Table 4.
Pollutant | Time delay (days) | IQRb | While controlling for NO2 | While controlling for PM10 |
---|---|---|---|---|
NO2 | 3 | 40 | — | 1.07 (1.01–1.13)* |
4 | 40 | — | 1.07 (1.01–1.14)* | |
5 | 40 | — | 1.08 (1.01–1.15)* | |
PNC50–100 | 2 | 3,600 | 1.06 (0.99–1.14) | 1.07 (1.00–1.15)* |
3 | 3,600 | 1.06 (0.98–1.16) | 1.08 (1.00–1.17)* | |
PNC100–300 | 2 | 4,400 | 1.08 (1.00–1.17) | 1.10 (1.02–1.19)* |
3 | 4,400 | 1.06 (0.97–1.16) | 1.11 (1.02–1.21)* | |
PSC50–100 | 2 | 60 | 1.06 (0.99–1.14) | 1.07 (1.01–1.15)* |
3 | 60 | 1.07 (0.98–1.16) | 1.09 (1.01–1.17)* | |
PSC100–300 | 2 | 440 | 1.07 (0.99–1.16) | 1.10 (1.02–1.19)* |
3 | 440 | 1.05 (0.95–1.15) | 1.10 (1.01–1.20)* |
For a complete table, see Supplemental Material, Table 3 (doi:10.1289/ehp.1002203). Estimates were calculated using cumulative effects models representing time-delayed effects with moving averages up to 6 days (mean of the same day and 5 previous days) and including both pollutants with the same lag, for example, same-day total particle number concentration and same-day NO2 concentration.
Units for IQR: NO2 (μg/m3); PNCx (1/cm3); PSCx (μm2/cm3).
p < 0.05 (p-values for the null hypothesis that the corresponding parameter is zero).