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4. Methods of Information Acquisition for Planning
(Nature measurements, Wind tunnels, Modelling)

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4.3.7    The Model PROKAS for Calculating Air Pollution on Roads

The model PROKAS (BOESINGER, 1996; VDI 3782, Section 8) calculates air pollution along roads on the basis of a Gaussian dispersal model for individual sections of road and road networks. For the calculation of emissions on roads with dense peripheral development, an integrated building model is employed that uses results based on calculations with MISKAM as well as results from wind tunnel studies and field experiments.

The emissions densities for individual sections of road are essentially determined by the traffic volumes, the type of driving, the reference year, and the time-elapsed emissions curves of the emissions factors (cf. Chapter 2.8.2).

In addition, the use of PROKAS requires representative dispersal class statistics with data about the wind velocity, wind direction, and dispersal class distribution.

Figure 4/43a and Figure 4/43b, generated with PROKAS, shows NO2 levels for Stuttgart’s main streets (> 5,000 vehicles/day) for the year 2010 and 2015. Easily recognizable are the highway in the south and the heavily-trafficked streets in the central city and the Neckar Valley, with values up to 80 µg/m3.

 

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Fig. 4/43a: NO2 concentrations for the main roads in Stuttgart for the year 2010, computed with PROKAS; LOHMEYER, 2007

 

Fig. 4/43b: NO2 concentrations for the main roads in Stuttgart for the year 2015, computed with PROKAS; LOHMEYER, 2007
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