1.6.3 Selection of terrestrial and inshore marine sites
1.6.3.1 Stage 1 of the selection process
Following the adoption of the Habitats Directive in 1992, the
conservation agencies began to draw up a list of potential SACs. In
developing the process for selecting sites the agencies' initial
planning considerations were:
a. the timetable,
principles and criteria for site selection set out in the Directive
which should be followed, along with any interpretation developed
by the EC Habitats Committee (established under Article 20 of the
Directive);
b. selection should be
based upon current knowledge of the Annex I habitat types and Annex
II species, as the timetable did not allow for large amounts of
extra survey. Only where current knowledge was inadequate should
selection be delayed to await the results of additional
survey;
c. there should be a
consistent approach to selection, taking account of the
distribution, abundance and range of variation of habitat types and
species; and
d. social and economic
factors should not be taken into account8.
In order to ensure an effective UK approach to the selection of
SACs an inter-agency team of senior staff was established. This
team was chaired by the Chief Officer of the JNCC and co-ordinated
the interaction of the various specialists, provided quality
assurance and managed various working groups involved in the
process.
As a first stage of site selection seven specialist working groups
were established to provide advice relating to woodlands,
coastlands, marine habitats and species, freshwater habitats and
species, lowland habitats, upland/peatland habitats, and
terrestrial plant and animal species. These groups were
commissioned to produce initial ideas on high-quality sites for
each of the Annex I habitat types and Annex II species by
application of the criteria listed in Section 1.5.4.
The process of site selection involved repeated internal peer
review of the developing ideas and advice on high-quality sites.
Changes were made to the proposals for sites to take account of the
comments from internal peer review, new knowledge as it came to
light or was produced from new surveys, and the comments and
suggestions that arose from public consultation. A range of
professional groups and statutory committees have scrutinised and
critically reviewed the lists of sites in various iterations, as
follows:
a. specialist working
groups drew up the initial list of sites for evaluation and quality
assured subsequent changes to the list recommended by other
groups;
b. local staff of the
country agencies were required to ensure that sites selected were
the ones in their area of geographical responsibility that best
satisfied the selection criteria, particularly in terms of
representation and the conservation of habitat structure and
function;
c. the management boards or
project boards of the individual agencies have taken an overview of
the representation of sites in their country to ensure an evenness
of response and adequate representation of each habitat and
species;
d. the governing bodies of
the country agencies have approved the proposals within their
particular geographical areas of responsibility;
e. the Joint Nature
Conservation Committee has formally approved the proposals prior to
providing formal advice to Government;
f. Government departments
and administrations have scrutinised the site selection process and
the resulting list to satisfy themselves that agencies have acted
in accordance with the requirements of the Directive.
Once areas suitable for selection as SACs have been
formally advised to UK Government, they are known as draft SACs
(dSACs). Once formally approved by government as sites for public
consultation, they are known as possible SACs
(pSACs). In March 1995 the JNCC published, on behalf of
the UK Government, an initial list of 280 sites that had been
recommended as pSACs (JNCC 1995). Public consultation on this list
of pSACs was initiated in March 1995. For each site, owners and/or
occupiers were contacted by the conservation agencies and notified
of the location and boundaries of the site, the reasons for its
recommendation as a pSAC, and a summary of the Directive and its
implications. In general, consultees were given a period of six
weeks in which to respond; for marine sites the consultation period
was extended to 12 weeks.
At the same time, comments were also sought from a wide range of
organisations, including Government departments and agencies, local
planning authorities, NGOs, and industrial and/or commercial
bodies. As well as NGOs with a wide conservation remit, such as the
World Wide Fund for Nature (WWF), specialist societies were also
consulted. Many responses were received as a result of this
consultation exercise. These were assessed by the conservation
agencies, and, where appropriate, changes were made to the list of
possible sites. For example, several sites were added to the UK
list at this stage as a result of representations by NGOs, and in
some cases, lists of qualifying features and/or site boundaries
were amended on scientific grounds.
After 1995 further consultation with owner/occupiers was carried
out, as amendments to the UK site list were formally advised to
Government. A second major public consultation exercise commenced
at the start of October 1997. Once again comments were received
from a variety of organisations and considered by the conservation
agencies.
Once consultation was completed satisfactorily, sites were
submitted to the EC. At this stage, sites become known as candidate
SACs (cSACs). For each site, a Natura 2000 standard data form was
compiled from information supplied by the country agencies
(following the
guidance provided by the European Commission DGXI (1995)), and
a digital map showing the site boundaries was produced. These data
were submitted to the EC in both electronic format and hard copy.
The first tranche of 136 candidate SACs was sent to the EC in June
1995. Over the next four years, eleven further tranches of sites
were submitted, and by June 1999 a total list of 340 cSACs had been
submitted. This completed Stage 1 of the selection process. The 340
sites were intended to represent a complete national list (with the
exception of a small number of sites for which formal submission
had been delayed), and were considered to represent a proper
interpretation of the Directive's requirements. The rationale
behind the selection of sites at this time was explained by Brown
et al. (1997) and Hopkins (1995).
1.6.3.2 Stage 2 of the selection process
Within the Atlantic Biogeographical Region Stage 2 of the SAC
selection process ('moderation') was initiated at meetings held in
Kilkee and Paris in autumn 1999.
While the site lists from all Member States considered at the
meetings were found to be insufficient in some respects, the UK
list of 340 cSACs was judged to provide insufficient representation
of a relatively large number of features (37 habitats and 28
species). There was general agreement that the UK had approached
the selection of SACs in a logical and scientifically robust
manner, and had succeeded in identifying the best sites for each
interest feature. However, three key issues were raised in relation
to the UK site list:
a. The proposed sites
were judged to provide inadequate coverage of the geographical
range or ecological variation shown by some habitats and
species.
b. For some interest
features the proportion of the total national resource contained
within the SAC series was considered to be too low.
c. The UK had only listed
selected habitats and species (i.e. those considered to be of
outstanding European importance) as SAC interest features. The EC
requires every significant occurrence of an Annex I habitat or
Annex II species on each site to be treated as a qualifying
interest feature.
In response to the conclusions of the Paris and Kilkee meetings,
the UK Government asked the statutory conservation agencies to
undertake a thorough review of the list of candidate SACs. This
process was started in October 1999. This work involved listing
additional interest features on existing sites, and identifying new
sites.
During the moderation process, attention focused on enhancing the
site lists for those features which were judged to be
insufficiently represented in the UK list. The majority of new
sites were therefore selected primarily for these under-represented
interest features. In a few cases, new sites were also proposed for
habitats and species which were not found to be insufficient but
where additional high-quality examples were identified. High
priority was given to finding sites which would fill geographical
gaps in coverage. However, in a small number of cases no sites have
been proposed in certain parts of the UK, either because there are
no examples of sufficient size and/or quality, or because available
survey data are not sufficient to allow suitable sites to be
identified.
Effort was directed towards increasing the proportional
representation of those interest features for which less than 20%
of the national resource had been represented in the SAC series.
Where appropriate, the assessment criteria previously applied were
adjusted, for example to take account of the requirement to list
every Annex I and Annex II feature on each site. Where necessary,
existing site boundaries were amended to increase the
representation of the principal features.
Provisional site lists were sent to JNCC in January 2000. JNCC then
carried out a UK assessment of the proposals to check that a) a
consistent approach towards site selection had been adopted across
the UK, and b) the revised lists satisfactorily addressed the
issues raised at the Kilkee and Paris meetings. This stage of the
work relied heavily on input from inter-agency specialist working
groups. Following discussion and resolution of any outstanding
issues final amendments were made to the UK site list, and this was
formally advised to DETR and devolved administrations in April
2000. Various minor amendments were made subsequently to the site
list as additional information became available (e.g.
addition/deletion of interest features and changes to site
boundaries). Since October 2000, sites have been submitted or
re-submitted to the EC in a series of tranches following
consultation with site owner/occupiers and other interested
parties.
Although the UK site selection process for the terrestrial
environment and inshore marine waters is now largely complete, the
consultation process has yet to be completed satisfactorily for a
few new or amended sites, which have not been submitted to the EC.
Some additions and changes to the national list of sites may arise
as a result of further scientific work and public consultation. Any
such changes are unlikely to significantly alter the fundamental
composition of the SAC series.
The changes made to the UK site list during moderation are
summarised in Table 1.7, which shows the number and area of sites
in the SAC series, and the number of features represented.
Table 1.7 Comparison of pre-moderation site
list (June 1999) and post-moderation site
list (August 2008)
| |
England |
England & Scotland |
England & Wales |
Northern Ireland |
Scotland |
Wales |
UK
Offshore
Waters
|
UK Total |
| Number of sites, June 1999 |
141
|
3
|
4
|
21
|
131
|
40
|
0 |
340
|
| Number of sites, August 2008 |
231
|
3
|
7
|
54
|
236
|
85
|
5 |
616
|
| Total site area, June 1999 (ha) |
540 514
|
111 599
|
3 605
|
47 136
|
686 553
|
376 548
|
0 |
1 765 955
|
| Total site area, August 2008 (ha)9 |
846 231
|
112 478
|
95 072
|
66 614
|
921 222
|
590 871
|
268 409 |
2 900 898
|
| Number of interest features, June 1999 |
324
|
10
|
16
|
26
|
259
|
89
|
0 |
724
|
| Number of interest features, August 200810 |
767
|
21
|
48
|
157
|
864
|
357
|
5 |
2 219
|

Figure 1.4: Distribution of SACs, SCIs and
cSACs in the UK.
8 The Lappel Bank judgement
(ECJ C-44/96, 11 July 1996), established that selection of SPAs
should be based on scientific, rather than socio-economic,
criteria, and this policy has also been applied to SACs. It is
currently being challenged in the European Court of Justice (ECJ
C-371/98) in a case brought by First Corporate Shipping against the
UK Government.
9 All area figures are rounded
down to the nearest whole hectare.
10 Refers only to European
qualifying features (i.e. features with a global grade of A, B or
C).