Changes for page 4.1.1 - LDEN – Day-evening-night noise level
Last modified by Emily West on 2022/02/08 13:31
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edited by Emily West
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edited by Emily West
on 2022/01/10 14:39
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Renamed from xwiki:Metric and Key Performance Indicators.4\.1\.1 - LDEN – Day-evening-night noise level.WebHome
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... ... @@ -1,0 +1,89 @@ 1 += 4.1.1 - LDEN – Day-evening-night noise level = 2 + 3 + 4 +(% class="table-bordered" %) 5 +|=(% style="width: 79px;" %)Topic|=(% style="width: 139px;" %)Urban challenges|=(% style="width: 666px;" %)Sub-challenges 6 +|(% style="width:79px" %)Social|(% style="width:139px" %)4 - Public Health and Wellbeing|(% style="width:666px" %)4.1 Acoustics 7 + 8 +(% class="table-bordered" %) 9 +|(% style="width:211px" %)((( 10 +====== **Description** ====== 11 +)))|(% style="width:730px" %)The LDEN is an acoustic indicator for sound environment. LDEN is expressed in dB(A) because it is based on a combination of equivalent sound pressure levels Leq,T (energetic summation through logarithmic law), calculated with the A ponderation on 3 periods (day, evening, night), depending on the sound source emission (i.e. road traffic conditions). Thus LDEN is a daily equivalent sound pressure level (T=00h-24h), with a 0dB(A) penalty increase for the Day period (T=6h-18h), a 5dB(A) penalty increase for the Evening period (T=18h-22h) and a 10dB(A) penalty increase for the Night period (T=22h-6h) 12 +|(% style="width:211px" %)((( 13 +===== **Scale as linked to D2.2 framework** ===== 14 +)))|(% style="width:730px" %)((( 15 +* City 16 +* Neighborhood 17 +* Street 18 +* Household 19 +* Object 20 +))) 21 +|(% style="width:211px" %)((( 22 +====== **Data source [ link to data framework]** ====== 23 +)))|(% style="width:730px" %)((( 24 +* Georeferenced data for built-up area: data from OPEN STREET MAP (OSM) 25 +* Road traffic counts: data from district, city or regional agencies 26 +* NBS data: qualitative information given by N4C consortium (when different scenarios will be available by other WPs and when additional functionalities will be integrated in numerical software) 27 +))) 28 +|(% style="width:211px" %)((( 29 +====== **Needs** ====== 30 +)))|(% style="width:730px" %)((( 31 +* Required tool: 32 +* Measured LDEN (in situ measurements): integrating sonometer, either professional, low-cost or even smartphone [[http:~~/~~/noise-planet.org/noisecapture.html>>http://noise-planet.org/noisecapture.html]] 33 +* Simulated LDEN (numerical predictions): noise prediction software, e.g. open-source tool “NoiseModelling” http:~/~/noise-planet.org/noisemodelling.html 34 +))) 35 +|(% style="width:211px" %)((( 36 +====== **Expected Outputs** ====== 37 +)))|(% style="width:730px" %)((( 38 +* quantitative 39 +* units: decibels with A ponderation: “dB(A)” 40 +))) 41 +|(% style="width:211px" %)((( 42 +====== **Calculation methods** ====== 43 +)))|(% style="width:730px" %)((( 44 +[[image:1641470704668-864.png]] 45 +))) 46 +|(% style="width:211px" %)((( 47 +====== **Links and references** ====== 48 +)))|(% style="width:730px" %)((( 49 +* Anderson, L.M., B.E. 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Tang. 2010. « Can surrounding greenery reduce noise annoyance at home ? » Science of the Total Environment 408: 4376‑84 68 +* Liu, J., J. Kang, T. Luo, H. Behm, et T. Coppack. 2013. « Spatiotemporal variability of soundscapes in a multiple functional urban area ». Landscape and Urban Planning 115: 1‑9. 69 +* Marquis-Favre, C., E. Premat, et D. Aubrée. 2005. « Noise and its Effects – A Review on Qualitative Aspects of Sound. Part II: Noise and Annoyance ». Acta Acustica united with Acustica 91 (4): 626‑42. 70 +* Marquis-Favre, C., E. Premat, D. Aubrée, et M. Vallet. 2005. « Noise and its Effects – A Review on Qualitative Aspects of Sound. Part I: Notions and Acoustic Ratings ». Acta Acustica united with Acustica 91 (4): 613‑25 71 +* Miedema, Henk M. E. 2004. « Relationship between exposure to multiple noise sources and noise annoyance ». The Journal of the Acoustical Society of America 116 (2): 949‑57. doi:10.1121/1.1766305 72 +* Raimbault, M., et D. 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Kang. 2015. « Using natural means to reduce surface transport noise during propagation outdoors ». Appl. Acoust. 92: 86‑101 78 +* Viollon, S., C. Lavandier, et C. Drake. 2002. « Influence of Visual Setting on Sound Ratings in an Urban Environment ». Appl. Acoust. 63 (5): 493‑511. doi:10.1016/S0003-682X(01)00053-6 79 +* Watts, G., L. Chinn, et N. Godfrey. 1999. « The effects of vegetation on the perception of traffic noise ». Appl. Acoust. 56 (1): 39‑56. 80 +* Wilson, D.K., N. Wayant, E.T. Nykaza, C.L. Pettit, et C.M. Armstrong. 2015. « Hierarchical modeling approach to community noise annoyance ». J. Acoust. Soc. Amer. 138 (3): 1731‑1731 81 +* Yang, F., Z. Bao, et Z. Zhu. 2011. « An assessment of psychological noise reduction by landscape plants ». Int. J. Environ. Res. Public Health 8: 1032‑48 82 +* Yu, L., et J. Kang. 2010. « Factors influencing the sound preference in urban open space ». Appl. Acoust. 71: 622‑33 83 +* Zhang, B., L. Shi, et G. Di. 2003. « The influence of the visibility of the source on the subjective annoyance due to its noise ». Appl. Acoust. 64 (4): 1205‑15 84 +* http:~/~/noise-planet.org/noisecapture.html 85 +* http:~/~/noise-planet.org/noisemodelling.html 86 +))) 87 + 88 +(% class="lead" %) 89 +