2020
DOI: 10.3390/atmos11040422
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Modelling Cyclists’ Multi-Exposure to Air and Noise Pollution with Low-Cost Sensors—The Case of Paris

Abstract: Cyclists are particularly exposed to air and noise pollution because of their higher ventilation rate and their proximity to traffic. However, few studies have investigated their multi-exposure and have taken into account its real complexity in building statistical models (nonlinearity, pseudo replication, autocorrelation, etc.). We propose here to model cyclists’ exposure to air and noise pollution simultaneously in Paris (France). Specifically, the purpose of this study is to develop a methodology based on a… Show more

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Cited by 13 publications
(13 citation statements)
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References 62 publications
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“…(2018b) have reported a negative association between exposure levels to noise and wind speed, with a decrease of -0.371 dB(A) for each additional km/h, and no effect with temperature. On the other hand, Apparicio et al (2016) and Gelb and Apparicio (2020) found no significant relationship between exposure to noise and temperature, humidity, and wind speed.…”
Section: Weathermentioning
confidence: 80%
“…(2018b) have reported a negative association between exposure levels to noise and wind speed, with a decrease of -0.371 dB(A) for each additional km/h, and no effect with temperature. On the other hand, Apparicio et al (2016) and Gelb and Apparicio (2020) found no significant relationship between exposure to noise and temperature, humidity, and wind speed.…”
Section: Weathermentioning
confidence: 80%
“…However, Gelb and Apparicio [28] observed that in Paris, France, close proximity to traffic can impose wellbeing threats to AT users via noise and air pollution. This may erode the corresponding health benefits.…”
Section: Physical and Mental Wellbeing Outcomesmentioning
confidence: 99%
“…To achieve the first objective, three Bayesian models were constructed using the brms package [46,47], in which the dependent variables are the level of noise exposure, the level of NO 2 exposure and the inhaled dose of NO 2 , and the observations are the one-minute segments (N = 4,157, 4,368 and 4,368, respectively). The models proposed here are largely based on recent studies [43,48,49]: GAMMAR models (generalized additive mixed model with an autoregressive term) with a student distribution for the dependent variable [50]. Consequently, four types of terms were introduced into each model: random effects terms, non-linear terms (i.e.…”
Section: Modelling Road Traffic Noise Exposure Air Pollution Exposure and Inhalationmentioning
confidence: 99%
“…As done previously [43,48,49], to take the temporal and spatial variability into account, the time of day (number of minutes passed since 08:00) and the geographic coordinates were introduced as non-linear terms (i.e., splines). Therefore, we expected to observe peaks of exposure and inhalation during the morning and evening rush hours, and in the most densely populated areas of Delhi.…”
Section: Modelling Road Traffic Noise Exposure Air Pollution Exposure and Inhalationmentioning
confidence: 99%