It has not proved possible
to assess the extent of Londons urban wasteland resource.
Urban wastelands were severely under-sampled in the London
Wildlife Habitat Survey 1984/85 and more recent assessments
of urban wasteland, derelict land and brownfield land, undertaken
by other agencies, have used various incompatible definitions.
Whatever the true extent of
Londons urban wasteland resource in the mid-1980s,
there is no doubt that there has been a substantial reduction
in its extent within the last decade. Londons former
docklands contained a significant proportion of the capitals
urban wastelands, but most of this area has been redeveloped
to accommodate Londons burgeoning service sector industries.
Other large areas have been lost in more recent years to
provide land for new housing. Despite
the losses to some of the most extensive areas of urban
wasteland in London, new sites, albeit smaller and more
widely dispersed, are constantly being created as a result
of abandonment · a feature of the development cycle in a
major conurbation.
As a whole, urban wastelands
may be one of the most diverse of Londons habitats.
They encompass a wide range of sites with varying substrates,
topographies and other factors that determine the distribution
of plant and animal species. The variation in other habitat
types such as grassland and heathland may be rather subtle,
as a result of minor changes in soil chemistry and hydrology,
for example. However, the variation amongst urban wasteland
communities can be quite striking, because of the different
substrates and the source of primary colonisation. Some
of the most important attributes of urban wasteland habitats
are essentially ephemeral. Micro-topographical features
and microclimatic effects are rapidly created as land is
disturbed or surrenders to natural processes after abandonment.
However, they are rapidly destroyed when land is recycled
for new development or natural succession leads to eventual
dominance by secondary woodland or Buddleia scrub.
A common feature of many urban
wastelands is the dominance of species that are considered
to be weedy, ruderal or pioneer species. These
species are best able to colonise disturbed or hostile environments,
but often succumb to competition once conditions ameliorate
or stabilise. For this reason many of the species that flourish
in urban wastelands are exotics which would normally be
out-competed by native species, or are species which have
exacting climatic or biological requirements that are rarely
available except in the unusual conditions which arise on
urban wastelands.
The importance of urban wastelands for invertebrates is
becoming increasingly apparent. The
bird most often cited as a wasteland species - the black
redstart · does indeed occur on urban wasteland sites, but
can be found in less derelict areas where the characteristics
of the habitat are very diffuse.
The single most prominent
threat to urban wastelands is redevelopment. All urban wastelands
are previously developed land, or land which has had an
industrial use (usually the disposal of waste material).
As such, urban wastelands are usually subject to redevelopment
or decontamination proposals. Redevelopment of land or the
restoration of contaminated land frequently results in the
almost total loss of species present on the site, as there
is often a requirement for the complete removal or capping
of the existing surface material and vegetation. Although
this will result in local extinctions of some species, many
other species will maintain local populations if there are
adjacent wasteland habitats or incipient wasteland habitats
(newly cleared or abandoned sites) nearby. However, in modern
day London the loss of urban wastelands far outstrips the
creation of new ones. The debate concerning the environmental
benefits and losses attributable to redevelopment or restoration
of urban wastelands cuts to the quick of the sustainability
debate in London.
The lack of awareness of the
nature conservation value of urban wastelands is a secondary,
but related, threat. Many sites are comprehensively redeveloped
simply because there is no consideration of the biodiversity
value of urban wastelands, whereas a development which may
impact upon a seemingly more natural habitat
is more likely to be conditioned to ensure appropriate protection
or mitigation. Similarly, many good wasteland sites are
subject to programmes of enhancement to improve
their nature conservation value without first appreciating
or ascertaining existing value. Often the only enhancement
required is improvements to interpretation and public access.
Few urban wasteland sites
have been protected as nature reserves, and fewer still
managed to maintain their urban wasteland character, with
the exception of a handful of sites such as Wandle Meadow
Nature Park in Merton and the extension to Gillespie Park
in Islington. The establishment and management of urban
wasteland nature reserves presents a major opportunity for
awareness-raising and advancing the cause of biodiversity
conservation in urban areas.
Most urban wasteland flora
and fauna will still need to secure opportunities outside
protected sites. Indeed the very processes that produce
diversity in urban wasteland wildlife are dependent upon
a turnover of sites or other disturbance factors. The advent
of green buildings and other initiatives to
green the city are efforts to reinstate the processes which
give rise to urban wastelands. Rooftop urban wastelands
could help offset habitats currently being lost to built
development.
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