Contribution of indoor and outdoor environments to PM2.5 personal exposure of children—VESTA study
Introduction
Sources of atmospheric particles are classified as outdoor environmental sources, e.g. traffic exhausts, industrial combustion processes or erosion, and indoor sources, such as tobacco smoke, indoor combustion processes (e.g. for heating or cooking), pets or human activity at home (Marge et al., 1999). The poor correlations often observed between personal exposures measured on a short time scale, and ambient air concentrations measured during the same period (Lioy et al., 1990, Monn et al., 1997, Boudet et al., 2000), suggest that a host of factors other than ambient air may contribute to personal exposures. Since people spend approximately 80% of their time in indoor environments, in western life-style areas, indoor concentrations might represent an important determinant of personal exposure. The influence of outdoor sources also depends upon the characteristics of indoor ventilation and upon the structure of the buildings, both being important determinants of the air exchange rate (Rojas-Bracho et al., 2000). The penetration factor from outdoor to indoor environment for fines particles has been estimated between 0.7 and 1 (Oglesby et al., 2000). While there are many papers describing the contribution of different indoor and outdoor particles sources on personal exposure of adults (Ozkaynak et al., 1996, Janssen et al., 1998, Ebelt et al., 2000), personal exposure studies on children are scarce (Mosqueron et al., 2001).
The aim of this study, which is part of a research program on the role of air pollution on the occurrence of childhood asthma (the VESTA study), is to assess the main factors that influence personal exposure to fines particles (PM2.5) of children in French urban environments.
Section snippets
Study population and PM2.5 personal exposure measurements
In the VESTA study, 434 children, 4–14 years of age, were included in five French cities (Grenoble, Paris, Toulouse, Clermont-Ferrand and Nice), between March 1998 and December 2000. The design of this study is detailed elsewhere (Zmirou et al., in press). This paper deals with a fraction of this study population, who could participate to the PM2.5 personal exposure measurements. Briefly, children between 8 and 14, who were all volunteers (n=68), carried during 48 h an active sampler (SKC pump,
Results
Fig. 1 and Table 1 summarises the characteristics of the study population, by city. Average values of 48-h PM2.5 personal exposures (P=0.008), of background PM10 ambient air concentrations (P=0.05), of the index of traffic exposure (P<10−3), as well as of the number of persons/room (P<10−3) differ according to the city. By contrast, no difference was observed according to the city for the number of cigarettes smoked by the mother during the 48 h of measurements (P=0.48), and for the percentage
Discussion
In this study conducted in three French metropolitan areas, 36% of the variance of children PM2.5 personal exposure is explained, on the one hand, by indoor factors such as maternal tobacco smoke (36.1% of the total between-subjects variability) and presence of rodents at home (20.5%), and on the other hand by outdoor factors such as background PM10 ambient concentrations (23.6%) and, to a lesser degree, the proximity to traffic exhausts (12.2%).
These results are in agreement with other
Conclusion
This study evaluates the contribution of indoor and outdoor factors on exposure of children to air particles, and confirms that short-term personal exposures are not closely related to ambient air concentrations, as already demonstrated for adults. It does not result that ambient air surveillance data should not be used to assess population exposures. Merely, it shows that, while these surveillance data are easier to get in routine, characteristics of personal and population activities, and
Acknowledgements
This program was supported by the French Research Program on air pollution (Primequal-Predit). Stephanie Gauvin received a doctoral grant by ADEME (French Environment and Energy Agency) and Union Française des Industries Pétrolières (UFIP). The authors thank the heads of the air quality monitoring networks of the three cities (ASCOPARG: MB Personnaz, ORAMIP: M. Della Massa, AIRPARIF: Ph Lameloise) for their collaboration, as well as Météo France.
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- 1
Present address: CSTB, Centre Scientifique et Technique du Bâtiment, Paris.
- 2
Present address: Nancy University Medical School.