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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.

 
 
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