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Abstract from BTO Research Report No 194:
Gough, S.J. & Fuller, R.J. (1998)
Scrub management for conservation in lowland England: practices,
problems and possibilities.
Executive summary
1. Scrub creates particular problems in managing habitats for conservation.
At many sites it is seen as an invasive threat to existing open
habitats of high conservation value, yet scrub mosaics can support
rich communities of animals, especially insects and birds. This
report assesses the extent to which scrub is actively managed as
a habitat in its own right (‘active management’), outlines
the management practices that are most commonly adopted, discusses
the problems of achieving sustainable scrub management and makes
recommendations about work that is needed to better understand the
conservation value of scrub.
2. Eleven nature reserves were visited to help gain an appreciation
of current scrub management practices. Additional information was
provided by the National Trust concerning scrub management for conservation
on their properties.
3. It is concluded that there is considerable interest in managing
scrub habitats for conservation and on eight of the 11 sites visited
large-scale maintenance of scrub habitats is a major element of
the management objectives. Active scrub management for conservation
reasons is also undertaken on many National Trust properties. Much
of this management appears to be aimed at creating and maintaining
a variety of scrub growth stages; insects and birds are the most
frequently cited ‘target groups’.
4. Active scrub management is predominantly undertaken by rotational
cutting. The principal exception is Gorse management for which burning
as well as cutting is used. We are only aware of grazing being used
to maintain grass-scrub mosaics on a handful of sites. Grazing is,
however, widely used to prevent scrub growth in open habitats.
5. A fundamental problem in seeking to conduct sustainable scrub
management is that the characteristic mosaic structures that form
when scrub invades grassland are extremely difficult to maintain
or re-create. Rotational cutting is likely to turn the vegetation
into relatively uniform coppice-like structures that lack the fine-scale
mosaics of grass and scrub. Grazing may offer more possibilities
for maintaining such mosaics but there is little available information
on appropriate practices.
6. A new classification of scrub types is needed: the National
Vegetation Classification does not describe the range of variation
in British scrub adequately.
7. It is suggested that a comprehensive review be undertaken to
identify more exactly the conservation value of different types
and structures of scrub and the circumstances under which scrub
should be tolerated or encouraged to expand. The findings of such
a review could feed into the development of local and national policies
for scrub conservation.
8. There is a need to learn more about successional changes in
animal communities that occur as scrub invades grassland and to
compare these changes with those that occur under rotational cutting.
For birds this work should examine both breeding and wintering bird
communities, including requirements for roosting. Experimental work
on scrub management and responses of insects and birds is highly
desirable. In particular it is suggested that (a) experimental grazing
regimes are established on a small number of sites to assess the
feasibility of sustaining grass-scrub mosaics, (b) comparisons are
undertaken of short and long-rotation cutting to assess whether
the former has potential for maintaining mosaics.
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