Table 5.
Measured NO2 pollution | No.a | HR (95% CI)b | σ2c | Likelihood ratio test p-valued |
---|---|---|---|---|
Fall–winter | 209 | 1.29 (1.11–1.49) | 0.00016 | |
Within-community deviation | 209 | 1.32 (0.91–1.92) | 0.00016 | > 0.1 |
Community mean | 1.28 (1.09–1.51) | |||
Summer | 204 | 1.27 (1.03–1.57) | 0.00020 | |
Within-community deviation | 204 | 0.99 (0.57–1.72) | 0.00019 | > 0.1 |
Community mean | 1.32 (1.05–1.66) | |||
Annual | 196 | 1.29 (1.07–1.56) | 0.00018 | |
Within-community deviation | 196 | 1.31 (0.76–2.26) | 0.00019 | > 0.1 |
Community mean | 1.28 (1.05–1.57) |
Number of subjects varied because of invalid measurements during fall–winter and summer months.
We adjusted models for Hispanic ethnicity, enrollment group, medical insurance coverage, and community annual mean relative humidity, with baseline strata for age and sex. Measured NO2 pollution estimates are over a 6.2-ppb exposure contrast, which is the average within-community interquartile range for average annual measured NO2.
Values of σ2 are the random-effects variance estimates, which represent the residual variation in asthma incidence attributable to the community cluster after we included all other fixed predictors in the model.
Likelihood ratio tests for the null hypothesis that there is no difference between the random-effects models and between/within-community models were not rejected.