Table 2. Trend in adjusted lung cancer rates in 37 municipalities of Rio Grande do Sul by radon exposure.
| Adjusted lung cancer rates | Coef.a | 95%CIb | p-valuec | Trend |
|---|---|---|---|---|
| Incidence rate (2013–2021) | ||||
| Municipalities with low exposure probabilityd | 0.27 | −0.13; 0.68 | 0.153 | Stationary |
| Municipalities with increased probability to exposured | 1.01 | 0.22; 1.81 | 0.020 | Growing |
| Hospitalisation rate (2000–2021) | ||||
| Municipalities with low exposure probabilityd | 0.46 | 0.08;0.85 | 0.021 | Growing |
| Municipalities with increased probability to exposured | 1.15 | 0.70; 1.60 | <0.001 | Growing |
| Total mortality rate (2000–2021) | ||||
| Municipalities with low exposure probabilityd | −0.16 | −0.33; 0.01 | 0.058 | Stationary |
| Municipalities with increased probability to exposured | 0.02 | −0.33; 0.37 | 0.899 | Stationary |
Caption:
Prais–Winsten regression coefficient indicating the average annual change in the rate
95% Confidence Interval (CI) for the regression coefficient
Statistical significance of the trend, based on the Prais–Winsten regression
Municipalities grouped based on estimated radon exposure probability derived from airborne gamma spectrometry (eU concentrations):
– Low exposure probability: lower eU levels
– Increased exposure probability: higher eU levels, indicating greater radon susceptibility