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

Table 3.

Multilevel Model Parameter Estimates for Nitrogen Dioxide Levels at School on Children's Cognitive Performance, With Further Adjustment for Aircraft and Road Traffic Noise Exposure at School, in the United Kingdom Air Pollution Subsample of the RANCH Project, 2001–2003 (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
Reading comprehension 651
 Nitrogen dioxide 0.00041 −0.013, 0.014 0.95 0.004 −0.009, 0.018 0.53
 Road traffic noise −0.004 −0.019, 0.012 0.65
 Aircraft noise −0.012* −0.023, −0.000063 0.05
Recognition memory 641
 nitrogen dioxide −0.005 −0.041, 0.031 0.78 0.012 −0.021, 0.044 0.48
 Road traffic noise −0.016 −0.054, 0.022 0.40
 Aircraft noise −0.045* −0.073, −0.017 <0.01
Information recall 638
 Nitrogen dioxide 0.012 −0.036, 0.061 0.62 0.015 −0.033, 0.062 0.54
 Road traffic noise 0.036 −0.020, 0.092 0.21
 Aircraft noise −0.043* −0.086, −0.000036 0.05
Conceptual recall 636
 Nitrogen dioxide −0.002 −0.015, 0.011 0.79 0.00023 −0.012, 0.013 0.97
 Road traffic noise 0.007 −0.008, 0.022 0.34
 Aircraft noise −0.015* −0.026, −0.003 0.01
Working memory 580
 Nitrogen dioxide 0.036 −0.174, 0.246 0.74 0.003 −0.295, 0.301 0.98
 Road traffic noise 0.034 −0.141, 0.209 0.70
 Aircraft noise 0.00086 −0.109, 0.111 0.99

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

* P ≤ 0.05.

a All models were 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.

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