TY - JOUR
T1 - The wind effect on sound propagation over urban areas
T2 - Predictions for generic urban sections
AU - Hornikx, M.
AU - Dohmen, M.
AU - Conen, K.
AU - van Hooff, T.
AU - Blocken, B.
PY - 2018/10/15
Y1 - 2018/10/15
N2 - The effect of a downward refracting atmosphere on distant sound propagation over various generic urban areas is predicted. The work uses a two-step approach, by first computing the wind field with computational fluid dynamics (RANS-CFD), and then adopting the mean wind field in a computational acoustics (PSTD-CA) method. These approaches were found to be valid for the studied geometries. For an urban configuration with multiple building blocks, a sound source is located in a street canyon, representing road traffic, and receivers are located at a distance up to 500 m. From results of calculations for various urban configurations, it can be concluded that: the sound levels increase due to the presence of a downward refracting atmosphere, and this effect is larger for higher frequencies; the wind effect ranges from 15 to 23 dB(A); the urban topology close to the source and receiver can largely influence the wind effect; whereas vegetated roofs have the potential to reduce sound levels without wind, in a downward refracting atmosphere the broadband effect is small (<2 dB(A)), however, a potential for reducing noise levels by roofs with low-frequency sound absorption has been identified.
AB - The effect of a downward refracting atmosphere on distant sound propagation over various generic urban areas is predicted. The work uses a two-step approach, by first computing the wind field with computational fluid dynamics (RANS-CFD), and then adopting the mean wind field in a computational acoustics (PSTD-CA) method. These approaches were found to be valid for the studied geometries. For an urban configuration with multiple building blocks, a sound source is located in a street canyon, representing road traffic, and receivers are located at a distance up to 500 m. From results of calculations for various urban configurations, it can be concluded that: the sound levels increase due to the presence of a downward refracting atmosphere, and this effect is larger for higher frequencies; the wind effect ranges from 15 to 23 dB(A); the urban topology close to the source and receiver can largely influence the wind effect; whereas vegetated roofs have the potential to reduce sound levels without wind, in a downward refracting atmosphere the broadband effect is small (<2 dB(A)), however, a potential for reducing noise levels by roofs with low-frequency sound absorption has been identified.
KW - Downward refraction
KW - Road traffic noise
KW - Urban sound propagation
KW - Vegetated roofs
UR - http://www.scopus.com/inward/record.url?scp=85052748776&partnerID=8YFLogxK
U2 - 10.1016/j.buildenv.2018.08.041
DO - 10.1016/j.buildenv.2018.08.041
M3 - Article
AN - SCOPUS:85052748776
SN - 0360-1323
VL - 144
SP - 519
EP - 531
JO - Building and Environment
JF - Building and Environment
ER -