Traffic-Related High Sleep Disturbance in the LIFE-Adult Cohort Study: A Comparison to the WHO Exposure-Response-Curves

Sleep is negatively affected by environmental noise. In the present study, we investigated self-reported high sleep disturbances (being "highly sleep disturbed"-HSD) from road traffic (primary and secondary road networks), rail (train and tram) and air traffic noise in the LIFE-Adult cohor...

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Veröffentlicht in:International journal of environmental research and public health 2023-03, Vol.20 (6), p.4903
Hauptverfasser: Schubert, Melanie, Romero Starke, Karla, Gerlach, Julia, Reusche, Matthias, Kaboth, Pauline, Schmidt, Wolfram, Friedemann, Dieter, Hegewald, Janice, Zeeb, Hajo, Zülke, Andrea, Riedel-Heller, Steffi G, Seidler, Andreas
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container_issue 6
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container_title International journal of environmental research and public health
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creator Schubert, Melanie
Romero Starke, Karla
Gerlach, Julia
Reusche, Matthias
Kaboth, Pauline
Schmidt, Wolfram
Friedemann, Dieter
Hegewald, Janice
Zeeb, Hajo
Zülke, Andrea
Riedel-Heller, Steffi G
Seidler, Andreas
description Sleep is negatively affected by environmental noise. In the present study, we investigated self-reported high sleep disturbances (being "highly sleep disturbed"-HSD) from road traffic (primary and secondary road networks), rail (train and tram) and air traffic noise in the LIFE-Adult cohort study in Leipzig, Germany. For this, we used exposure data from 2012 and outcome data of Wave 2 (collected during 2018-2021). HSD was determined and defined according to internationally standardized norms. The highest risk for transportation noise-related HSD was found for aircraft noise: the odds ratio (OR) was 19.66, 95% CI 11.47-33.71 per 10 dB increase in L . For road and rail traffic, similar risk estimates were observed (road: OR = 2.86, 95% CI 1.92-4.28; rail: OR = 2.67, 95% CI 2.03-3.50 per 10 dB L increase). Further, we compared our exposure-risk curves with the curves of the WHO environmental noise guidelines for the European region. The proportion of individuals with HSD for a given noise level was lower for rail traffic but higher for aircraft noise in the LIFE study than in the WHO curves. For road traffic, curves are not directly comparable because we also included the secondary road network. The results of our study add to the body of evidence for increased health risks by traffic noise. Moreover, the results indicate that aircraft noise is particularly harmful to health. We recommend reconsidering threshold values for nightly aircraft exposure.
doi_str_mv 10.3390/ijerph20064903
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In the present study, we investigated self-reported high sleep disturbances (being "highly sleep disturbed"-HSD) from road traffic (primary and secondary road networks), rail (train and tram) and air traffic noise in the LIFE-Adult cohort study in Leipzig, Germany. For this, we used exposure data from 2012 and outcome data of Wave 2 (collected during 2018-2021). HSD was determined and defined according to internationally standardized norms. The highest risk for transportation noise-related HSD was found for aircraft noise: the odds ratio (OR) was 19.66, 95% CI 11.47-33.71 per 10 dB increase in L . For road and rail traffic, similar risk estimates were observed (road: OR = 2.86, 95% CI 1.92-4.28; rail: OR = 2.67, 95% CI 2.03-3.50 per 10 dB L increase). Further, we compared our exposure-risk curves with the curves of the WHO environmental noise guidelines for the European region. The proportion of individuals with HSD for a given noise level was lower for rail traffic but higher for aircraft noise in the LIFE study than in the WHO curves. For road traffic, curves are not directly comparable because we also included the secondary road network. The results of our study add to the body of evidence for increased health risks by traffic noise. Moreover, the results indicate that aircraft noise is particularly harmful to health. 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In the present study, we investigated self-reported high sleep disturbances (being "highly sleep disturbed"-HSD) from road traffic (primary and secondary road networks), rail (train and tram) and air traffic noise in the LIFE-Adult cohort study in Leipzig, Germany. For this, we used exposure data from 2012 and outcome data of Wave 2 (collected during 2018-2021). HSD was determined and defined according to internationally standardized norms. The highest risk for transportation noise-related HSD was found for aircraft noise: the odds ratio (OR) was 19.66, 95% CI 11.47-33.71 per 10 dB increase in L . For road and rail traffic, similar risk estimates were observed (road: OR = 2.86, 95% CI 1.92-4.28; rail: OR = 2.67, 95% CI 2.03-3.50 per 10 dB L increase). Further, we compared our exposure-risk curves with the curves of the WHO environmental noise guidelines for the European region. 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subjects Adult
Air traffic control
Aircraft
Aircraft noise
Background noise
Cohort analysis
Cohort Studies
Disease
Dose-response effects
Environmental Exposure - adverse effects
Exposure
Health aspects
Health risks
Humans
Noise levels
Noise pollution
Noise, Transportation - adverse effects
Norms
Questionnaires
Railroads
Roads
Sleep
Sleep disorders
Sleep Wake Disorders - epidemiology
Sleep Wake Disorders - etiology
Systematic review
Traffic
Transportation networks
Transportation noise
Vehicles
World Health Organization
title Traffic-Related High Sleep Disturbance in the LIFE-Adult Cohort Study: A Comparison to the WHO Exposure-Response-Curves
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