Home button, access key h Intro button, access key i Our wildlife audit, access key o Taking action, access key t News + events, access key n Partnership business, access key b
Site map, access key s Library, access key l Glossary, access key g Partners and links, access key p Contact us, access key c
Our wildlife audit
Download the complete
London Biodiversity
Audit
(4.1MB)

Habitat audits
Habitat Audits intro
Woodland
Open Landscapes with
Ancient/Old Trees

Acid Grassland
Chalk Grassland
Grassland, Meadows
and Pasture
Heathland
Grazing Marsh and
Floodplain Grassland
Marshland
Reedbed
The Tidal Thames
Canals
Ponds, Lakes and
Reservoirs

Churchyards and
Cemeteries

Railway Linesides
Farmland
Rivers and Streams

Habitat statements
Habitat Statements intro
Private Gardens
Parks, Amenity Grasslands
and City Squares

Urban Wastelands
Hedgerows
 
Urban wastelands
habitat statement

DOWNLOAD THE FULL AUDIT: in pdf or text format

For the purposes of this statement, urban wastelands are defined as those sites that support semi-natural vegetation that has developed over an imported or artificial substrate, subsequent to previous development or disturbance. Such sites include disused railway sidings, demolition sites, redundant industrial land and derelict land. It is noted that Urban Wastelands are not synonymous with 'brownfield land', which includes a much wider range of 'previously developed' land and can encompass sites which are now essentially semi-natural woodland, grassland or other habitats covered in the Audit.

It has not proved possible to assess the extent of London's 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 London's 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. London's former docklands contained a significant proportion of the capital's urban wastelands, but most of this area has been redeveloped to accommodate London's 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 London's 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.



This is only a summary - download the full audit in pdf or text format

Related documents:
None


Back to top of page