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. 2012 Jul 25;176(4):327–337. doi: 10.1093/aje/kws012

Table 4.

Multilevel Model Parameter Estimates for Aircraft and Road Traffic Noise at School and Nitrogen Dioxide Levels at School on Children's Health in the United Kingdom Air Pollution Subsample of the RANCH Project, 20012003 (n = 719)

Variable No. of Participants Air Pollution at School Adjusted for Sociodemographic Factorsa
Air Pollution, Aircraft Noise, and Road Traffic Noise at School Adjusted for Sociodemographic Factorsa
βb 95% CI P Value βb 95% CI P Value
Psychological distress 634
 Nitrogen dioxide 0.012 −0.042, 0.067 0.67 0.025 −0.033, 0.083 0.40
 Road traffic noise −0.037 −0.104, 0.029 0.27
 Aircraft noise −0.028 −0.079, 0.023 0.28
Self-rated health 655
 Nitrogen dioxide 0.013 −0.006, 0.033 0.18 0.013 −0.008, 0.033 0.22
 Road traffic noise −0.00020 −0.027, 0.027 0.99
 Aircraft noise 0.004 −0.018, 0.026 0.70
Systolic blood pressure 276
 Nitrogen dioxide 0.058 −0.092, 0.210 0.45 0.070 −0.120, 0.259 0.47
 Road traffic noise −0.102 −0.31, 0.11 0.35
 Aircraft noise 0.017 −0.139, 0.174 0.83
Diastolic blood pressure 276
 Nitrogen dioxide 0.033 −0.084, 0.151 0.58 0.088 −0.059, 0.236 0.24
 Road traffic noise 0.030 −0.136, 0.195 0.73
 Aircraft noise 0.012 −0.110, 0.134 0.85

Abbreviations: CI, confidence interval; RANCH, Road Traffic and Aircraft Noise Exposure and Children's Cognition and Health.

a All models adjusted for age, gender, employment status, crowding, home ownership, mother's educational level, long-standing illness, main language spoken at home, parental support for schoolwork, and classroom window glazing type except the blood pressure models, which were additionally adjusted for body mass index, cuff-size, room temperature, birth weight, parental high blood pressure, and prematurity.

b Per 1-dB increase in road traffic noise or aircraft noise or a 1-point increase in nitrogen dioxide (μg/m3).