experience were 4.06 and 1.55 μg/g creatinine, respectively. The GMs of the urinary 1-OHP concentrations were 0.26 and 0.14 μg/g creatinine, respectively. The results showed that the concentrations of PAH metabolites were significantly higher in the exposed group than those in the non-exposed group (p < 0.001). Multiple linear regression analysis with the log-transformed urinary 2-NAP and 1-OHP concentrations and other variables indicated a strong correlation of residence in the exposed area and smoking with an increase in the urinary 2-NAP and 1-OHP concentrations. CONCLUSIONS: In addition to the known risk factors, this study indicated that living near a cement factory with kilns is also a risk factor for PAH exposure.
PURPOSE: This study was performed to investigate polycyclic aromatic hydrocarbons (PAHs) exposure in the area around a cement factory with kilns using waste, including refuse plastic fuel. METHODS: Atmospheric total suspended particulates (TSPs) for each of an exposed area and a non-exposed area were collected. Similarly, urine samples were collected from 330 subjects in the exposed area and 126 subjects in the non-exposed area. Gas chromatography with mass spectrometry was used to analyze PAHs in the collected TSP samples and the PAH metabolites, urinary 2-naphthol (2-NAP) and 1-hydroxypyrene (1-OHP), of the residents. The concentrations of urinary 2-NAP and 1-OHP were adjusted by creatinine concentrations. RESULTS: The atmospheric concentrations of PAHs, including naphthalene and pyrene, were higher in the exposed area than those in the non-exposed area. The geometric means (GMs) of the urinary 2-NAP concentrations in the exposed and non-exposed groups without work experience were 4.06 and 1.55 μg/g creatinine, respectively. The GMs of the urinary 1-OHP concentrations were 0.26 and 0.14 μg/g creatinine, respectively. The results showed that the concentrations of PAH metabolites were significantly higher in the exposed group than those in the non-exposed group (p < 0.001). Multiple linear regression analysis with the log-transformed urinary 2-NAP and 1-OHP concentrations and other variables indicated a strong correlation of residence in the exposed area and smoking with an increase in the urinary 2-NAP and 1-OHP concentrations. CONCLUSIONS: In addition to the known risk factors, this study indicated that living near a cement factory with kilns is also a risk factor for PAH exposure.
Authors: Rebeca I Martínez-Salinas; M Elena Leal; Lilia E Batres-Esquivel; Gabriela Domínguez-Cortinas; Jacqueline Calderón; Fernando Díaz-Barriga; Iván N Pérez-Maldonado Journal: Int Arch Occup Environ Health Date: 2009-11-03 Impact factor: 3.015
Authors: Noel J Aquilina; Juana Mari Delgado-Saborit; Claire Meddings; Stephen Baker; Roy M Harrison; Peyton Jacob; Margaret Wilson; Lisa Yu; Minjiang Duan; Neal L Benowitz Journal: Environ Int Date: 2010-06-29 Impact factor: 9.621