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2.9 Pollutant
Levels and Threshold Values
The wide array of
substances in the urban atmosphere – some studies of the air
in cities have identified more than 1,000 different substances
– does not allow all components to be regularly monitored. The
resulting vapor bell above the city – characterized in its
extreme form as smog – does not only afflict humans, it also
reduces the general brightness, the amount of solar radiation
received, and the duration of sunshine.
Inversion weather
conditions strongly enrich the urban air with pollutants. Figure
2/20 shows a model of the dependence of pollutant
concentrations on the altitude of the inversion boundary based
on a 1985 winter emissions situation in Stuttgart. The higher
the altitude of this lower inversion boundary is, the greater is
the volume of the mixed air above the city. In addition, the
concentrations of various pollutants depend upon the altitude of
the typical source. Although traffic-produced carbon monoxide
(CO) decreases as the lower boundary of an inversion rises, the
sulfur dioxide (SO2) concentration rises, since
higher sources now reach the mixed air and long-distance
transport of pollutants now becomes perceptible.
Since the middle of the
1960s pollutants in Baden-Württemberg have been analyzed
regularly. Although reductions in the levels of sulfur dioxide
and particulate matter are recognizable, levels of the pollutant
nitrogen dioxide (NO2) have increased further. This
is due primarily to continuously increasing traffic. In cities
above all, the threshold values of the TA Luft publication
(1986) are in part exceeded in street canyons (BAUMUELLER,
REUTER, 1993).
The immission threshold
values IW1 (for long-term effects) and IW2 (for short-term
effects) outlined in the TA Luft serve for the air-hygienic
evaluation of developments that require permitting. As such,
establishing that a development meets the TA Luft values is
necessary for the development to be approved. In this process,
the arithmetic average of the immission values (labeled as
I1Value) is compared with the long-term value IW1. In contrast,
the short-term value IW2 refers to 98% of the cumulative
frequency distribution. The TA Luft values are not a legal
planning instrument; they define rather the legal concept of
"damaging environmental effect." The TA Luft values
IW1 and IW2 are only valid in connection with the respective
processes set forth in the TA Luft for reporting on immissions.
These refer to individual test surfaces typically 1 kilometer
square inside the area affected by the development in question.
Admittedly, as the only existing official threshold values, the
TA Luft values are often carried over to other evaluation
scenarios.
The 22nd
BImSchV’s limit values for nitrogen dioxide and partikulate matter (PM10) have attained
particular importance, as these require measurements taken
directly on and near roads. Heavily-trafficked city streets
frequently exceed these threshold values.
The World Health
Organization has developed health-related indicator values (WHO,
2006).
The definition of
"maximum immissions values" (MI values) (VDI
Regulation 2310) from the VDI commission "Air Quality
Maintenance" aims at avoiding damage, whether short- or
long-term, to the health of humans, especially children, the
elderly, and the sick, and further aims at protecting animals,
plants, and goods from harm. The concept of "health"
also includes the well being of a human, to which one’s
biological and material environment contributes. The MI values
are concerned with purely effect-related, scientifically
established values guided by practical experience and with a
medical or natural science indication. The values do not take
into account technical practicability. For
the evaluation of comprehensive air pollution levels it further
makes sense to introduce an air pollution index (API), which
takes into account multiple air pollutants (BAUMUELLER, REUTER,
1995; MAYER
et al., 2002).
Table 2/5: Threshold and guideline
values in µg/m3
| I1: |
arithmetical
annual mean value |
|
I2: |
98- Percentil during 1 year |
|
a |
depending from the PM value |
|
b |
depending from location; I2-values
as a 14 days mean |
|
c |
18 exceedings are allowed in the year |
|
d |
only for 2 successive values |
|
e |
on successive days |
|
f |
10 - min. mean value |
|
g |
PM10 depending on location;
I2-values as 14 days mean |
|
h |
partly transition period,
partly alert values |
|
i |
allowed 35 excceedings per year |
|
k |
180: limit value to inform the population
240: imit value to warn the population |
|
l |
allowed 24 excceedings per year |
|
m |
allowed 3 excceedings per year |
|
n |
fine particulate |
| o |
allowed 25 days
excceedings per year
|
|