ArticlesRenal function, cytogenetic measurements, and sexual development in adolescents in relation to environmental pollutants: a feasibility study of biomarkers
Introduction
People worldwide are exposed to many environmental pollutants, which are usually monitored by measurements in air, food, water, soil, or dust. Extrapolation from these data to assess the total internal exposure of human beings or to the possible health effects is uncertain.1 People are exposed via different routes. Variability between individuals in absorption, distribution, metabolism, and excretion of xenobiotics is huge. Several chemicals can act on the same target organs. Diseases caused by chronic exposure to low concentrations of pollutants might become clinically evident only after a long period of time. Concentrations of pollutants or their metabolites in blood, urine, or tissues show current or lifetime exposure via all routes. Biomarkers of exposure are more directly associated with biomarkers of effects than are measurements of pollutants in external media, and provide better estimates of health risk before onset of disease.2
Exposure to chlorinated pesticides has been compared between women aged 50–65 years in rural areas and in suburbs: serum-sample concentrations of pentachlorophenol, lindane, and active p,p′-DDT (dichlorodiphenyl-trichloroethane) and its inactive metabolite p,p′-DDE were significantly higher in rural areas than in suburbs (100 women per area), but the opposite was noted for hexachlorobenzene (Department of Welfare, Health and Equal Opportunities, Ministry of the Flemish Community, Brussels, 2000).
We have therefore investigated whether biomarkers can reveal exposure and early health effects in relation to four main classes of environmental pollutants: heavy metals, polychlorinated biphenyls (PCBs), volatile organic compounds (VOCs), and polycyclic aromatic hydrocarbons (PAHs). We chose 17-year-old adolescents as our target population, because in a society with a life expectancy of more than 74 years, biomarkers in young people show recent exposure, even for cumulative toxins such as heavy metals,3 polychlorinated biphenyls,4, 5 or dioxins.4 Moreover, in Belgium, school attendance is compulsory until age 18 years and school doctors routinely examine adolescents. Hence, our study benefited from professional expertise and infrastructure.
Section snippets
Geographical areas
The suburbs Hoboken and Wilrijk are 11–13 km south-east of the chemical industry in the seaport of Antwerp.6 We selected them for our study area because they included a large non-ferrous smelter,7, 8 two waste incinerators,9 a crematory,9 a printing works, and other various industries. Both suburbs are crossed by motorways that carry over 80 000 vehicles per day.6 In 1998, the mean air concentrations of benzene, toluene, and ethylbenzene were 3·2, 13·0, and 3·6 μg/m3, respectively (Vlaamse
Participants
524 adolescents, born in 1980–83 were eligible. 169 children were excluded: seven because they had not lived all their lives in the study areas, and 162 because the sex quota by area had already been filled. Of 355 invited youngsters, 207 (58%) volunteered to take part. We did not examine seven adolescents: three had recently moved out of the study area, two were unavailable because of illness, and two were away travelling.
The 200 adolescents included 120 girls (60%), none of whom were
Discussion
In adolescents, biomarkers were sensitive enough to detect significant geographical gradients in common environmental pollutants, in their metabolites, and in their biological effects. Across individual teenagers, dose-effect and dose-response curves were established, which were prespecified in our protocol on the basis of experimental data,21, 22, 31 hypotheses,31, 32, 33 or observations mostly made at high levels of occupational1, 18, 20, 29, 34 or accidental35 exposure to pollutants. We also
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