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6.1.2 Benchmarks
for Describing "Green" Uses
A quantification
of the climatic effects of green areas in urban planning has
already been made – as far as possible on the basis of secure
knowledge – in
Chapter 2. This will also play a role in the following
recommendations for planning.
Various attempts have been made along the lines of green
planning to quantitatively describe the vegetation potential of
a land area. In this process, the non-uniformity of conceivable
vegetation forms (e.g. grass, forest, potato fields, cornfields)
must be considered from a climatic perspective (Figure 6/1b).
In addition, it
must be remembered that a living plant continuously changes: It
germinates, grows, has rest and vegetation periods, loses its
leaves or keeps them for many years, ages, and finally dies (GROSSMAN,
1989).
Various models assume that the ratio of vegetation to surface
area of a property should be expressed through a standard
defined "plant-quantity number." In this context the
"green volume number (GVZ)" and the "surface
function number (BFZ)" were introduced by POHL et al.
(1984).
The example of the
"phyto measurement number (PMZ)" according to SCHERER
(1973) (see GROSSMAN, 1989) allows the principle of the
plant-quantity calculation (phyto measures) to be read in the
form of a defined hierarchy (Table 6/1).
| Open
ground |
0,5 |
| Lawn |
1,0 |
| Meadow |
1,5 |
| Shrub
to 1 m height |
2,0 |
| Small
wood to 1 m height |
3,0 |
| Hedge
to 2 m height |
4,0 |
| Needle
wood to 3 m height |
4,5 |
| Leaves
wood to 3 m height |
5,0 |
| Needle
wood 3 m to 5 m height |
6,0 |
| Leaves
wood 3 m to 5 m height |
7,0 |
| Coniferous trees
to 10 m height |
8,0 |
| Deciduous trees
to 10 m height |
9,0 |
| Coniferous trees
over 10 m height |
11,0 |
| Deciduous trees
over 10 m height |
14,0 |
Table 6/1: Phytomass
numbers for various forms of vegetation
The allocation of "phyto
measures" per square meter of undeveloped property area to
the specified vegetation forms should concurrently describe
their efficiency relative to various bio-ecologic components,
including dust filtration effect, evaporation, wind protection,
and shade provision.
From an urban climatic
perspective it should be noted that no absolute measurement
value can be conceived. The various specified properties cannot
be considered valid when detached from a concrete local
situation and a specific problem definition. For example, grass
areas (with a PMZ of only 0.5) that cool off strongly during the
night exhibit a significantly large local climatic use as
components of cold-air production areas (cf.
Chapter 6.2.1). On the contrary, the forest
(which itself should be protected), being a hindrance to airflow,
has the disadvantageous property of restricting ventilation.
This "disadvantage" however, is exactly the factor
that produces the dust filtration effect of the forest. In the
case of a lee-producing planting (cf. Chapter
3.4.2) or in the example of a "corked
obstacle" as in Figure
6/12,
the attainment of both desired and unintentional effects points
out the difficult handling of overall climatic pros and cons.
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