Table 3.
Association between postnatal exposure to air pollution and childhood obesity in human epidemiologic studies
Study | Country | Study design | Study population |
Obesity parameter | Air pollutant | Direction of relationship with obesity (+/-/0) | Findings | |||
---|---|---|---|---|---|---|---|---|---|---|
Sample size (n) | Age at exposure (yr) | Age at outcome (yr) | ||||||||
Traffic density/proximity | ||||||||||
Jerrett et al. [25] 2010 | USA | Cohort | 2,889 | 9–10 | 18 | BMI | Traffic density | (+) | Positive association with attained BMI over 8 study years | |
Jerrett et al. [26] 2014 | USA | Cohort | 4,550 | 5–7 | 10 | BMI | Traffic density | (+) | Positive association with attained BMI at the age of 10 | |
Amram et al. [27] 2019 | USA | Cross-sectional | 10,327 | 10–11 | 10–11 | BMI | Arterial road exposure | 0 | No association with overweight | |
NOx/elemental carbon | ||||||||||
McConnell et al. [28] 2015 | USA | Cohort | 3,318 | 10 | 18 | BMI | NOx | (+) | Synergism between tobacco smoke and NOx exposure on attained BMI at the age of 18 | |
Alderete et al. [29] 2017 | USA | Cohort | 314 | 8–15 | 18 | BMI | NO2 | (+) | Positive association with BMI and SAAT at the age of 18 | |
Body fat% | ||||||||||
SAAT | ||||||||||
IAAT | ||||||||||
Kim et al. [16] 2018 | USA | Cohort | 2,318 | 1 | 10 | BMI | NOx | (+) | Positive association with attained BMI at the age of 10 | |
Fioravanti et al. [32] 2018 | Italy | Cohort | 719 | 0, 4 | 4, 8 | BMI, WC, WHR | NO2 | 0 | No association with childhood obesity | |
Bloemsma et al. [30] 2019 | Nether-lands | Cohort | 3,680 | 12–14 | 3–17 | BMI | NO2 | (+) | Positive association with overweight | |
de Bont et al. [31] 2019 | Spain | Cross-sectional | 2,660 | 7–10 | 7–10 | BMI | NO2 | (+) | Positive association with overweight/obese | |
PM | ||||||||||
Kim et al. [33] 2016 | Korea | Cohort | 1,129 | 0.5–1 | 1–5 | Weight-for-age | PM10 | (-) | Negative association with weight at the age of 12–60 mos | |
Mao et al. [18] 2017 | USA | Cohort | 1,446 | 0–2 | 2–9 | BMI | PM2.5 | (+) | Positive association with childhood overweight or obesity | |
Alderete et al. [29] 2017 | USA | Cohort | 314 | 8–15 | 18 | BMI | PM2.5 | (+) | Positive association with BMI and SAAT at the age of 18 | |
Body fat% | ||||||||||
SAAT | ||||||||||
Kim et al. [16] 2018 | USA | Cohort | 2,318 | 1 | 10 | IAAT | PM2.5 | 0 | No association with attained BMI at the age of 10 | |
Fioravanti et al. [32] 2018 | Italy | Cohort | 719 | 0, 4 | 4, 8 | BMI, WC, WHR | PM2.5 PM10 | 0 | No association with childhood obesity | |
Bloemsma et al. [30] 2019 | Nether-lands | Cohort | 3,680 | 12–14 | 3–17 | BMI | PM2.5 PM10 | 0 | No association with overweight | |
de Bont et al. [31] 2019 | Spain | Cross-sectional | 2,660 | 7–10 | 7–10 | BMI | PM2.5 | (+) | Positive association with overweight/obese | |
Smoking | ||||||||||
McConnell et al. [28] 2015 | USA | Cohort | 3,318 | 10 | 18 | BMI | Smoking | (+) | Synergism between tobacco smoke and NOx exposure on attained BMI at the age of 18 | |
PAH | ||||||||||
Scinicariello et al. [35] 2014 | USA | Cross-sectional | 3,189 | 6–19 | 6–19 | BMI, WC | PAHs | (+) | Positive association with obesity parameters in children |
The direction of relationship with obesity: (+), factor related with greater childhood obesity; (-), factor related with decreased childhood obesity; (0), no relationship with childhood obesity.
BMI, body mass index; IAAT, cross-sectional area of intra-abdominal adipose tissue; NO2, nitrogen dioxide; NOx, nitrogen oxides; PAHs, polycyclic aromatic hydrocarbons PM2.5, particulate matter <2.5 microns in diameter; PM10, particulate matter <10 microns in diameter; SAAT, cross-sectional area of subcutaneous abdominal adipose tissue; WC, waist circumference; WHR, waist-to-hip ratio.