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Outdoor propagation – cylindrical field. Line Sources Many noise sources found outdoors can be considered line sources: roads, railways, airtracks, etc.

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Outdoor propagation – cylindrical field

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Line Sources Many noise sources found outdoors can be considered line sources: roads, railways, airtracks, etc. Geometry for propagation from a line source to a receiver - in this case the total power is dispersed over a cylindrical surface: In which Lw is the sound power level per meter of line source

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Coherent cylindrical field The power is dispersed over an infinitely long, pulsating cylinder: r L In which Lw is the sound power level per meter of line source

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discrete (and incoherent) linear sourcesdiscrete (and incoherent) linear sources Another common case is when a number of point sources are located along a line, each emitting sound mutually incoherent with the others: Geometry of propagation for a discrete line source and a receiver - We could compute the SPL at the receiver as the energetic (incoherent) summation of many spherical wavefronts. But at the end the result shows that SPL decays with the same cylindrical law as with a coherent source: Lw The SPL reduces by 3 dB for each doubling of distance d. Note that the incoherent SPL is 2 dB louder than the coherent one!

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Example of a discrete line source: cars on the road Distance a between two vehicles is proportional to their speed: In which V is speed in km/h and N is the number of vehicles passing in 1 h The sound power level L Wp of a single vehicle is: - Constant up to 50 km/h - Increases linearly between 50 km/h and 100 km/h (3dB/doubling) - Above 100 km/h increases with the square of V (6dB/doubling)

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Example of a discrete line source: cars on the road Hence there is an optimal speed, which causes the minimum value of SPL, which lies around 70 km/h Modern vehicles have this optimal speed at even larger speeds, for example it is 85 km/h for the Toyota Prius

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Outdoors propagation – excess attenuation

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Free field: excess attenuation Other factors causing additional attenuation during outdoors progation are: air absorption absorption due to presence of vegetation, foliage, etc. metereological conditions (temperature gradients, wind speed gradients, rain, snow, fog, etc.) obstacles (hills, buildings, noise barriers, etc.) All these effects are combined into an additional term L, in dB, which is appended to the free field formula: L I = L p = L W - 20 log r - 11 + 10 log Q - L (dB) Most of these effects are relevant only at large distance form the source. The exception is shielding (screen effect), which instead is maximum when the receiver is very close to the screen

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Excess attenuation: temperature gradient Figure 1: normal situation, causing shadowing Shadow zone

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Excess attenuation: wind speed gradient Vectorial composition of wind speed and sound speed Effect: curvature of sound rays

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Excess attenuation: air absorption Air absorption coefficients in dB/km (from ISO 9613-1 standard) for different combinations of frequency, temperature and humidity: Frequency (octave bands) T (°C)RH (%)631252505001000200040008000 10700,120,411,041,933,669,6632,8117,0 15200,270,651,222,708,1728,288,8202,0 15500,140,481,222,244,1610,836,2129,0 15800,090,341,072,404,158,3123,782,8 20700,090,341,132,804,989,0222,976,6 30700,070,260,963,147,4112,723,159,3

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Improved Methods for the Assessment of the Generic Impact of Noise to the Environment 6th Framework Programme, Area 1.2.1, Policy-oriented research, contract.

Improved Methods for the Assessment of the Generic Impact of Noise to the Environment 6th Framework Programme, Area 1.2.1, Policy-oriented research, contract.

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