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. 2004 Jan;61(1):8–15.

Risk of congenital anomalies in the vicinity of municipal solid waste incinerators

S Cordier 1, C Chevrier 1, E Robert-Gnansia 1, C Lorente 1, P Brula 1, M Hours 1
PMCID: PMC1757799  PMID: 14691267

Abstract

Background: Although municipal solid waste incineration (MSWI) has contributed to increase the overall environmental load of particulate matter containing dioxins and metals, evidence of health consequences to populations is sparse.

Aims: To assess at a regional level (in southeast France) the impact of these emissions on birth defect rates.

Methods: Communities with fewer than 50 000 inhabitants surrounding the 70 incinerators that operated at least one year from 1988 to 1997 were studied. Each exposed community (n = 194) was assigned an exposure index estimated from a Gaussian plume model. Poisson models and a reference population of the 2678 unexposed communities in the region were used to calculate relative risks for congenital malformations, adjusted for year of birth, maternal age, department of birth, population density, average family income, and when available, local road traffic.

Results: The rate of congenital anomalies was not significantly higher in exposed compared with unexposed communities. Some subgroups of major anomalies, specifically facial clefts and renal dysplasia, were more frequent in the exposed communities. Among exposed communities, a dose-response trend of risk with increasing exposure was observed for obstructive uropathies. Risks of cardiac anomalies, obstructive uropathies, and skin anomalies increased linearly with road traffic density.

Conclusions: Although both incinerator emissions and road traffic may plausibly explain some of the excess risks observed, several alternative explanations, including exposure misclassification, ascertainment bias, and residual confounding cannot be excluded. Some of the effects observed, if real, might be attributable to old-technology MSWIs and the persistent pollution they have generated.

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Selected References

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  1. Balducci F., Grandamas O., Zmirou D. POLAIR: logiciel et guide méthodologique pour l'investigation épidémiologique d'une pollution atmosphérique ponctuelle. Rev Epidemiol Sante Publique. 1995 Dec;43(6):594–603. [PubMed] [Google Scholar]
  2. Den Hond Elly, Roels Harry A., Hoppenbrouwers Karel, Nawrot Tim, Thijs Lutgarde, Vandermeulen Corinne, Winneke Gerhard, Vanderschueren Dirk, Staessen Jan A. Sexual maturation in relation to polychlorinated aromatic hydrocarbons: Sharpe and Skakkebaek's hypothesis revisited. Environ Health Perspect. 2002 Aug;110(8):771–776. doi: 10.1289/ehp.02110771. [DOI] [PMC free article] [PubMed] [Google Scholar]
  3. Harris J., Robert E., Källén B. Epidemiologic characteristics of kidney malformations. Eur J Epidemiol. 2000;16(11):985–992. doi: 10.1023/a:1011016706969. [DOI] [PubMed] [Google Scholar]
  4. Lloyd O. L., Lloyd M. M., Williams F. L., Lawson A. Twinning in human populations and in cattle exposed to air pollution from incinerators. Br J Ind Med. 1988 Aug;45(8):556–560. doi: 10.1136/oem.45.8.556. [DOI] [PMC free article] [PubMed] [Google Scholar]
  5. Pradat P., Francannet C., Harris J. A., Robert E. The epidemiology of cardiovascular defects, part I: a study based on data from three large registries of congenital malformations. Pediatr Cardiol. 2003 Mar 14;24(3):195–221. doi: 10.1007/s00246-002-9401-6. [DOI] [PubMed] [Google Scholar]
  6. Ritz Beate, Yu Fei, Fruin Scott, Chapa Guadalupe, Shaw Gary M., Harris John A. Ambient air pollution and risk of birth defects in Southern California. Am J Epidemiol. 2002 Jan 1;155(1):17–25. doi: 10.1093/aje/155.1.17. [DOI] [PubMed] [Google Scholar]
  7. Robert E., Francannet C., Robert J. M. Le registre de malfromations de la région Rhône-Alpes/Auvergne. Intéret et limites de la tératovigilance. Onze ammées d'experience (1976-1986). J Gynecol Obstet Biol Reprod (Paris) 1988;17(5):601–607. [PubMed] [Google Scholar]
  8. Rydhstroem H. No obvious spatial clustering of twin births in Sweden between 1973 and 1990. Environ Res. 1998 Jan;76(1):27–31. doi: 10.1006/enrs.1997.3785. [DOI] [PubMed] [Google Scholar]
  9. Seta N., Arfi C., Momas I. Exposition de la population générale aux dioxines, contaminants ubiquitaires. Rev Epidemiol Sante Publique. 2000 Jun;48(3):281–293. [PubMed] [Google Scholar]
  10. Vrijheid M., Dolk H., Stone D., Abramsky L., Alberman E., Scott J. E. Socioeconomic inequalities in risk of congenital anomaly. Arch Dis Child. 2000 May;82(5):349–352. doi: 10.1136/adc.82.5.349. [DOI] [PMC free article] [PubMed] [Google Scholar]
  11. Williams F. L. R., Ogston S. A. Identifying populations at risk from environmental contamination from point sources. Occup Environ Med. 2002 Jan;59(1):2–8. doi: 10.1136/oem.59.1.2. [DOI] [PMC free article] [PubMed] [Google Scholar]
  12. Williams F. L., Lawson A. B., Lloyd O. L. Low sex ratios of births in areas at risk from air pollution from incinerators, as shown by geographical analysis and 3-dimensional mapping. Int J Epidemiol. 1992 Apr;21(2):311–319. doi: 10.1093/ije/21.2.311. [DOI] [PubMed] [Google Scholar]

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