The Schorfheide-Chorin Project
In the years 1994 to 1999 the German Federal Ministry of Education,
Science, Research and Technology (BMBF) and the German Foundation for
the Environment (Deutsche Bundesstiftung Umwelt, Osnabrück = DBU)
financed an extensive, multidisciplinary research and
developmental project, entitled: “Implementation of nature conservation
objectives in an agricultural landscape, exemplified by the Biosphere
Reserve Schorfheide-Chorin” (in the following abbr. “Schorfheide-Chorin
Project”). The intention of this project was to develop theoretical and
practical methodologies and models how to integrate nature conservation
targets into the ordinary management of farming. This includes the
conventional conservation and restoration of natural or semi-natural
habitat patches within agricultural landscapes. But the project
additionally focussed on the definition and implementation of
conservation targets on the arable fields itself and the functional
interactions of the structural elements of a typical eastern German
cultural landscape. The project was conducted by the administration of
the Schorfheide-Chorin Biosphere Reserve, which co-operated with
22 research institutes and 41 co-operating farms, and with the regional
administration for agriculture. The reference region had a total size
of 16.000 ha out of which a study site of about 2.000 ha was analysed
in detail.
The project consisted of two building blocks of roughly the same size:
(a) a research block and (b) a practical block. Thus, the project
deliberately brought together scientists, practioners of nature
conservation and agriculture, and administrators within a
multidisciplinary approach. Both blocks were conducted in parallel,
forcing the interaction between science and practise. It was aimed,
that the practical part – out of its own necessities – will ask the
“right” questions to the scientists and vice versa, in an interactive
process, the scientists influence the way of practical and
technological thinking. The project worked in parallel on different
space levels. It was one of the main challenges of the project to link
these space levels in a sound way, contributing by this to one of the
main problems of landscape ecology and planning.
We chaired the scientific block over a couple of years, were
responsible for the cooperation between both blocks and – in a separate
part project – worked on conservation assessment schemes for
agricultural landscapes and the definition of conservation quality
targets. For the first task we combined assessment approaches, like the
American Habitat Evaluation procedure, the German “Nutzwertanalyse”,
and other schemes for specific parts of nature to a comprehensive,
logically sound procedure for an overall evaluation of agricultural
landscapes. Basic tool are relations which convert scientific data into
“nature values”.
Agricultural landscapes are exposed to continuous changes as result of
natural features and the actual requirements of humans. While the
methods for the conservation of natural areas are rather simple (namely
to protect untouched nature and leave it to its own mechanisms) the
definition of nature conservation goals in cultural landscapes is much
more complicated: (1) human influence is more or less omnipresent, (2)
it is up to our decision which variant of future development we chose
and the options are often very different from each other. Therefore,
nature conservation in agricultural landscape needs “landscape visions”
which are specified models on a desired future “optimal” state. If such
visions are only roughly described they cannot guide the “actor” in the
landscape (e.g. farmer) in his daily work and daily decision-making. It
is therefore necessary to specify the “vision” by well defined target,
called here “conservation quality targets”. Those targets are
quantified by “standards”. Such a method proved to be practicable and
successful in many fields of environmental protection (e.g. related to
noise, air pollution etc.). However, all such specifications result not
automatically from scientific data. They are the result of normative
conventions. The Schorfheide-Chorin Project offered a unique chance to
bring together scientists, practical persons and administrators from
very different fields who together should guarantee for balanced
definitions.
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Effects of agricultural activities on different
levels of space
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Quality standards can be defined either in relation
to measures or to ecological effects
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| Indicator |
Further specification
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| Size |
Area in ha
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| Age |
Continuity in history in time and space
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| Connectivity |
Distance to objects of the same type
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General structure of vetation
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Sociological status of vegetation
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| Completeness |
Share of (a) characteristic plant species and (b) characteristic
animal species out of regional lists
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Indicators for disturbances
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Number and abundance of non-characteristic species (e.g. indicators
for nutrient supply)
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Habitat spectrum
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Share of habitats out of a list of "characteristical habitats" for
this biotope
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Indicators for the object value of nutrient-poor dry grassland on
sand in northern Brandenburg
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Generally suitable habitat for the partridge Perdix perdix (left)
in a landscape compartment and significance of single agricultural lots
for the survival of the local population (right) according to
experts´assessment. Especially red and orange lots should be used and
managed in a way which respects the requirement of the species
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