Application of land-use regression models to estimate sound pressure levels and frequency components of road traffic noise in Taichung, Taiwan

被引:37
作者
Chang, Ta-Yuan [1 ]
Liang, Chih-Hsiang [1 ]
Wu, Chang-Fu [2 ]
Chang, Li-Te [3 ]
机构
[1] China Med Univ, Coll Publ Hlth, Dept Occupat Safety & Hlth, 91 Hsueh Shih Rd, Taichung 40402, Taiwan
[2] Natl Taiwan Univ, Inst Occupat Med & Ind Hyg, Coll Publ Hlth, Taipei, Taiwan
[3] Feng Chia Univ, Dept Environm Engn & Sci, Taichung, Taiwan
关键词
Land-use regression; Octave-band frequency analysis; Prediction; Road traffic noise; Validity; AIR-POLLUTION EXPOSURE; ENVIRONMENTAL NOISE; BLOOD-PRESSURE; HYPERTENSION; EUROPE; AREAS;
D O I
10.1016/j.envint.2019.104959
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Few studies have applied land-use regression to predict road traffic noise exposure, and there are few predictive models for different frequencies. This study aimed to measure 24-h average road traffic noise levels and to analyze the frequency components over one year to establish land-use regression models of noise exposure. Fifty monitoring stations were set up to conduct 3 measurements for A-weighted equivalent sound pressure levels over 24 h (L-eq,L-24h) and night equivalent sound pressure levels (L-night), as well as octave-band analyses, during the 2013-2014 period. Noise measurements were integrated with land-use types, road and traffic information, meteorological data and geographic information systems to construct land-use regression models. Leave-one-out cross-validation was performed to test the validity of the predictive models. The annual means of L-eq,L-24h and L-night were 66.4 +/- 4.7 A-weighed decibels (dBA) and 62.1 +/- 6.0 dBA, respectively. Octave-band frequency analyses revealed that the highest means over 24 h and at night were 61.4 +/- 5.3 decibels (dB) and 56.7 +/- 6.6 dB (both at 1000 Hz), respectively. The model-explained variance (R-2) of the full-frequency noise was 0.83 for L-eq,L-24h and 0.79 for L-night. The R-2 values for octave-band-frequency noise ranged from 0.67 to 0.88 for L-eq,L-24h and 0.65 to 0.85 for L-night, with the highest R-2 at 250 Hz for L-eq,L-24h and at 125 Hz for L-night. The differences between the model R-2 and the leave-one-out cross-validation R-2 ranged from 5% to 15% for both L-eq,L-24h and L-night at all frequencies. In the validation, the root mean squared error was 2.09 dBA and 2.80 dBA for the full-frequency L-eq,L-24 and L-night, respectively, and ranged from 1.89 to 2.62 dB and from 2.51 to 3.28 dB for the octave-band-frequency L-eq,L-24h and L-night, respectively. This study observed that the annual means of the measured L-eq,L-24h and L-night in Taichung were both above 60 dBA and had the highest level at 1000 Hz. The developed land-use regression models of L-eq,L-24 and L-night both had good predictive capacity for the full frequency spectrum and within octave bands and can therefore be applied for epidemiological studies.
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页数:11
相关论文
共 38 条
[1]   Application of land use regression modelling to assess the spatial distribution of road traffic noise in three European cities [J].
Aguilera, Inmaculada ;
Foraster, Maria ;
Basagaa, Xavier ;
Corradi, Elisabetta ;
Deltell, Alexandre ;
Morelli, Xavier ;
Phuleria, Harish C. ;
Ragettli, Martina S. ;
Rivera, Marcela ;
Thomasson, Alexandre ;
Slama, Remy ;
Kuenzli, Nino .
JOURNAL OF EXPOSURE SCIENCE AND ENVIRONMENTAL EPIDEMIOLOGY, 2015, 25 (01) :97-105
[2]   The spatial relationship between traffic-generated air pollution and noise in 2 US cities [J].
Allen, Ryan W. ;
Davies, Hugh ;
Cohen, Martin A. ;
Mallach, Gary ;
Kaufman, Joel D. ;
Adar, Sara D. .
ENVIRONMENTAL RESEARCH, 2009, 109 (03) :334-342
[3]   Auditory and non-auditory effects of noise on health [J].
Basner, Mathias ;
Babisch, Wolfgang ;
Davis, Adrian ;
Brink, Mark ;
Clark, Charlotte ;
Janssen, Sabine ;
Stansfeld, Stephen .
LANCET, 2014, 383 (9925) :1325-1332
[4]   Effects of long-term exposure to air pollution on natural-cause mortality: an analysis of 22 European cohorts within the multicentre ESCAPE project [J].
Beelen, Rob ;
Raaschou-Nielsen, Ole ;
Stafoggia, Massimo ;
Andersen, Zorana Jovanovic ;
Weinmayr, Gudrun ;
Hoffmann, Barbara ;
Wolf, Kathrin ;
Samoli, Evangelia ;
Fischer, Paul ;
Nieuwenhuijsen, Mark ;
Vineis, Paolo ;
Xun, Wei W. ;
Katsouyanni, Klea ;
Dimakopoulou, Konstantina ;
Oudin, Anna ;
Forsberg, Bertil ;
Modig, Lars ;
Havulinna, Aki S. ;
Lanki, Timo ;
Turunen, Anu ;
Oftedal, Bente ;
Nystad, Wenche ;
Nafstad, Per ;
De Faire, Ulf ;
Pedersen, Nancy L. ;
Ostenson, Claes-Goeran ;
Fratiglioni, Laura ;
Penell, Johanna ;
Korek, Michal ;
Pershagen, Goeran ;
Eriksen, Kirsten Thorup ;
Overvad, Kim ;
Ellermann, Thomas ;
Eeftens, Marloes ;
Peeters, Petra H. ;
Meliefste, Kees ;
Wang, Meng ;
Bueno-de-Mesquita, Bas ;
Sugiri, Dorothea ;
Kraemer, Ursula ;
Heinrich, Joachim ;
de Hoogh, Kees ;
Key, Timothy ;
Peters, Annette ;
Hampel, Regina ;
Concin, Hans ;
Nagel, Gabriele ;
Ineichen, Alex ;
Schaffner, Emmanuel ;
Probst-Hensch, Nicole .
LANCET, 2014, 383 (9919) :785-795
[5]   Development of NO2 and NOx land use regression models for estimating air pollution exposure in 36 study areas in Europe - The ESCAPE project [J].
Beelen, Rob ;
Hoek, Gerard ;
Vienneau, Danielle ;
Eeftens, Marloes ;
Dimakopoulou, Konstantina ;
Pedeli, Xanthi ;
Tsai, Ming-Yi ;
Kunzli, Nino ;
Schikowski, Tamara ;
Marcon, Alessandro ;
Eriksen, Kirsten T. ;
Raaschou-Nielsen, Ole ;
Stephanou, Euripides ;
Patelarou, Evridiki ;
Lanki, Timo ;
Yli-Tuomi, Tarja ;
Declercq, Christophe ;
Falq, Gregoire ;
Stempfelet, Morgane ;
Birk, Matthias ;
Cyrys, Josef ;
von Klot, Stephanie ;
Nador, Gizella ;
Varro, Mihaly Janos ;
Dedele, Audrius ;
Grazuleviciene, Regina ;
Moelter, Anna ;
Lindley, Sarah ;
Madsen, Christian ;
Cesaroni, Giulia ;
Ranzi, Andrea ;
Badaloni, Chiara ;
Hoffmann, Barbara ;
Nonnemacher, Michael ;
Kraemer, Ursula ;
Kuhlbusch, Thomas ;
Cirach, Marta ;
de Nazelle, Audrey ;
Nieuwenhuijsen, Mark ;
Bellander, Tom ;
Korek, Michal ;
Olsson, David ;
Stromgren, Magnus ;
Dons, Evi ;
Jerrett, Michael ;
Fischer, Paul ;
Wang, Meng ;
Brunekreef, Bert ;
de Hoogh, Kees .
ATMOSPHERIC ENVIRONMENT, 2013, 72 :10-23
[6]  
Berglund B., 1999, World health organization: Guidelines for community noise
[7]   Acute effects of noise exposure on 24-h ambulatory blood pressure in hypertensive adults [J].
Chang, Ta-Yuan ;
Liu, Chiu-Shong ;
Hwang, Bing-Fang ;
Hsieh, Hsiu-Hui ;
Bao, Bo-Ying ;
Chen, Chiou-Jong ;
Wang, Ven-Shing ;
Lai, Jim-Shoung .
JOURNAL OF HYPERTENSION, 2015, 33 (03) :507-514
[8]   Road traffic noise frequency and prevalent hypertension in Taichung, Taiwan: A cross-sectional study [J].
Chang, Ta-Yuan ;
Beelen, Rob ;
Li, Su-Fei ;
Chen, Tzu-I ;
Lin, Yen-Ju ;
Bao, Bo-Ying ;
Liu, Chiu-Shong .
ENVIRONMENTAL HEALTH, 2014, 13
[9]   Noise frequency components and the prevalence of hypertension in workers [J].
Chang, Ta-Yuan ;
Liu, Chiu-Shong ;
Young, Li-Hao ;
Wang, Ven-Shing ;
Jian, Shen-En ;
Bao, Bo-Ying .
SCIENCE OF THE TOTAL ENVIRONMENT, 2012, 416 :89-96
[10]   Correlation between co-exposures to noise and air pollution from traffic sources [J].
Davies, H. W. ;
Vlaanderen, J. J. ;
Henderson, S. B. ;
Brauer, M. .
OCCUPATIONAL AND ENVIRONMENTAL MEDICINE, 2009, 66 (05) :347-350