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European Cooperation in the field of Scientific and Technical Research - COST Action C11 |
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The need for Greenstructure Planning in the UK © Anne R. Beer,
2000 The need for
Greenstructure Planning Greenspace in
too many urban areas tends to be almost bare of
vegetation, characterless and hardly used by local
people; designated at the time of original
development of the area of settlement as public
open space it was often only supplied as lip
service to the prevailing landuse planning
legislation (the open space standards of provision
which operated from the 1930s to 1980s). Such
spaces are not surprisingly seen by outsiders as
useless and, therefore, much of our greenspace is
constantly subject to threat from development
pressures. The present state of greenspace in many
urban areas is a sign of a lack of thought about
the importance of greenspace to the general quality
of life in cities (see Chapter 7-Environmental
Planning for Site Development- 2nd edition,
A.R.Beer & C.Higgins, Spons 2000). Perhaps as a
direct result of this there has been a lack of
public resources to care for such spaces - many
have severely degraded over the last two decades of
the twentieth century becoming almost
wastelands. A strategy
which aims to regenerate such spaces, with the aim
of using their full potential for enhancing local
biodiversity, as well as enhancing the quality of
local people's lives, can give local community
groups a focal point- so playing a major part in
enhancing the quality of life. Good quality
local greenspace enhances the quality of life and
the sustainability of the local land uses in many
ways (see Chapter 7 -Environmental Planning for
Site Development- 2nd edition, A.R.Beer &
C.Higgins, Spons 2000). For instance, through
increasing the range of local recreational
opportunity, which in turn reduces the need for car
usage in leisure-time. Good quality
greenspace also enhances the visual environment,
creates educational opportunities for children,
allows the development of efficient local water
management schemes and grows biomass for use
locally). It has even been seen to have a direct
economic impact through the way its presence can
influence the decision making of entrepreneurs
making decisions about where to local new and
expoanded enterprises. Greenstructure
Plans - City and Local I argue that
there is a need for Greenstructure Planning to be
added to the Town Planning process which operates
in the UK. Without proper emphasis given to a
city's greenstructure its greenspace can never play
the very significant role in helping enhance the
environmental sustainability of a city which a full
understanding of their capacities would
ensure. For instances:
Greenstructure
Planning needs to parallel Infrastucture Planning
and Land Use Planning in planning urban areas. To
be effective as an instrument to improve the
quality of life in a city and that city's level of
environmental sustainability Greenstructure
Planning needs to be of equal weight to all the
other aspects of that decision making process
commonly termed Town Planning. Without
Greenstructure Planning we in England are not going
to be in position to solve our present flood
problems. Vast acres of housing, industry and
commerce have been built on river floodplains just
because of the low level of priortity given to
greenstructure issues by the British Planning
process (the only exception was the New Towns of
the 1950s to 1970s all of which ahad "Landscape
Plans' which identified a coherenet greestructure
and used the local floodable land as part of that.
Greenspaces
are: By not
understanding the role of the greenspaces in a city
we have allowed such a sunstantial increase in the
area of sealed surface that surface water flow has
accrelerated and the rivers and streams cannot cope
let alone the "storm water" sewers which were all
that those planning the city had to allow for under
present regulations. Local
communities and greenstructure
planning Through
adopting Greenstructure Planning each city would
have a mechanism through which it could present its
goals for the local greenstructure. To be effective
this would need to be done in a manner which would
enable local communities to develop their own
Community Greenstructure and Local Environment
Plan. Local Greenstructure Plans should identifying
the qualities it would like its greenspaces to have
and the functions it would like each to fulfil -
such spaces will often be muli-functional that is
supporting biodiversity, aiding in storm water
control or water collection for irrigation, helping
clean particles out of the air (this has been seen
to be effective in Stuttgart for instance where the
wind flows through well vegetated valleys) as well
as providing an attractive setting for a specific
human activity - residential, industrial,
educational, commercial as well as
recreational. The existance
of a long term Local Greenstructure Plan presents
the possibility that a community could, through its
own efforts, work with a local authority as well as
appropriate experts to redesign its local
greenspaces. In this way greenspaces that are more
supportive of the whole range of the recreational
activities in which all age groups would like to
participate might result. Passive recreation, the
appreciation of just being in the 'outdoors' in
beautiful natural surroundings, should not be
forgotten in striving to increase the range of
activities supported by the local
greenspaces. Where, for
instance, there is a local lack of public
greenspace a Greenstructure Plan should help local
people identify the part that could be played by
other elements of the greenstructure. For
instance: Identifying the
existance of all the elements and "spaces" of a
local greenstructure and then working out possible
multi- functional uses for each space is one method
of arriving at a coherent greenstructure? The
greenstructure is composed of its existing and
potential greenspaces and the open land outside the
boundary of the built up area. Local
communities have an important role to play in
identifying the need for different types of play
and recreation and encouraging the regeneration of
any existing unimaginative and poorly planned
playspaces as well as creating new opportunities
for recreational activity. They also have a vital
role in preserving and enhancing biodiversity in a
locally appropriate manner. Rethinking
openspace, who plans it, designs it and who
maintains it and how this could be financed is
something that could encourage the direct
involvement of local groups. There is even the
possibility, if local financial arrangements can be
rethought, of developing schemes whereby local
people could be paid to be involved in caretaking
and maintaining their local greenspaces. In such
circumstances the local authority's role could
become that of providing the land and the
professional design and management skills while the
local people evolve their own sustainable approach
to local greenspace. Local
policies and their implementation Each area for
which a community level plan is developed is
inevitably different and, therefore, the policies
that you develop for your area should be unique to
it. The following are examples only of policies
relating to local water management, biodiversity
and greenspace; these are illustrated as they are
the range of policies most likely to involve local
community working in groups rather than as
individuals. They are not intended to be fully
inclusive of all the issues which will require
policies to be worked out by the local community,
they are just examples to get you started when
thinking how to solve your areas particular
environmental problems. Problems best solved by
individual or public/private agency initiatives are
not dealt with here, although they would of course
have to be addressed in finalising a Community
Environmental Plan. Policies
aiming to encourage sustainable local water
management Increase the
area of permeable surface. Wherever
possible impermeable surfacing (tarmac, paving and
buildings) should be altered into permeable
surfaces (gravel, turf and structurally reinforced
turf, 'grass-crete', treed and shrubbed areas
etc.). The surface cover types which could be
considered for change by a local community include:
driveways, entrance areas, public spaces,
courtyards, low capacity parking areas, some
industrial areas (although due to the need to
contain spillage of toxic material and liquids some
of these areas must remain impermeable), school
yards and sports pitches. Open some river
banks to re-create the old flood plains where
appropriate and develop new ponding areas along the
river to reduce down stream flooding. Implementing
such a policy would require liaison with the local
Water Board, industrialists and the local
authority. Promote
rainwater storage through improvement and creation
of retention ponds and surface drainage
systems. Parks, golf
courses, cemeteries, lawns, "dead" left over space,
school grounds and communal open space are all
suitable locations for retention ponds. Man made
water channels (shallow valley forms operating like
ditches) can be introduced or improved and extended
into a system which can channel water from the
gardens as well as any open land to the retention
ponds. Storage in ponds allows the eventual
development of valuable ecosystems and wildlife
habitats. Plants, fish and other aquatic organisms
can colonise; this helps to filter the water and
maintain the stability of the habitat. There is a
need to liaise with the Water Board and the Local
Authority. Two types of
retention ponds can be considered:
Permanent storage ponds, which are appropriate
where a continuous supply is available and where
inflow and outflow and soils permit a stable
condition.
Temporary storage ponds are only full during and
after storm events, and are allowed to dry out.
This type is less suitable for development in
recreation areas but the boggy land, which will
ensue is still a wildlife resource as it creates a
habitat too often eliminated from rural as well as
urban areas. Store and
use rainwater and grey water for household and
irrigation purposes. Individuals can
organise for rain water to simply be collected from
the roofs and other impermeable surfaces, and
stored on site in rain water storage tanks or
communally in larger pools. It is easier to do if a
whole community is involved in the purchase of the
necessary equipment and can share its plumbing
skills. This water can be used in vegetable growing
and general gardening, car washing and for any
other outdoor use. Such a system also helps
alleviate flash flooding except in times of the
heaviest rainfall. Grey-water too
can be collected for recycling, it contains soap
and dirt which can act as a mild fertiliser, so it
must be treated before use to avoid contamination.
This is easier to arrange in new build than in
existing housing areas. Improve
recreational access to water courses and local
reservoirs Many parts of
water courses are often inaccessible and hidden
away, and sometimes sections are culverted. The
full potential of the water courses needs to be
gradually realised through a series of local
environmental improvements. There is a need to
liaise with the Water Board and the Local
Authority. Policies
aiming to enhance biodiversity through the
management of local landuse Too often
current 'nature conservation' policies are
ineffective, they have not achieved even 'weak
sustainability' as far as bio-diversity is
concerned and loss of biodiversity continues. Even
in areas where the loss has not been catastrophic a
precautionary policy almost always has to be
recommended, whereby the concept of enhancing
bio-diversity through every landuse and land
management action is integrated into all areas of
development. Maximise
locally appropriate genetic
diversity Genetic
diversity is the sum of genetic information
contained in the genes of individuals of plants,
animals and micro-organisms. Within all urban areas
a major problem for biodiversity is that many of
the newly planted plants are cultivated; the plants
used are often clones and, therefore, genetic
copies of the 'parent' plant. To ensure genetic
diversity, native plants should be used wherever
appropriate in all urban greenspaces, if possible
they should be from seed grown stock, preferably
from local provenance (developing a local plant
nursery to supply the public greenspaces could be
part of a local job creation project for a local
community). Where possible, soil importation should
be avoided, and where improvement is required, this
should be carried out in the form of locally
collected organic composts. Educational material
should be developed within the larger community to
encourage any residents who are interested to do
the same in their gardens. Maximise
locally appropriate species
diversity Species
diversity relates to the number and diversity of
species regarded as populations, within such
populations gene flow occurs. In urban areas
species rich communities are generally taken to be
more 'stable' than those that are relatively
species poor. It is, therefore, desirable to
implement planting and management schemes that
promote species rich communities. For instance,
meadow grassland rather than mown turf and mixed
rather than single species hedgerows. Maximise
locally appropriate habitat
diversity Habitat
diversity is important, it relates to the variety
of habitats, biotic communities and ecological
processes in the biosphere as well as the diversity
within ecosystems. Diverse, naturalistic
communities of the type which can be found in urban
areas can withstand change and should be encouraged
to develop. It would make sense, therefore, to
target areas of low diversity within the case study
area such as the schools and playing fields and
some parkland as areas within which to encourage
the development of new naturalistic habitats
appropriate to the local conditions. Implementing
such a policy would reinforce the current planning
commitment to providing more nature like plant
communities in greenspaces. Adopting such
policies should do much to reverse the continual
erosion of bio-diversity which has occurred over
the past century within the urban area
particularly. The loss has been the result of a
combination of the following factors:
Conversion of land from natural/semi-natural
vegetation to agricultural or other uses
Pollution, pesticides or other chemical
contamination
Introduction of exotic species Local
communities gradually need to become aware of these
factors and to consider how to eliminate the worst
effects as it implements changes in land management
practices. Increase
biodiversity within private gardens and other
private land The
possibilities of enhancing local bio-diversity
through the way in which private gardens are
managed by their owners or tenants are substantial.
Success in doing this could make a real impact on
local bio-diversity. It would do much to compensate
for its loss in the more densely developed urban
areas (Beer, 1998). Increase
biodiversity in the wider urban
fabric There are many
small 'corners' within the built up parts of any
settlement which are in effect 'spaces left over
after planing' - spaces with no real function.
These spaces too often attract rubbish and litter
and are an on-going cost to the community to
maintain; transforming them through community
environmental 'actions' into small scale 'nature
reserves' is one way to cope with them - and it can
have the advantage of enhancing bio-diversity as
well as eliminating an eye-sore. Policies
aiming to enhance the sustainability of
greenspace Greenspace -
the unifying element Greenspace can
act as the unifying theme for a Community
Environmental Plan. All unbuilt land within the
urban boundary is part of the urban green even when
it is privately owned. Locally appropriate policies
are needed for changing what the greenspace looks
like, how it is used as well as how it acts to
support urban biodiversity. For greenspace
to fulfil its full potential in relation to
Community Environmental Planning it is important to
develop policies relating to: the
availability of greenspace and openspace within
400m of every home for use by, in particular the
elderly, disabled, young children and young
adults. adequate
footpaths and cycle routes and links between
greenspaces. These can be provided in the form of
green corridors with associated refuges for
wildlife within the urban area. Safe usable paths
with plenty of seating throughout the study area's
greenspaces are needed but, in particular, where
people have to go up and down hills on their way to
their homes, the shops, schools and
workplace. the
recreational uses reflecting the local 'carrying
capacity' of that greenspace and its habitats. For
example, an area with a fragile habitat or
supporting relatively rare wildlife should not be
design so as to encourage boisterous
activities. the
creation of rich and ecologically varied local
environments designed to maximise the generally
desired feeling among urban dwellers of wanting
some contact with nature. In areas where people's
interest in specific activities rather than nature
are to predominate skilled designers will need to
be used to meet people's requirements.
stimulating local interest in greenspace by using
them for educational purposes and encouraging
community involvement
See also Sheffield case Study
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Meetings Background Meetings Background Meetings Background |
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©ARB 18 Nov 2000