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2. Characteristics and Forms of the Urban Climate
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2.8.2    The Automobile as Pollutant Source

The combustion of petrol or diesel in an automobile motor produces an array of pollutants, of which the following pollutant components stand out in particular measure:

  • Carbon Monoxide (CO)
  • Hydrocarbons (HC) with Benzene
  • Nitrogen Oxides (NOx) = Nitrogen Monoxide and Dioxide (NO, NO2)
  • Lead (Pb)
  • Sulfur Dioxide (SO2)
  • Particulate Matter (PM)

The starting point for the consideration of both emission-side and immission-side exhaust gas levels on roads is the specific pollutant output of motor vehicles, which varies strongly with the respective operating condition. Petrol and diesel motors also exhibit large differences in emissions behavior.

The emission rates of pollutant components in automobile exhaust can be calculated by the multiplication of the temporal traffic volume by the so-called "exhaust emissions factors," which are based in turn on the emissions of an individual car or truck in average condition.

Motor vehicle emissions depend on the speed and manner of driving, i.e. the so-called "driving models" on the roads. A specific driving model can be assigned to every traffic situation. Table 2/3 gives an overview of various driving models with the indication of the average driving speed.

For the determination of the exhaust gas factors, TÜV Rhineland (UBA, 2004) categorized automobiles with various exhaust controls with regards to their exhaust emissions.

Traffic situation

Average speed 
[km/h]

Vast majority characterisation

AB_100_g

85.0

Freeway + streets similar than freeways, speed limit
100 km/h, strong traffic

AB_120

120.0

Freeway + streets similar than freeways, speed limit
120 km/h, 

AB_80

95.0

Freeway + streets similar than freeways, speed limit
80 km/h

AO_1

76.7

country road, straight, good conditions

AO_2

67.5

country road, good condition, twisting

AO_3

60.6

country road,  inconstant twisting

IO_HVS1>50

58.4

Main road, speed limit higher than 50 km/h, flowing traffic with no troubles

IO_HVS2

46.2

Main road, , flowing traffic with minimal troubles

IO_HVS3

39.1

Main road, with right of way,
flowing traffic with mean troubles

IO_HVS4

32.0

Main road,  traffic with much troubles

IO_Kern

19.9

Main street in the city center

IO_Nebenstr_d

18.6

side road with street canyon 

Tab. 2/3: Examples of various styles of driving for different types of roads; Source: UBA (2004)


An additional study examined the emissions of trucks and buses (UBA, 1995a). These emissions data were summarized in a handbook (UBA, 1995b) and were distributed by the Federal Office for Environmental Protection as a PC database.

These emissions factors refer significantly to the pollutants benzene, carbon monoxide, nitrogen oxides, lead, sulfur dioxide, carbon dioxide, hydrocarbons, and particulate matter. Data for diesel particles were not given directly. The proportion of diesel particles can be determined from FIGE (1995) at 60% for cars and 40% for trucks.

In these factors, road gradients and cold engine starts can also be taken into consideration. A cold engine increases exhaust emissions, as the catalytic converter is not yet fully functioning. One can choose in the database from emissions factors for various vehicle categories (e.g. car, truck, bus, motorcycle) as well as years of reference (up to 2010).

Table 2/4 lists examples of emissions factors. Benzene emissions tend to decrease with rising vehicle cruising speeds (not driving speeds!). Remarkably, in the cases of NOx and particulates the emissions factor is roughly 10 times that for trucks as for cars.

Various calculation models are used for the evaluation of pollutant levels on roads (see Chapter 4.3). Usually these are the Gauss model, the Lagrange model, and the Box model, the last being used especially for street canyons.

Wind tunnel analyses also come into play for the simulation of the exhaust gas propagation on streets and for the quantification of the resulting immission levels (see Chapter 4.2).

Traffic situation

P.
Car
Km/h

Benzene
[g/km]

NOx
[g/km]

Soot (incl.
car tire abrasion)
[g/km]

Particel PM10
(only exhaust)
[g/km]
  

P.
Car

Lorry

P.
Car

Lorry

P.
Car
Lorry P. Car Lorry

AB_100_g

85,0 0,0021 0,0048 0,249 6,425 0,0084 0,0660 0,011 0,143

AB_120

120,0 0,0030 0,0050 0,372 6,325 0,0113 0,0607 0,018 0,129

AB_80

95,0 0,0023 0,0049 0,282 6,372 0,0095 0,0633 0,013 0,136

AO_1

76,7 0,0029 0,0046 0,243 5,970 0,0062 0,0629 0,007 0,135

AO_2

67,6 0,0029 0,0046 0,235 6,168 0,0066 0,0639 0,008 0,137

AO_3

60,6 0,0036 0,0055 0,256 6,552 0,0072 0,0690 0,009 0,150

IO_HVS1>50

58,4 0,0058 0,0057 0,243 5,933 0,0119 0,0896 0,010 0,144

IO_HVS2

46,2 0,0062 0,0083 0,241 7,204 0,0114 0,1100 0,009 0,195

IO_HVS3

39,1 0,0067 0,0097 0,252 7,901 0,0116 0,1212 0,009 0,223

IO_HVS4

32,0 0,0075 0,0134 0,263 9,485 0,0117 0,1501 0,010 0,295

IO_Kern

19,9 0,0093 0,0163 0,301 9,708 0,0129 0,1689 0,012 0,342

IO_Nebenstr_d

18,6 0,0113 0,0180 0,364 10,700 0,0138 0,1867 0,013 0,387

Tab. 2/4: Distance-related emissions factors per vehicle in the year 2005 (without cold engine starts); Source: UBA (2004)

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