On the basis of the responsible party
principle anchored in federal pollution protection law, the
individual emitting facility is the focus of measures for air
pollution control, the most significant element of which is the
pollution permitting process.
In relation to the permissible level of
pollution in the area affected by a facility seeking a permit,
the "Technical Guideline for Air Pollution Control" (the
first general administrative specification under federal
pollution control law, also known as "TA Luft") makes
concrete requirements for consideration of the surrounding area,
but from an urban development perspective does not distinguish
between levels of required protection for areas affected by
pollutant immissions. In contrast to noise protection practices,
the immission (threshold) values in TA Luft are thus equally
valid for all types of construction sites in accordance with §
1 (2) BauNVO.
The compatibility of an emitting facility with
its surrounding area results solely from the validity of the
permitting process under building law, in accordance with the
Federal Building Use Ordinance (BauNVO) and the corresponding
regulations of the site plan.
An area’s level of justified protection is
measured by what is allowable in that area under planning law.
To that extent, the existing classification of types of
construction sites in §§ 2 to 10 of the BauNVO also contain a
progressive ranking of immissions controls corresponding to the
respective land use of a site. This relates to the sensitivity
of the allowable land uses to both emissions and immissions.
According to § 15 (3) BauNVO, the
permissibility of facilities in construction sites should be
evaluated on more than just the process guidelines of the
Federal Pollution Control Law (BImSchG) and the ordinances
developed from it. Rather, it is noted that facilities requiring
a permit under pollution control law can also be located outside
of industrial areas, depending on the individual case. The
typical view assumes that § 4 of the BImSchG allows
permit-requiring facilities (typically manufacturing or other
productive enterprises) without restriction only in industrial
areas, whereas commercial areas and mixed-use areas are to be
reserved for facilities not requiring permits.
Of particular note is the option foreseen
under § 1 (4) BauNVO of dividing a construction site according
to the types of permissible uses as well as the type of
enterprises and facilities and their particular requirements and
characteristics. This option of division can be employed to
prevent the locating of air-polluting enterprises in special
locations (e.g. in air exchange corridors or transient areas to
other uses important for the urban climate), even in an
industrial area. This corresponds to recognized principles of
urban planning that fundamentally forbid the creation of new
problem situations in the planning of new development.
The protection of a construction site is given by the
actual planning law. So §§ 2 till 10 BauNVO with the different
kinds of construction sites defines also the hierarchy to
protect against pollutants.
Immissions Climatology
In permitting processes
for larger emitting facilities as well as in connection with
prescribed accident analyses, immissions prognoses obtained by
means of dispersal calculations or experimental simulations are
highly important (cf. Chapter 4).
Fundamentally speaking,
industrial and commercial areas should be located downwind from
developments, with sufficient areas of green space in between.
The main direction of wind indicates the compass direction from
which the strongest and most frequent winds emanate on average.
In southwestern Germany this is typically west through southwest.
Thus it is in the easterly or northeasterly direction from a
pollutant source that the highest concentrations of pollutants
under free dispersal conditions are found. Under much less
frequent low-exchange weather conditions the highest levels of
pollutant concentration arise in the presence of weak or no
winds (east through southeast wind directions). Average annual
dispersal calculations therefore show a maximum level of
proximate immissions primarily northwesterly from a pollutant
emitter. The old rule of urban development concerning the main
wind direction thus – with the noted restriction – remains
valid.