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Cemeteries and Churchyards
Habitat Audit - page 3
Page 1 Page 2
Nature
Conservation Importance, Threats
and Opportunities, Data Sources,
Rationale and
Limitations of Approach
Cemeteries and churchyards make a significant contribution to
the provision of urban green space in London, sometimes providing
a sanctuary for wildlife in urban areas devoid of greenspace.
Although many have restricted access they still provide a useful
resource for the local community, particularly within inner London
Boroughs.
A wide variety of habitats can be found in Greater Londons cemeteries.
This is demonstrated by St Pancras and Islington Cemetery in Barnet,
which supports areas of neutral grassland, wetland, scrub and
secondary woodland. Due to the antiquity of many churchyards and
cemeteries they can support habitats which are relics of former
countryside and may, therefore, support a range of rare or uncommon
plant species. The only known London site for green-winged orchid
Orchis morio, for example, is Morden Cemetery in
Merton. Other more commonly occurring plants, which are indicative
of the countryside within which many of these cemeteries were
formerly located, include cuckoo-flower Cardamine pratense,
harebell Campanula rotundifolia and crested dogs-tail
Cynosorus cristatus.
The older cemeteries, in common with mature suburban gardens,
often support animal species that are essentially species of open
woodland or woodland edge. These include spotted flycatcher, song
thrush, tawny owl and stag beetle. Holly blue, gatekeeper and
speckled wood butterflies often occur, as well as most of the
commoner species that occur in our parks and gardens.
Apart from a few unusually large sites, churchyards tend to have
a more limited diversity of habitats Ö mature trees and small
areas of grassland (occasionally quite species rich) being the
main features of interest. Yew Taxus baccata and ivy Hedera
helix are frequent components of the churchyard flora.
In addition, churchyard walls, monuments and gravestones may support
unusual plant communities with species such as harts-tongue fern
Phyllitis scolopendrium, wall rue Asplenium ruta-muralis,
pellitory-of-the-wall Parietaria judaica and various
lichens and other lower plants. The church buildings themselves
may also be of special nature conservation interest if they contain
bat roosts.
Isolated cemeteries and churchyards can provide sheltered habitat
in spring and autumn for migrant birds, providing an important
link in the network of open space that provides these species
with temporary refugia. Within central London, churchyards are
often among the few areas of greenspace where the local community
is able to have some contact with the natural world.
Some cemeteries and churchyards of nature conservation
value in Greater London
Highgate Cemetery, Camden
St Marys Churchyard, Sutton
Kensal Green Cemetery, Hammersmith & Fulham
Abney Park Cemetery, Hackney
Tower Hamlets Cemetery, Tower Hamlets
Harefield Churchyard, Hillingdon
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Threats
While churchyard/cemetery status confers protection from certain
forms of development, loss of existing habitat may occur as a
result of increasing pressure for burial space. Twenty one of
the thirty eight cemeteries with recognised nature conservation
value in London have been identified as sites for potential re-use
(Bailey 1998). The notable nature conservation value of these
sites is often due to their antiquity and the current laws preventing
the disturbance of human remains. Re-use could result in the loss
of the tree and scrub cover that has developed over many of these
older cemetery sites.
The responsibility for management of many cemetery sites has
been given to various local authority departments who are often
ill-equipped to advise on ecological management, or are reluctant
to accept nature conservation value. In an attempt to avoid affronting
the perceived sensitivities of relatives of the interred, most
land management in operational cemeteries is aimed at maintaining
a well-ordered, tidy appearance which limits the opportunities
for biodiversity conservation and enhancement.
Opportunities
In London, there is considerable potential for increasing
the nature conservation value of many of the extensive cemetery
sites. Simple measures such as a reduction in mowing frequency
where the sward is species-rich, or tree and shrub planting where
existing habitat is of low value would do much to increase their
ecological value. Placing bird and bat boxes in sites with trees
would provide a very public indication of support for biodiversity
conservation. The growing interest in green burials may also
create an opportunity to incorporate enhancement or creation of
wildlife habitat within existing or newly created cemeteries.
By recognising the existing and potential value of cemeteries
and churchyards these sites can provide an educational resource
which encompasses biodiversity, history and other disciplines.
For example, the relic flora of the site, in addition to dates
on headstones, can provide evidence as to the history of the site.
Lichens on walls and monuments can be related to air quality.
Although perceived as a threat to existing habitats within cemeteries,
re-use could provide an opportunity to create new habitats or
restore open habitats which have been lost to scrub or secondary
woodland. Indeed a London Planning Advisory Committee report,
Burial Space Needs in London, specifically refers to
the need to conserve biodiversity within any re-use strategy.
Sites such Tower Hamlets, Abney Park and Highgate Cemeteries demonstrate
the potential for incorporating biodiversity objectives into the
management of cemeteries and churchyards.
Bailey, R. (1998). Re-Use
of Graves Threatens Londons Valuable Wildlife Sites.
MSc Project, University College London.
The Confederation of Burial Services and The Institute of
Burial and Cremation Administration, Inc.
Halcrow Fox (1997). Burial Space Needs in London. LPAC.
London Ecology Unit Handbooks nos.: 5, 7, 9-13,15-21, 24-28.
London Ecology Unit Schedules: Bexley, City of Westminster,
Enfield, Kensington & Chelsea, Southwark and Wandsworth.
Mellor, H. (1981). London Cemeteries. Avebury.
Data on the distribution and extent of cemeteries came from the
London Advisory Planning Committees (LPAC) Report Burial Space
Needs In London (1997). The report contains the most comprehensive
audit of Londons cemeteries to date, although not all cemeteries
responded to the survey. A full audit of churchyards was not possible
as the data is not yet available. The figures provided in this
preliminary audit represent the churchyard resource with the
Sites of Importance for Nature Conservation identified by the
London Ecology Unit (LEU). This is not a definitive representation
of Greater Londons churchyard resource.
The list includes churchyards of nature conservation importance
for most boroughs (those with LEU handbooks/schedules). The data
for these sites was collected from a database at the Unit and
checked against each borough handbook and schedule. No churchyards
are listed for boroughs that are not members of the London Ecology
Committee: City of London, Havering, Bromley and Hackney.
Although lists of churches with churchyards are available for
approximately half of London there are no available data on the
size of these churchyards. There are six Church of England Diocese
which cover the Greater London area: London, Rochester, Southwark,
Guildford, Chelmsford and St Albans (Table 2). Available lists
provide the names of churches without giving their exact locations.
The Diocesan handbooks could be used to identify each church and
would need to be purchased at a cost of £3-5. The Dioceses of
Chelmsford and Southwark do not have a list of churches with churchyards.
The Diocesan handbook could be used to contact each parish individually.
Roman Catholic churches in Greater London fall under two Archdiocese
(Westminster, Southwark) and a smaller Diocese (Brentford). The
structure of the Methodist church in London is based on the boundaries
of Greater London with four divisions forming the four quarters
of the city; NW, NE and so on. No preliminary research has been
carried out for other denominations. However, in context of ecclesiastical
land use history these will, perhaps, represent a small resource
proportion of the Church of England, Roman Catholic, and Methodist
churchyard resource.
Page 1,
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