1.6.5 UK SACs and the Natura 2000 network
1.6.5.1 Overview of the UK SAC series
Summary data on the UK SAC series are given in Table 1.8. Figure
1.4 shows the distribution of SACs in the UK.
Table 1.8 Area of
SACs (including, for the purposes of
this table, SACs, SCIs and cSACs) in each
part of the UK, and actual and percentage land area within the SAC
series, with a comparison for SPAs, and the total area of Natura
2000 sites in the UK (May 2006).
|
|
England
|
England &
Scotland
|
England &
Wales
|
Northern
Ireland
|
Scotland
|
Wales
|
UK Total
|
| Total national land area (km2) (incl. inland
water)11 |
130 410
|
n/a
|
n/a
|
14 144
|
78 789
|
20 758
|
244 101
|
| Total area of UK territorial waters
(km2)12 |
-
|
n/a
|
n/a
|
-
|
-
|
-
|
161 200
|
| Number of SACs |
230
|
3
|
7
|
53
|
236
|
85
|
614
|
| Total SAC area (km2)13 |
8 459
|
1 125
|
951
|
663
|
9 212
|
5 899
|
26 308
|
| SAC land area (km2)14 |
7 363
|
482
|
542
|
559
|
6 257
|
1 436
|
16 639
|
| % SAC cover of total land area |
5.65%
|
-
|
-
|
3.95%
|
7.94%
|
6.92%
|
6.82%
|
| Total area of SACs in territorial waters
(km2)15 |
1 096
|
643
|
408
|
104
|
2 956
|
4 463
|
9 670
|
| % SAC cover of UK territorial waters |
-
|
-
|
-
|
-
|
-
|
-
|
6.00%
|
| Number of SPAs |
78
|
1
|
2
|
14
|
140
|
17
|
253
|
| Total SPA area (km2) (classified/designated
SPAs only) |
6 711
|
436
|
377
|
1 082
|
6 002
|
1 230
|
15 839
|
| Total area contained within Natura 2000 sites
(km2)16 |
-
|
-
|
-
|
-
|
-
|
-
|
30 042
|
| Total land area contained within Natura 2000 sites
(km2) |
-
|
-
|
-
|
-
|
-
|
-
|
20 971
|
| Total % Natura 2000 land cover |
-
|
-
|
-
|
-
|
-
|
-
|
8.59%
|
Sites are distributed throughout the UK (see Figure 1.4).
Concentrations of sites in certain parts of the UK (e.g. Scottish
Highlands, north-west England, north Wales) reflect the presence of
more extensive areas of semi-natural habitat and associated species
in these regions. Individual sites vary considerably in size. The
most extensive localities (e.g. The Wash and North Norfolk Coast,
Caithness and Sutherland Peatlands) exceed 100,000 ha, while the
smallest are less than one hectare.
There is considerable variation in the number of sites selected for
each Annex I habitat and Annex II species. For very rare features
with a restricted distribution (e.g. 1903 Fen orchid
Liparis loeselii, 6520 Mountain hay
meadows, and 4020 Temperate Atlantic wet heaths
with Erica ciliaris and Erica tetralix),
the selection of only a small number of localities has been
sufficient to include a high proportion of the total UK resource
within the SAC series. For habitats and species with a wider
distribution in the UK, a larger number of sites have been selected
to ensure adequate representation in terms of geographical
coverage, ecological variation and the proportion of the national
resource within the site network. The number of sites selected has
also generally been greater for priority features (e.g.
7110 Active raised bogs), those for which the UK
has particular responsibilities (e.g. 7130 Blanket
bogs), and habitats which show a wide range of ecological
variation (e.g. 4030 European dry heaths).
1.6.5.2 Favourable conservation status - the relationship
between SACs and the wider environment
For Annex I habitats and Annex II species with a very restricted
distribution, all or almost all examples are included within the
SAC series, and site-based measures (as described in Article 6 of
the Directive) are therefore likely to be sufficient to achieve
favourable conservation status. However, most habitats and species
are more widely distributed, and only a proportion of the total
national and Community resource will be protected within SACs.
Examples of such habitats and species in the UK include
4030 European dry heaths, 1166 Great
crested newt Triturus cristatus and 1355
Otter Lutra lutra. For these interest features,
maintaining or achieving favourable conservation status will
require a complementary mix of site-based conservation measures and
actions to be taken outside the SAC network.
The importance of wildlife conservation outside designated sites is
recognised in the Directive, e.g. in the measures required to
protect species listed on Annexes IV and V (Articles 12 16).
Article 10 acknowledges that the series of Natura 2000 sites should
function as an ecologically coherent network, and stresses the
importance of managing landscape features, such as river banks,
hedgerows and ponds, to facilitate species migration and dispersal,
and generally to provide an ecological infrastructure which
supports the protected sites network. In March 2002, the European
Commission's Environment Committee reaffirmed the role of
protection of species protected under the Birds and Habitats
Directives outside of Nature 2000 sites in biodiversity
conservation.
Complementary site-based and wider environment measures are
fundamental to the successful implementation of the UK Biodiversity Action Plan (UK
BAP), and are likely to become increasingly important if the
predicted impacts of climate change are realised. Mechanisms for
protecting and enhancing Annex I habitats and Annex II species
across the UK include national Habitat and Species Action
Plans, local biodiversity action plans, agri-environment
schemes, river basin management plans developed under Directive
2000/60/EC of the European Parliament and of the Council of 23
October 2000 establishing a framework for Community action in the
field of water policy (the 'Water Framework Directive'),
forestry practice guidance, and planning policies.
In order to report on the conservation status of Annex I habitats
and Annex II species (as required by Article 17 of the Directive)
it will be necessary to develop monitoring and surveillance
schemes. On SACs, this will be achieved through the Common
Standards Monitoring programme (JNCC
1998). In the wider environment, some Annex II species are
already monitored effectively, but suitable surveillance schemes
for other species (e.g. most fish species) have yet to be
developed. Work is ongoing to develop surveillance strategies for
Annex I habitats; this is likely to be linked to the reporting
requirements of priority habitats under the UK BAP. The Marine monitoring handbook (Davies
et al. 2001) addresses the principles behind, and the
procedures for, monitoring Annex I habitats, and selected Annex II
species, within marine SACs in British waters to assess their
condition in accordance with the relevant requirements of the
Directive and the UK's common standards for site monitoring.
11
Source: Whitaker's almanac
12 Source: JNCC Offshore Natura
2000 Project.
13 All area figures are rounded
down to the nearest whole km2.
14This is calculated as the total
SAC area, less the area classed by the country agencies on the
Natura data forms as being in the NUTS Marine region, rather than
any other administrative area. However, some inshore waters,
particularly within estuaries, are not always classed as Marine on
the forms. Consequently the land area within the SAC series is
overestimated to some extent.
15This is the SAC area classed by
the country agencies on the Natura data forms as being in the NUTS
Marine region. However, some coastal waters, particularly within
estuaries, are not always classed as Marine on the forms.
Consequently the marine area within the SAC series is
underestimated to some extent.
16 SACs and SPAs in some cases
overlap or coincide; this figure gives the area of the combined
Natura site series without double-counting such 'double-badged'
sites. This can be calculated only for designated SACs, SCIs
and submitted candidate SACs and classified SPAs, by using GIS
intersection.