| Ambient air pollution and cardiovascular emergency department visits 42
|
4,407,535 |
United States |
NA |
CO
NO2
PM2.5
Organic carbon
Elemental carbon
Oxygenated hydrocarbons
|
Visits for congestive heart failure linked with organic carbon (RR: 1.048, 95%CI: 1.007-1.091), elemental carbon (RR: 1.035, 95%CI: 1.003-1.068) and PM2.5 (RR: 1.055, 95%CI: 1.006-1.105)
Visits for cardiovascular disease linked with organic carbon (RR: 1.026, 95%CI: 1.006-1.046), elemental carbon (RR: 1.020, 95%CI: 1.005-1.036), PM2.5 (RR: 1.033, 95%CI: 1.010-1.056), CO (RR: 1.017, CI: 1.008-1.027), NO2 (RR: 1.025, 95%CI: 1.012-1.039), and oxygenated hydrocarbons (RR: 1.029, 95%CI: 1.000-1.059)
Visits for peripheral vascular and cerebrovascular disease linked with CO (RR: 1.031, 95%CI: 1.010-1.052), PM2.5 (RR: 1.050, 95%CI: 1.008-1.093) and NO2 (RR: 1.041, 95%CI: 1.013-1.069)
Visits for ischemic heart disease linked with oxygenated hydrocarbons (RR: 1.066, 95%CI: 1.012-1.122) and NO2 (RR: 1.029, 95%CI: 1.005-1.053)
|
| Traffic-related air pollution and asthma hospital readmission in children: a longitudinal cohort study 45
|
758 |
United States |
1-16 years |
|
|
| Traffic-related air pollution and obesity formation in children: A longitudinal, multilevel analysis 46
|
4257 |
United States |
5-7 years |
|
|
| Association of childhood obesity with maternal exposure to ambient air polycyclic aromatic hydrocarbons during pregnancy 47
|
422 followed up to age 5
341 followed up to age 7 |
United States |
Birth to 7 years |
|
Highest levels of prenatal polycyclic aromatic hydrocarbon exposure correlated with higher BMI z score at both age 5 years (β = 0.39, 95%CI: 0.08-0.70) and age 7 years (β = 0.30, 95%CI: 0.01-0.59)
Higher prenatal polycyclic aromatic hydrocarbon exposure correlated with elevated body fat percentage (β = 1.93, 95%CI: 0.33-3.54) and fat mass (β = 1.11, 95%CI: 0.10-2.11) but not with differences in lean mass at 7 years of age
|
| Effects of air pollution exposure on glucose metabolism in Los Angeles minority children 48
|
429 |
United States |
8-18 years |
|
Non-freeway NOx correlated with elevated insulin and fasting glucose (p < 0.001), decreased insulin sensitivity (p = 0.02), and increased insulin secretion (p = 0.002)
Total NOx correlated with elevated insulin and fasting glucose (p = 0.03) and increased insulin secretion (p = 0.047)
|
| Longitudinal associations between ambient air pollution with insulin sensitivity, beta-cell function, and adiposity in Los Angeles Latino children 49
|
314 |
United States |
8-15 years |
|
Elevated long-term exposure to ambient air pollution (NO2 and PM2.5) associated with a faster decrease in insulin sensitivity (p = 0.02) during the study period and reduced insulin sensitivity at 18 years of age (p = 0.04 for NO2, p = 0.01 for PM2.5)
Increased long-term mean ambient air pollution exposure during the study period correlated with higher fasting and 2-hour insulin levels (p < 0.05)
Elevated NO2 and PM2.5 exposures correlated with greater increases in BMI and central adiposity in pre-existing overweight and obese children at start of study (p < 0.05)
|
| Long-term exposure to traffic-related air pollution and insulin resistance in children: results from the GINIplus and LISAplus birth cohorts 50
|
5,991 from the GINIplus Study
3,097 from the LISAplus Study |
Germany |
Birth to 10 years |
|
|
| Long-term exposure to fine particulate matter and incidence of type 2 diabetes mellitus in a cohort study: effects of total and traffic-specific air pollution 51
|
4,814 |
Germany |
45-75 years |
|
Exposure to total PM10 potentially linked with higher frequency of type 2 diabetes incidence (RR: 1.20, CI: 1.01,1.31)
Increase in 1 μg/m3 of PM originating from traffic sources (RR: 1.36, CI: 0.98,1.89 for PM10, RR: 1.36, CI: 0.97,1.89 for PM2.5) had higher toxicity than the same amount of total PM (RR: 1.05, CI: 1.00,1.10 for PM10, RR: 1.03, CI: 0.95,1.12 for PM2.5)
|