Figure 1 - uploaded by Almut Jirku
Content may be subject to copyright.
Source publication
The shaping of the transitional zones between town and country is an area for landscape architecture which is gaining in importance. Three landscape competitions for such areas took place and have been partly implemented in the ‘Berliner Barnim’ on the north-eastern border of Berlin. Agricultural use will have to continue because otherwise the open...
Context in source publication
Context 1
... future of cultural landscapes is a hot topic at present. In particular, the peripheral areas are under a lot of pressure from urban, non-agricul- tural uses. These issues and the structural change in agriculture, which has been taking place at least since the 1950s, have been altering the face of the landscapes and continue to do so. The resulting scenery does not please everybody, often nobody likes it. There are problems with its acceptance because the expectations of traditional cultural landscapes are no longer met. Recently, a specific kind of agriculture has emerged that caters for the interests of city dwellers and is therefore called ‘urban agriculture’. It is mainly situated on the fringe of urban agglomerations. ‘Urban agriculture’ does not just mean agriculture near or within cities. It is a new approach which is not only oriented to production, but services too – things which city dwellers can do in their leisure time, e.g. fruit picking, arrang- ing flowers or riding ( Fleury and Donadieu 1997; Lohrberg 2000, 2004; BGMR 2004 ). This can help develop a more open-minded approach to the necessary changes in the perception of landscape and encourage an awareness of the importance of an economically viable agriculture. How to transform landscapes into new uses so that they may be profit- ably managed for farmers while maintaining an aspect which is pleasing to non-farmers is an important question. Since agriculture is heavily sub- sidised by the European Union, it has to offer the majority who support it indirectly something that they think is worth paying for. New approaches both from farmers and visitors to peripheral rural areas are necessary. The farmers need to broaden their outlook and take into consideration the needs of city dwellers. Visitors need to accept that the cultural landscape of the past cannot be maintained without very heavy subsidies and they must widen their imagination with regard to what is beautiful. The Barnim area on the north-eastern periphery of Berlin is given here as an example to illustrate these changes in attitude towards peripheral landscapes. Three consecutive competitions for landscape architects took place in the Barnim area with results beyond old and new design stereo- types – a new type of landscape came into being which is specific to the place and at the same time unconditionally modern. First, the historical decisions in planning and politics will be described which led to the planning opportunities of today. Then the wider context of the area in the actual Berlin–Brandenburg schemes will be explained. The questions that were raised in the preparation of the competition briefs will be discussed and the results of the competitions are described briefly. Their effect on future design processes is discussed with relevance to consideration of reactions from laymen and professionals. The most relevant entries of the three Barnim competitions are analysed. By refer- ring to contemporary theories in the arts, some general principles for future design in peripheries can be derived from these entries. The foundations for landscape architecture in the Barnim area in the north-east of Berlin were laid as early as the end of the nineteenth century. Although the Berlin city area was much smaller than it is today, it was recognized that open spaces in the catchment area of the growing city could be threatened. To safeguard the options for nearby recreation and sewage disposal, the city administration of Berlin bought woods and estates outside the city limits. The forests were given special protection and in this way they were secured until today. At this time the understanding grew that there is a connection between hygiene and epidemics. Reformists like the doctor Rudolf Virchow and the civil engineer James Hobrecht developed a new sewage canal system and pushed its realization through parliament. Open sewage disposal within the city was abolished. Sewage was now transported in canals to the outskirts where it was cleaned by seepage in so-called ‘Rieselfelder’. At first, these sewage fields were also used for agricultural purposes; however, later, this was no longer possible because of pollution, especially heavy metals, in the waste water. The fields were divided up by dams into rec- tangular polders, into which the sewage was directed in order to allow the water to seep away (Fig. 1). The cleaned water was then returned to the water system by means of artificial ditches. These sewage farms were gradually replaced by sewage processing plants. Some, however, survived until the 1970s, mainly in the eastern half of the city. In March 1933, Berlin possessed 25,000 ha of forest areas and 27,000 ha of country estates, within the city limits as well as outside. These pub- licly owned areas are a great asset even for regional planning today ( Ermer et al. 1996 ). Many of these sewage farms were located on the north-east of the city, on the Barnim plateau. Once their use as sewage farms ceased, the expanses were used by the agricultural production co-operatives of the GDR (Landwirtschaftliche Produktionsgenossenschaften – LPG) as extensive fields and meadows. The landscape was largely empty and unstructured, due to industrialized farming methods. Also the poor soils of the Mark Brandenburg make large continuous acres necessary because the yield per acre is low and the farms are few and far between (Fig. 2). Due to the political situation of West Berlin and rigorous state planning in East Berlin during the separation of Germany, Berlin differed from comparable western cities in that a suburbanization process hardly oc- curred at all. In the north-east, in particular, high-rise housing developments bordered directly on fields, and a clearly defined urban edge could be recognized. Some changes were inevitable here, but at the same time we should recognize the unique situation which is a result of the special history of Berlin. The close proximity of the city to open spaces is a unique poten- tial and the preservation of this condition was the goal of the regional park concept developed in 1996 ( MUNR 1998 ). The main idea is to dedicate eight areas, located between the development axis following the outgo- ing lines of the railways, to be regional parks. These areas are situated in a ring around the city of Berlin. Several parks start at the city border and a small section is situated in Berlin but predominantly the park territories lie in Brandenburg. The main goal for these regional parks is to develop a strong, specific identity to prevent them from being only buffer-spaces and easily built upon. Regional parks in Germany are not a legal category like national parks, but a voluntary union of local authorities. Therefore each park is organ- ized in a different way. The landscape character of the eight parks is rather diverse (Figure 3 shows the predominant character of each park). Several consist mainly of forests and lakes whose amenities are obvious. But there are also open agricultural landscapes which are more in need of improvement. This is especially true for the regional park Barnimer Feldmark. Barnim is the name of a plateau north of the Spree glacial valley. There are two regional parks within its territory, Barnim Nature Park and Regional Park Barnimer Feldmark, west and east of the development axis in the northern direction. Both regional parks have a small part of their territory in Berlin, the so-called ‘Berliner Barnim’. In the Barnim area, planning activities had begun even before the regional park concept was developed. This was necessary because neither the appearance nor the image was attractive. The area is dominated by monotonous farming, trees or forests are few and far between. Only a few beautiful spots exist, but most parts are in desperate need of enrichment. This region is still waiting for recognition of its specific attraction which lies mainly in its openness. Therefore, elements need to be inserted in a way that structures the area without destroying its character. The Barnimer Feldmark regional park is very suitable for bicycle tours because of its flatness. Also it is easily accessible by local trains. The Barn- imer Feldmark Society, a voluntary organization of local authorities and NGOs, developed a system of paths, of which there are four different kinds: from train station to train station, circuits, local walkways and bridle paths. Barriers such as motorway and railway rings are a problem with regard to their implementation because few possibilities to cross them have been found till now. From the very earliest zoning plan considerations after re-unification, the aim was to develop here a fourth large-scale recreational area for Berlin to supplement the forest and lake areas in the three other corners of the city.[1] This improvement of the north-eastern sector was particularly necessary because massive building activities took place here in the 1970s and 1980s in the GDR. The large prefabricated housing estates of Mar- zahn-Nord and Hohenschönhausen (Fig. 4) are in the immediate neighbourhood. After re-unification, building in the catchment area of the local railway lines continued, and new residential areas arose in the north (Karow- Nord, Buchholz and Buch). At the same time there were not nearly enough areas for recreation on a larger scale ...
Citations
... Intensywny rozwój Berlina w XIX w. spowodował, że dość wcześnie zaczęto formować w otoczeniu miasta tereny do wypoczynku mieszkańców, które jednocześnie miały pełnić funkcje prozdrowotne. W tym celu do początku XX w. władze miejskie zakupiły 14 obszarów położonych poza miastem o powierzchni 25 000 ha z przeznaczeniem na budowę polderów służących oczyszczaniu ścieków miejskich oraz zapewnieniu terenów rekreacyjnych dla mieszkańców (Jirku 2007). Były one zarządzane jako swoiste farmy gminne, aż do czasu ich prywatyzacji w ostatnich latach (Kühn, gailing 2008). ...
The problem of controlling the development has been a challenge for urban
planners for over 150 years, and one of the basic tools used for this purpose is a
planning instrument referred to as a green belt in English and zielony pierścień
(green ring) in Polish. This concept is based on the protection of open areas located
on the outskirts of cities against the urban sprawl. Thus, a green belt is a system of
undeveloped open spaces around the city, created in order to limit the process of
chaotic urbanization. Special planning arrangements are made for the green belt in
order to maintain “openness” and ensure the implementation of many functions
assumed by the planners. The popularity of the concept proves that it is one of the
most resonant urban concepts connected to urban development of municipal and
development of metropolitan areas. Green belts are used on all continents and
usually refer to metropolitan areas. This dissertation broadly presents the origins and evolution of the green belt
concept, but its primary focus lies on the characteristics of the structure and functions
of green belts both theoretically and practically. The monograph consists of
seven main chapters. The introductory chapters discuss methodological issues as
well as the origin and evolution of the green belt concept. In the following chapter
(3), 23 case studies from all over the world are presented in detail, taking into
account their structure, function and specific implementation. This approach made
it possible to determine characteristics of the green belt models used today, which
are examined in the next chapter discussing their structural features and the functions
they perform. The following chapter (5) includes comparative studies that
were carried out for 10 large European cities, where different models of green belts have already been implemented. The method selected for this purpose involved
mapping the potential of natural environment in the surroundings of cities, and
more precisely in densely built-up areas (in buffer zones with a radius of 20 km
around densely built-up areas). The analyses of potentials were then related to
functions specific to green belts and discussed in relation to the concept of ecosystem
services. Chapter 6 presents the application perspectives for the implementation
of the concept in Poland; analyses the potential for the implementation of
green belts functions in the nine largest Polish cities; and provides an overview of
the green belts proposals applied in the Polish planning documents, which,
however, have not yet gone beyond the concept stage. The analyses of green belts made it possible to formulate a number of conclusions
both summarizing the existing knowledge about the concept as well as concerning
new aspects resulting from the analyses of the potential of metropolitan areas.
These conclusions are not only academic, but also have a potential for application.
More than 150 years after the first green belt solutions were implemented, the
concept remains valid. Although some green belts or green wedges did not survive
the post-war urban sprawl, most of them have consolidated and become established
in planning systems of different countries. This statement confirms the main
hypothesis about the effectiveness of this planning instrument in limiting urban
sprawl. The idea of preserving open spaces around cities, especially larger ones, has
evolved considerably, adapting to changing conditions, i.e. mainly the pace of
urbanization, means of transport and other technological conditions, and above all
environmental changes. Moreover, new scientific approaches have also contributed
to its development, especially in the field of ecology and landscape ecology. The
concept has evolved significantly, both in terms of structure and function. The current planning solutions for the protection of open spaces around cities
are characterised by a very diverse spatial structure. They depend on physicogeographical
properties resulting from the location of the city or metropolis in
question, as well as their development conditions. Currently, six basic models for
the protection of open spaces around cities are in use: (1) a compact green belt
surrounding the city, (2) green wedges, (3) Urban Growth Boundary with an agricultural
conservation zone, (4) green belt of protected areas, (5) a green heart,
(6) green belt of ecological network (Fig. 4.4). As mentioned above, they all have
one supreme goal in common – to protect against uncontrolled development. Also,
they are all located outside of densely built-up areas in the suburban zone. The
review of the solutions made it possible to determine certain regularities with
regard to the existing green belt models. Case studies indicate that in order to
protect high-value agricultural land, solutions with tight boundaries are more often
used, whereas when recreational or ecological functions come to the foreground –
the applied solutions are usually much smaller in terms of space, but they emphasize the continuity of the system, i.e. green wedges, ecological networks, but
also a system of protected open areas.
The list of declared objectives created for various green belts indicates that the
main functions performed by them include: the structure-forming (structural)
function – conservation of open areas and at the same time restrictions on development,
the supporting function – conservation of agricultural and forest production
areas, the recreational function – preservation of recreational areas and the ecological
function – protection of high-value ecological areas (both in terms of habitat
for various species and landscape connectivity). The landscape function, i.e.
protection of landscape physiognomic values, is less frequently indicated as important,
and the environment-forming function is hardly mentioned. It seems that in
the context of contemporary environmental problems, especially those related to
climate change, as well as air pollution and water supply problems, the environmental
significance of green belts will grow. Another matter, which allows an optimistic view on the development of the
green belts concept, is its relation with the concept of green infrastructure, as well as
the growing importance of urban agriculture. The new perception of the role of green
belts can also be linked to the concept of ecosystem services, which reveals the current
benefits that the inhabitants of large cities derive from the existing green belts.
Analyses of possibilities to form green belts based on European and Polish
examples clearly indicate that there is space for their implementation, and in most
of the analysed case studies also the potential to perform all the key functions:
structure-forming (structural), supporting, recreational and ecological, and above
all, environment-forming.
The review of green belt implementations clearly indicates that in spaces as
ridden by conflict and collision as metropolitan areas, where the interests of city
dwellers and defenders of open spaces often clash, the social function has so far
been underestimated as the one that can make a difference. With insufficient
emphasis on those functions, which are desirable from the social perspective, the
negation of the development function is viewed as particularly negative, perceived
as a fundamental problem in the implementation of concepts. Arrangements which
are socially relevant have a much greater chance of universal acceptance and,
consequently, implementation of the instrument. Such a view fundamentally
increases the possibilities of implementing the concept also in Poland, recalling
Herbert Gans’s observation from 1969 that if people reject the ideas of planners, it
is rarely because they are stupid or bad, but often because they have different lifestyles
and goals . Hence, nowadays the inclusion of inhabitants in the planning
process is not only necessary at the local level, which is already quite common, but
also at the regional level, examples of which are presented in this paper. The main conclusions which could find application include the following:
There is no single one, but many models of green belts. There is no need for
a single model planning instrument for many cities – the concept of green
belts is very flexible and capacious, a green belt should be tailored to each
metropolitan area individually;
2. The structural model of green belts should be selected or developed according
to the configuration of each area, its environmental conditions, preferred
directions of development and the dynamics of demographic growth.
However, the share of open areas within them should not be less than 60%
of the area surrounding the city;
3. The catalogue of functions assigned to green belts needs to be adapted to
local conditions, taking into account the guiding principles concerning:
multifunctionality of protected areas, maximum protection of environmental
resources (which, apart from water, soil and air, includes undeveloped
space) and the role of social conditions in all dominant functions. And so:
• In areas where there is a clear need to protect good agricultural soils,
the supporting function should be complemented with a recreational
one, taking into account education and culture, e.g. by highlighting the
importance of traditional crops, involving metropolitan residents in
activities specific to urban agriculture, such as promoting allotment
gardens, linking food producers and consumers, introducing innovative
technologies in cultivation,
• In areas with predominant ecological functions, it is also necessary to
add recreational functions, especially those related to nature education
- such a solution is suggested by the concept of green infrastructure,
• In areas with predominant recreational functions, it is important to pay
attention to the widest possible access to open areas of the green belt, wedges or green heart for the residents, also in connection with public
transport. Open areas, such as forests or allotment gardens, should
fulfil a social function, which requires appropriate recreational infrastructure,
• Make society aware of the important environment-forming role - planning
documents should draw attention to the preservation and restoration
of environmental resources: water, adaptability to climate change,
but also protection against floods, carbon sequestration. Also, actively
promote these issues;
4. The following best practices should be applied to planning green belts:
• Indicate the limits of compact development (urban growth boundary)
and maintain an appropriate proportion of land reserved for building
purposes in the peri-urban zone – its shortage is one of the main
reasons for the collapse – of green belts,
Create a compensation system for landowners and involve them in the
decision-making process concerning the design of the green belt,
• (If possible, gradually) local or regional authorities, possibly even NGOs
should purchase land that is most valuable for the creation of green belts,
i.e. mainly natural and semi-natural areas, but also urban farms,
• Involve broad public in maintaining the green belts – support local and
regional NGOs working for the preservation of open spaces – This will
ensure a better understanding for top-down planning activities,
• Introduce a single institution to coordinate the management of areas
protected by the green belt to prevent institutional fragmentation and
to coordinate the activities of administrative units, especially as regards
local planning. However, this is not about absolute, top-down implementation
of the green belts, which has not worked in the hitherto
approaches, but rather about coordinating the maintenance of the
green belt,
• Introduce strict rules for the authorisation of development in areas
protected by the green belt. If necessary, these may be quite restrictive
(as in Portland), provided that it is economically or socially justifiable,
• Consider introducing a schedule for using up land reserved for building
purposes.
In terms of implementing the green belts concept in Poland, fears that the
implementation comes to late are to some extent justified, which is indicated by the
problems of urban sprawl and, as a result, a high degree of spatial chaos. This is
evidenced by the high share of fragmented development in the peri-urban zone.
However, it is still possible to take conservation or remedial measures, as indicated
by the analyses of the potential of green belts carried out for the functional urban
areas of the nine largest Polish cities.
This review of solutions from many parts of the world gives a practical lesson
in the principles of shaping green belts, indicating that in the age of Bauman’s liquid
modernity (2006), there are no ready-to-use models that, like components, could
be matched to different metropolitan areas. It is the decisions concerning the vision
for the development of the core city and satellite communes, related to the response
to the needs of the inhabitants, as well as the observation of environmental changes,
that can contribute to the shaping of the space around large cities in line with the
principles of sustainable development.
Studies presented in this dissertation were in part the results of research project
no. N 305-1752 40 financed by the NCN [National Science Centre] entitled “Spatial
and functional models of green belts in shaping metropolitan areas”. The materials
were also documented as part of the Fulbright Senior Award.