Biological monitoring of environmental exposure to polycyclic aromatic hydrocarbons in subjects living in the vicinity of a creosote impregnation plant
M. Bouchard et al., Biological monitoring of environmental exposure to polycyclic aromatic hydrocarbons in subjects living in the vicinity of a creosote impregnation plant, INT A OCCUP, 74(7), 2001, pp. 505-513
Citations number
52
Categorie Soggetti
Envirnomentale Medicine & Public Health","Pharmacology & Toxicology
Journal title
INTERNATIONAL ARCHIVES OF OCCUPATIONAL AND ENVIRONMENTAL HEALTH
Objective: This study was undertaken to evaluate the environmental exposure
to polycyclic aromatic hydrocarbons (PAHs) in nonsmoking adult subjects li
ving in the vicinity of a creosote impregnation plant in Delson, Canada. Ur
inary metabolites of naphthalene, alpha- and beta -naphthol, and pyrene met
abolite 1-hydroxypyrene (1-OHP), were used as biomarkers of exposure. Metho
ds: Morning and evening urine samples were collected in mid-August from 30
exposed individuals living at a distance of 50-360 m downwind of the plant
and from a control group in the adjoining municipality residing at a distan
ce of 1.9-2.7 km upwind of the plant. Metabolites were measured by gas chro
matography/mass spectrometry. Results: Excretion values of alpha- and beta
-naphthol were significantly higher in the exposed group than in controls (
P < 0.04), after accounting for possible confounding variables by multivari
ate analyses. The respective geometric mean concentrations (5th and 95th pe
rcentiles) of alpha -naphthol for the exposed and nonexposed groups were 2.
04 (0.55-6.00) and 1.37 (0.39-7.02) mu mol/mol creatinine for evening sampl
es, and 2.49 (0.77-8.43) and 1.17 (0.37-6.88) mu mol/mol creatinine for mor
ning samples. Corresponding values for fl-naphthol were 1.78 (0.82-3.67) an
d 1.36 (0.63-5.07) mu mol/mol creatinine for evening samples, and 1.94 (1.0
3-4.96) and 1.08 (0.49-5.05) mu mol/mol creatinine for morning samples. On
the other hand, no significant difference in 1-OHP excretion was observed b
etween the exposed and the control group (P >0.5). The respective geometric
mean concentrations (5th and 95th percentiles) of 1-OHP for these groups w
ere 0.05 (0.01-0.17) and 0.06 (0.01-0.48) mu mol/mol creatinine for evening
samples, and 0.05 (0.02-0.12) and 0.05 (0.01-0.42) mu mol/mol creatinine f
or morning samples. Conclusions: The measurement of alpha- and beta -naphth
ol urinary concentrations appears to be an approach sufficiently sensitive
to reveal differences in low exposure levels of volatile PAHs due to creoso
te impregnation plant emissions. However, uptake of pyrene due to the plant
was too small to contribute significantly to 1-OHP excretion.