| CAWDOR WOOD |
(site map at base of page) |
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Total site
surface area (ha)
: 159.4 ha
Status: Candidate Special Area of Conservation
Other protection
status : The site is also a Site of Special Scientific Interest Scientific
description of site
: Importance
of the site for the conservation of the species/habitat types targeted
at regional, national and EU level : Threats: Threat 1:
Lack of management planning and background information It is vital that works
undertaken within the project are understood in the context of long term
conservation management and set within a formal management plan.
Lack of data on conservation features and new constraints to
management need to be considered and addressed.
As habitat management progresses towards favourable condition,
management needs to become more refined and consider more levels of
information, e.g. on different groups of species. Location A
management plan is required for the whole site and survey work into the
extent and management needs of the following elements within the pSCI is
required: Impact on habitat Threat 3:
Displacement of understorey and groundflora by Rhododendron Rhododendron Rhododendron
ponticum is an exotic ornamental evergreen shrub which has become
established Cawdor woods pSCI. The plant spreads by seed and
subsequently by vegetative layering and will coppice from cut stumps.
Once established it can spread rapidly forming a dense canopy in
the understorey shading out native shrubs, groundflora and tree
regeneration. Location Impact on habitat Threat 4:
Displacement of native species by exotic broadleaved trees Exotic broadleaved tree
species such as sycamore, Acer
pseudoplatanus and beech Fagus
sylvatica have invaded many native woodlands or been planted for
amenity (or occasionally for timber) in the past.
Both species are shade bearing and compete well, displacing
native trees and shading out groundflora and understorey species. Threat 6:
Overgrazing by deer
Overgrazing by roe deer
is a dominant threat. High
deer numbers reduce understorey development, prevent regeneration and
reduce the diversity of native tree populations.
It can also have a detrimental effect on the groundflora
communities and damage existing trees through bark stripping and damage.
Native deer species are however a natural component of woodlands and at
low levels (4-6
deer/100ha), deer browsing can play a part in habitat diversification
and maintenance. Threat 7:
Displacement or restriction of native woodland by planted exotic
coniferous woodland There remains a legacy
of previous forest policies which encouraged conifer plantations within
native woodland sites throughout the UK.
This ‘enrichment’ planting created dense plantations which
displace native trees, shade out native flora, alter soil conditions and
restrict woodland expansion. Conifer underplanting or planting on native
woodland sites contributes to the loss and fragmentation of woodland
habitat. Threat 11:
Lack of regeneration of native trees In a few cases, even
where measures such as thinning, protection from grazing and ground
preparation have been undertaken, the immediate regeneration of native
species can be limited losing the opportunity for regeneration. This may be because there is a limited seed source or
infrequent seeding by certain species or perhaps due to climatic
conditions. In some cases
direct intervention by planting or protecting young seedlings is
warranted. Natural regeneration is likely to be slow in the area of
exotics surrounded by the site which are being removed. Location Impact on Habitat Threat 17:
Lack of public awareness The native woodland
habitat is threatened by a general lack of recognition of its
conservation value and by the public’s limited understanding of what
positive management can entail. This
impacts on the level of financial and community support for conservation
works. Other cultural
features of the site attract many visitors who will be interested or
concerned over works in the woodland area. Formal footpath access
requires upgrading and interpretation provided.
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