The impact of different transportation noise sources and noise environments on arterial stiffness remains unknown.
We evaluated the association between residential outdoor exposure to annual average road, railway, and aircraft noise levels, total noise intermittency (IR), and total number of noise events (NE) and brachial-ankle pulse wave velocity (baPWV) following a cross-sectional design.
We measured baPWV (meters/second) in 2,775 participants (49–81 y old) at the second follow-up (2010–2011) of the Swiss Cohort Study on Air Pollution and Lung and Heart Diseases in Adults (SAPALDIA). We assigned annual average road, railway, and aircraft noise levels ( ), total day- and nighttime and ( , none or constant noise; , high fluctuation) at the most exposed façade using 2011 Swiss noise models. We applied multivariable linear mixed regression models to analyze associations.
Medians [interquartile ranges (IQRs)] were (3.1) m/s; (8.0) dB; (8.1) dB; (99.7% exposed): 54.2 (10.6) dB; (179); (870); (27); and (40.3). We observed a 0.87% (95% CI: 0.31, 1.43%) increase in baPWV per IQR of , which was greater with or with daytime sleepiness. We observed a nonsignificant positive association between and baPWV in urban areas and a negative tendency in rural areas. , but not , was associated with baPWV. Associations were independent of the other noise sources and air pollution.
Long-term exposure to railway noise, particularly in an intermittent nighttime noise environment, and to nighttime noise events, mainly related to road noise, may affect arterial stiffness, a major determinant of cardiovascular disease. Ascertaining noise exposure characteristics beyond average noise levels may be relevant to better understand noise-related health effects. https://doi.org/10.1289/EHP1136