Son et al., 2008 [54] |
Seoul, Korea |
Firstborn infants in Seoul, Korea, during 1999–2003 |
To examine the relationship between air pollution and post-neonatal mortality from all causes using both case-crossover and time-series analyses |
The risk of post-neonatal infant death from all causes was positively associated with all studied air pollutants except ozone |
Woodruff et al., 2008 [55] |
U.S. counties with>250,000 residents |
Infants born from 1999 to 2002 (n=about 3.5 million births, with 6,639 post-neonatal infant deaths) |
To evaluate the relationship between cause-specific post-neonatal infant mortality and chronic early-life exposure to particulate matter and gaseous air pollutants across the United States |
PM10 is a risk factor for respiratory-related post-neonatal mortality and ozone may be associated with sudden infant death syndrome |
Heinrich et al., 2007 [56] |
Review |
Studies on the impact of fine particle exposure on infant death, lung function, respiratory symptoms and reproductive outcomes |
To review the children's susceptibility to ambient fine particles and characteristics of infant and children which underlie their increased susceptibility to PM |
Exposure to PM is strongly and consistently associated with post-neonatal respiratory mortality and less consistently with sudden infant death syndrome |
Hajat et al., 2007 [57] |
10 major cities of England |
Daily time-series data of air pollution and all infant deaths between 1990 and 2000 |
To investigate the effects of outdoor pollution on infant mortality in the UK |
Few associations were observed between infant deaths and most pollutants studied except for SO2
|
Rinne et al., 2007 [58] |
Ecuador |
Eighty households in a rural community |
To explore the relationship between biomass fuel, infant mortality, and children's respiratory symptoms |
A significant trend for higher infant mortality among households that cooked with a greater proportion of biomass fuel was documented |
Yang et al., 2006 [59] |
Taipei, Taiwan |
Infant (27 days – 1 year) mortality data (1994–2000) |
To examine the relationship between air pollution exposure and post-neonatal infant mortality |
Air pollutants had a non-significant association with the risk of post-neonatal deaths. This weak association might be because of the subtropical climate of the area under study |
Woodruff et al., 2006 [60] |
California,USA (n=788 infant deaths) |
Monitoring data for PM ≤ 2.5 were linked to data of infants born to mothers who lived within 5 miles of a monitor (1999–2000) |
To examine the relationship between long-term exposure to fine PM air pollution and post-neonatal infant mortality |
Increase in PM2.5 increased post-neonatal mortality and sudden infant death syndrome |
Romieu et al., 2004 [61] |
Ciudad Juarez, Mexico |
Infant mortality and ambient PM10 levels on days before death (1997–2001) |
To study short-term PM10 exposure, relating to increased respiratory-related infant mortality, and estimated for poor living conditions |
Overall air pollutants did not affect infant mortality but low socioeconomic condition increased this risk. Increase in PM10 increased mortality |
Glinianaia et al., 2004 [62] |
Review |
Epidemiological studies (15 studies included) |
Systematic review of an association between particulate air pollution and infant mortality |
A strong association of particulate air pollution with some causes of infant death was found |
Lipfert et al., 2000 [63] |
USA |
U.S. birth and death records (1990) |
To explore associations between infant mortality and environmental factors, based on spatial relationships |
Significantnegative mortality associations were found for SO4(2) without any role for outdoor PM2.5 |
Loomis et al., 1999 [64] |
Mexico City, Mexico |
Infant mortality data (1993-1995) |
To investigate the association of air pollution and infant mortality by a time-series study |
Excess infant mortality was associated with the level of fine particles followed by the levels of nitrogen dioxide and ozone 3 to 5 days before death |
Bobak et al., 1992 [65] |
Czech Republic |
Infant mortality and air pollution data in 46 of the 85 districts (1986–1988) |
To assess the ecological associations of air pollution and infant mortality |
The strongest effects were seen for the level of total suspended particulates (TSP-10) followed by SO2 level |
Duchiade et al., 1992 [66] |
Rio de Janeiro, Brazil |
Civil Register mortality data (1976–1986) |
To study the associations between socioeconomic, climatic, and air pollution variables and the levels of mortality |
The mortality rates appeared to be associated with the variations of the log of average pollution |