Table 2.
Women | Men | ||||||
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Outcome | OR | 95% CI | OR | 95% CI | |||
M1 model | |||||||
Aircraft noise annoyance* | LAeq24h† | 2.90 | 2.11 | 3.97 | 3.10 | 2.12 | 4.52 |
Lden† | 2.69 | 2.01 | 3.61 | 2.78 | 1.97 | 3.92 | |
M2 model | |||||||
LAeq24h† | 0.93 | 0.65 | 1.34 | 1.45 | 0.96 | 2.21 | |
SRHS‡ | Aircraft noise annoyance | 1.35 | 0.92 | 1.98 | 1.56 | 0.97 | 2.52 |
Lden† | 0.95 | 0.69 | 1.30 | 1.36 | 0.94 | 1.98 | |
Aircraft noise annoyance | 1.35 | 0.92 | 1.98 | 1.57 | 0.98 | 2.44 | |
M3 model | |||||||
LAeq24h† | 0.99 | 0.70 | 1.40 | 1.58 | 1.05 | 2.37 | |
SRHS‡ | Lden† | 1.00 | 0.73 | 1.37 | 1.47 | 1.02 | 2.11 |
M1 model was adjusted for age, number of people in the household, occupational activity, economic dependency on airport activities, use of the noise source, fear of a plane crash, homeownership, type of housing, residential satisfaction, source- and authority-related attitudes, and noise sensitivity. CI = confidence interval, OR = odds ratio, SRHS = self-reported health status. * Severe aircraft noise annoyance was modeled. †For a 10 dBA increase in aircraft noise levels. ‡ Impaired SRHS was modeled. Bold numbers indicate that OR is statistical significant at the 5% threshold.