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. 2014 Jan;122(1):107-13.
doi: 10.1289/ehp.1306755. Epub 2013 Oct 22.

Air pollution and respiratory infections during early childhood: an analysis of 10 European birth cohorts within the ESCAPE Project

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Air pollution and respiratory infections during early childhood: an analysis of 10 European birth cohorts within the ESCAPE Project

Elaina A MacIntyre et al. Environ Health Perspect. 2014 Jan.

Erratum in

  • Environ Health Perspect. 2014 Jan;122(1):112

Abstract

Background: Few studies have investigated traffic-related air pollution as a risk factor for respiratory infections during early childhood.

Objectives: We aimed to investigate the association between air pollution and pneumonia, croup, and otitis media in 10 European birth cohorts--BAMSE (Sweden), GASPII (Italy), GINIplus and LISAplus (Germany), MAAS (United Kingdom), PIAMA (the Netherlands), and four INMA cohorts (Spain)--and to derive combined effect estimates using meta-analysis.

Methods: Parent report of physician-diagnosed pneumonia, otitis media, and croup during early childhood were assessed in relation to annual average pollutant levels [nitrogen dioxide (NO2), nitrogen oxide (NOx), particulate matter≤2.5 μm (PM2.5), PM2.5 absorbance, PM10, PM2.5-10 (coarse PM)], which were estimated using land use regression models and assigned to children based on their residential address at birth. Identical protocols were used to develop regression models for each study area as part of the ESCAPE project. Logistic regression was used to calculate adjusted effect estimates for each study, and random-effects meta-analysis was used to calculate combined estimates.

Results: For pneumonia, combined adjusted odds ratios (ORs) were elevated and statistically significant for all pollutants except PM2.5 (e.g., OR=1.30; 95% CI: 1.02, 1.65 per 10-μg/m3 increase in NO2 and OR=1.76; 95% CI: 1.00, 3.09 per 10-μg/m3 PM10). For otitis media and croup, results were generally null across all analyses except for NO2 and otitis media (OR=1.09; 95% CI: 1.02, 1.16 per 10-μg/m3).

Conclusion: Our meta-analysis of 10 European birth cohorts within the ESCAPE project found consistent evidence for an association between air pollution and pneumonia in early childhood, and some evidence for an association with otitis media.

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Conflict of interest statement

The authors declare they have no actual or potential competing financial interests.

Figures

Figure 1
Figure 1
Forest plots of individual cohort and combined effect estimates (ORs) by outcome for (A) NO2, (B) NOx, (C) PM2.5, (D) PM2.5 absorbance, (E) PM10, (F) coarse PM, (G) traffic intensity on nearest street, and (H) traffic load on all major roads. Weight indicates relative weight (%) assigned using random-effects meta-analysis. The lifetime cumulative incidence of respiratory infection (pneumonia, otitis media, croup) was assessed at 12 months (INMA Valencia), 14 months (INMA Gipuzkoa, INMA Sabadell), 15 months (GASPII), 18 months (INMA Asturias), 24 months (BAMSE, GINI/LISA North, GINI/LISA South, PIAMA), and 36 months (MAAS) of age. Individual cohort models were adjusted for municipality (BAMSE), sex, older siblings, breastfeeding at 6 months, atopy of either parent, any child-care reported during follow-up, maternal smoking during pregnancy, any environmental tobacco smoke in the child’s home reported during follow-up, visible mold or dampness in the home, use of gas stove, birth season, parental socioeconomic status (low, medium, high), and intervention (GINIplus, MAAS, PIAMA). Associations are presented for the following increments in exposure: 10 μg/m3 for NO2, 20 μg/m3 for NOx, 5 μg/m3 for PM2.5, 1 unit for PM2.5 absorbance, 10 μg/m3 for PM10, 5 μg/m3 for coarse PM, 5,000 vehicles/day for traffic intensity on the nearest street; and 4,000 vehicle-km/day for traffic load on major roads within a 100-m buffer.

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References

    1. Aguilera I, Pedersen M, Garcia-Esteban R, Ballester F, Basterrechea M, Esplugues A, et al. 2013Early-life exposure to outdoor air pollution and respiratory health, ear infections, and eczema in infants from the INMA study. Environ Health Perspect 121387–392.; 10.1289/ehp.1205281 - DOI - PMC - PubMed
    1. Bateson TF, Schwartz J. Children’s response to air pollutants. J Toxicol Environ Health A. 2008;71(3):238–243. - PubMed
    1. Beelen R, Hoek G, Vienneau D, Eeftens M, Dimakopoulou M, Pedeli X, et al. Development of NO2 and NOx land use regression models for estimating air pollution exposure in 36 study areas in Europe—the ESCAPE project. Atmos Environ. 2013;72:10–23.
    1. Black RE, Cousens S, Johnson HL, Lawn JE, Rudan I, Bassani DG, et al. Global, regional, and national causes of child mortality in 2008: a systematic analysis. Lancet. 2010;375:1969–1987. - PubMed
    1. Brauer M, Gehring U, Brunekreef B, de Jongste J, Gerritsen J, Rovers M, et al. 2006Traffic-related air pollution and otitis media. Environ Health Perspect 1141414–1418.; 10.1289/ehp.9089 - DOI - PMC - PubMed

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