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2.8.1 The
Road as Pollutant Source
The growth in
individual motorized traffic (IMT) – which can be expected to
continue increasing in the future with the common market of the
European Community and the opening of the borders to the East
– places new demands on transportation policy. In many places,
people today already speak of a collapse in traffic conditions
on the roads, particularly in built-up areas. This increase in
traffic is connected with a substantial burden on the
environment, especially through noise (STAEDTEBAULICHE
LAERMFIBEL, 1994, 2001, 2007) and air pollution. With this in mind,
discussion about the "traffic of tomorrow" has
recently been strengthened.
The introduction
of pollutants into the atmosphere is not, however, only
important on the local and regional levels. Owing to new
realizations about the air chemistry in the stratosphere and the
effect of greenhouse gases on the world climate, this aspect has
attained a fully new, global dimension (see also Chapter
2.12).
The automobile dominates person and cargo
traffic in the Federal Republic of Germany. As such, in 2002 about
78% of the 917 billion total person-kilometers were driven
with passenger cars, and nearly 70% of the 509 billion total
ton-kilometers were driven with trucks.
Figure 2/15
shows the proportion of pollutant emissions attributed to road
traffic in the Federal Republic of Germany in reference to the
year 2002. The amount of pollutants produced by traffic was 37%
of carbon monoxide (CO), 42% of nitrogen oxide (as NO2),
11% of NMVOC, and 18,5% of the greenhouse gas carbon
dioxide (CO2).
In November 1990
the 35th Conference of Environmental Ministers
decided upon the following reduction goals for traffic emissions
in the former West Germany (Table 2/2).
Important consequences have the pollutants
coming from traffic in connection with a new guideline of the EU
because all limit values there are valid in all EU countries. When the declared
limit values are reached there must be to install a air
pollution abatement plans and it is allowed to reduce traffic to
reduce air pollution too.
| . |
NOx |
HC |
CO2 |
| till
1998 |
-
30% (- 22%) |
-
50% (- 48%) |
-
5% (+ 15%) |
| till
2005 |
-
60% (- 43%) |
-
70% (- 69%) |
-
10% (+ 18%) |
Table 2/2: Reduction
goals for traffic emissions in the former Federal Republic of
Germany (reference year 1987). Resolution of the 35th
Conference of Environmental Ministers; values in parentheses:
technical reductions achievable in the EC (reference year 1987;
optimistic assumptions)
The limit values are listed in the 22rd
order to the Federal Emission Protection Law (2007). In a lot of
street canyons in german cities the limit values for NO2
and PM10 are exceeded und this will be true also in the year
2010.
For planning and zoning, this has the consequence that the
future planning of streets must not only study the effects of
noise (STAEDTEBAULICHE LAERMFIBEL, 1994) but also must
scrutinize and take into consideration the effects of pollutant
gases.
The immissions situation
of a location is formed partially by local emissions and their
source altitude (very close to the ground for auto traffic), but
also by local propagation conditions, in which wind and vertical
temperature distribution play an important role (see Chapter
2.7). Figure 2/16 shows the air hygiene situation in the
region of Stuttgart in the presence of low wind velocity and an
inversion hindering the vertical air exchange with higher air
layers.
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