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Disentangling the effects of traffic-related noise and air pollution on blood pressure: indoor noise levels and protections

机译:弄清交通噪声和空气污染对血压的影响:室内噪声水平和防护

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Outdoor road traffic noise levels are associated with hypertension (HT). Studies on blood pressure (BP) are inconsistent and the true indoor traffic noise exposure may differ due to protections against noise. We analysed the effects of long-term exposure to outdoor and indoor traffic noise levels on HT, systolic (SBP) and diastolic BP (DBP, mmHg), adjusting for outdoor annual average concentrations of near-road traffic-related air pollution (nitrogen dioxide, NO_2) among 1926 participants (aged 36-82) from the Catalan REGICOR study. Long-term outdoor residential levels of traffic noise at night (L_(night), in A-weighted dB) and annual averages of NO_2 (in μg/m~3) were estimated at the postal addresses' facades with a city-specific noise model and a land-use regression model, respectively. Indoor traffic noise was calculated from outdoor noise levels subtracting the attenuations in dB according to reported noise protections. Median noise levels were 56.7 dB outdoors and 27.1 dB indoors. Spearman correlations between outdoor and indoor noise with NO_2 were 0.75 and 0.23, respectively. Outdoor noise was only associated with HT (OR=1.19,95%CI: 1.02,1.40), whereas there was a suggestive association of indoor noise with both HT (OR=1.06,95%CI: 0.99,1.13) and SBP (β=0.38, 95%CI: -0.08, 0.83) per 5 dB increase in outdoor noise levels. NO_2 was also associated with both outcomes after adjustment for indoor noise. Findings for indoor traffic noise levels are more plausible than those for outdoor traffic noise. The use of indoor traffic noise estimates help to disentangle the effects from those of traffic-related air pollution.
机译:户外道路交通噪音水平与高血压(HT)有关。血压(BP)的研究不一致,并且由于采取了防噪音措施,因此真正的室内交通噪声暴露可能会有所不同。我们分析了长期暴露在室外和室内交通噪声水平下对HT,收缩压(SBP)和舒张压BP(DBP,mmHg)的影响,并针对室外近年与道路交通相关的空气污染(二氧化氮)的年平均浓度进行了调整,NO_2)来自加泰罗尼亚REGICOR研究的1926名参与者(年龄在36-82岁之间)。在特定城市的邮政地址立面处,估计夜间室外长期居住交通噪声水平(L_(夜),以A加权dB为单位)和NO_2的年平均水平(以μg/ m〜3为单位)模型和土地利用回归模型。根据报告的噪声保护措施,通过从室外噪声水平减去以dB为单位的衰减来计算室内交通噪声。中位噪声水平为室外56.7 dB,室内27.1 dB。 NO_2在室内外噪声之间的Spearman相关系数分别为0.75和0.23。室外噪声仅与HT(OR = 1.19,95%CI:1.02,1.40)相关,而室内噪声与HT(OR = 1.06,95%CI:0.99,1.13)和SBP(β在室外噪声电平每增加5 dB,= 0.38,95%CI:-0.08,0.83)。调整室内噪声后,NO_2也与两种结果相关。室内交通噪声水平的发现比室外交通噪声的发现更合理。室内交通噪声估计的使用有助于将影响与交通相关空气污染的影响区分开。

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