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Night-Time Exposure to Road, Railway, Aircraft, and Recreational Noise Is Associated with Hypnotic Psychotropic Drug Dispensing for Chronic Insomnia in the Paris Metropolitan Area

Maxime Chauvineau, Sabine Host, Khadim Ndiaye, Matthieu Sineau, Victor Decourt, Manuel Hellot, Fanny Mietlicki and Damien Léger ()
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Maxime Chauvineau: VIFASOM (UMR Vigilance Fatigue Sommeil et Santé Publique), Université Paris Cité, 75006 Paris, France
Sabine Host: Observatoire Régional de Santé (ORS) Île-de-France, 93200 Saint-Denis, France
Khadim Ndiaye: Observatoire Régional de Santé (ORS) Île-de-France, 93200 Saint-Denis, France
Matthieu Sineau: Bruitparif, 93200 Saint-Denis, France
Victor Decourt: Bruitparif, 93200 Saint-Denis, France
Manuel Hellot: Bruitparif, 93200 Saint-Denis, France
Fanny Mietlicki: Bruitparif, 93200 Saint-Denis, France
Damien Léger: VIFASOM (UMR Vigilance Fatigue Sommeil et Santé Publique), Université Paris Cité, 75006 Paris, France

IJERPH, 2025, vol. 22, issue 11, 1-23

Abstract: Urban environmental noise represents a major public health issue contributing to chronic sleep disturbances, mainly from road, aircraft, and railway traffic. Night-time recreational noise from cafés, bars, and restaurants has emerged as a frequent source of sleep complaints but remains poorly understood, along with the influence of sociodemographic and economic factors. We addressed this gap by conducting a large-scale ecological study across the Paris Metropolitan Area (~10.5 million inhabitants) examining associations between the Average Energetic Index of night-time noise (AEI L n ) from road, aircraft, railway, and recreational sources and the prevalence of adults aged 18–79 reimbursed for hypnotic psychotropic drugs prescribed for chronic insomnia between 2017 and 2019, stratified by sex, age, and socioeconomic status. The AEI L n represents the population-weighted average energy noise level within each territory at night (22:00–06:00 in France), calculated at the IRIS level (~2487 inhabitants per IRIS). The dispensing of hypnotic psychotropic drugs concerned 513,276 inhabitants (65.4 per 1000 inhabitants [‰]) on average per year. About 8 million inhabitants (75.7%) are exposed to night-time road traffic noise exceeding WHO health guidelines, followed by railway (~1.2 million, 11.6%), recreational (~1.2 million, 11.5%), and aircraft noise (~1.0 million, 9.8%). Each 5 dB(A) increase in AEI L n was significantly associated ( p < 0.001) with higher dispensing of hypnotic psychotropic drugs, strongest for road noise (+1.0‰), followed by recreational (+0.8‰), aircraft (+0.5‰), and railway noise (+0.3‰). Effects were significantly greater among individuals aged >50 (+8.3‰), women (+2.0‰), and those in the most socioeconomically deprived areas (+2.5‰). These results support proactive public policies aimed at reducing noise from transportation and recreational activities in densely urban areas to mitigate chronic insomnia.

Keywords: noise pollution; sleep disorders; insomnia; hypnotics; recreational noise; public health (search for similar items in EconPapers)
JEL-codes: I I1 I3 Q Q5 (search for similar items in EconPapers)
Date: 2025
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