Table S2.
Indicator | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 |
---|---|---|---|---|---|---|---|---|---|---|
PM2.5 | 1.00 | .71** | .28** | .01 | –.04 | .01 | .04 | .09 | .13* | .09 |
BaP | 1.00 | .23** | .10 | .02 | –.02 | .01 | .12* | .13* | .05 | |
Lden | 1.00 | .38** | .00 | .03 | .18** | .24** | .21** | .21** | ||
Self-reported traffic intensity | 1.00 | .17** | .11* | .20** | .36** | .26** | .18** | |||
Lifetime residential exposure to loud noise | 1.00 | .15** | .23** | .09* | –.03 | .11* | ||||
Lifetime occupational exposure to loud noise | 1.00 | .06 | .12** | .10* | .10* | |||||
Noise annoyance | 1.00 | .05 | .07 | .29** | ||||||
Perceived air quality | 1.00 | .43** | .27** | |||||||
Perceived severity of air pollution | 1.00 | .50** | ||||||||
Air pollution annoyance | 1.00 |
Note. BaP = Benzo alpha pyrene, PM2.5 = Particulate matter pollutants of ≤2.5 μm in aerodynamic diameter, Lden = Day-evening-night equivalent sound level Model is based on the original dataset prior to replacement of missing values and dichotomizing variables. Spearman’s correlation coefficients are reported Correlation is *Significant at P < 0.05, **Significant at P < 0.01