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Noise emissions from road traffic are influenced substantially by the factors driving speed and traffic flow (see section 3.1.2.4). Reducing the driving speed from 50 km/h (about 31 mph) to 30 km/h (about 19 mph) means a reduction of the average sound level of about 2.5 dB(A). A reduction from 80 km/h (about 50 mph) to 60 km/h (about 37 mph) leads to a noise reduction of about 2 dB(A), from 130 km/h (about 81 mph) to 100 km/h (about 62 mph) between 1 and 3 dB(A) (depending on the truck percentage). Besides the reduction of noise, a lower driving speed also means an increase of road safety and driving quality. Another frequent consequence is the reduction of pollutant emissions, but the effects on the air quality must be considered on an individual basis (Climate Booklet for Urban Development, 2012). The traffic flow and a person's driving habits have an enormous influence on noise emissions. At an average speed of 45 km/h (about 28 mph), a car's noise emission level is by about 4 dB(A) higher when it repeatedly brakes and accelerates than at a constant flow. At an average speed of 30 km/h (about 19 mph), the difference even amounts to about 5 dB(A). A speed reduction from 50 km/h (31 mph) to 30 km/h (about 19 mph) can reduce the maximum level by 7 dB(A) if accelerations are avoided (ALD, 2010). Lower speeds also help to achieve the following aims:
The positive effects are opposed to the following disadvantages:
If the resident population shall be protected from a high noise exposure at least during the night and be granted nighttime peace, a speed limit restricted to the nighttime hours could be an adequate measure if speed limits during the day are not possible. A slow and uniform traffic flow without disturbing braking or accelerating sounds at high engine speeds can be realized through an appropriate road design (see also section 7.1.4). This can be applied to residential roads (no confusing obstacle arrangements) and to major roads as well, which should not be oversized. The driving speed within towns or cities can be reduced through narrow roads. If the cross-section of a road is reduced, the additional space can be used for bicycle or parking lanes, green strips or constructional design elements. A uniform driving speed can also be realized through phased traffic lights or the installation of a roundabout at an existing crossing. A reduction of the road cross-section could also lead to an increased distance between road and buildings, which in turn reduces the sound level and the subjective perception of noise as well. If the sight of the passing vehicles is prevented by vegetation for example, residents often gain the subjective impression of a noise reduction even if the actual noise impact remains unchanged.
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