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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)
|