NATURA 2000 SITES
46. It now seems to be generally accepted that the
list of candidate Natura 2000 sites submitted by the Government
in June 1999 was inadequate. The Atlantic meetings of the Biogeographical
Region in Kilkee and Paris presided over a 'moderation' process
which decreed that several Member States (including the UK) had
failed to put forward an adequate number of candidate Natura 2000
sites. The list put forward was insufficient for a number of reasons.
The Worldwide Fund for Nature told us that:
"First of all, we did
not think there were enough sites on the list to ensure favourable
conservation status for habitats and species on the directive,
and secondly that there was not sufficient geographical representation
of sites all over the UK to make sure that the biological variation
would be represented. It was no surprise to us that at the Atlantic
meeting the UK was found insufficient for I think 39 habitats
on the directive, that is half of those occurring in the UK, and
14 species, that is 73 per cent of the total occurring in the
UK."[110]
In addition to the two reasons detailed above, the
Department of the Environment, Transport and the Regions officials
noted that there also needed to be greater recognition of the
importance of 'subsidiary' species or habitats within sites.[111]
47. Since the Atlantic meetings, the UK has been
in the process of developing a fuller list. Although many witnesses
reiterated their disappointment with the original list, they did
also suggest that they were now broadly happy with the approach
adopted to selecting sites and emphasised that there was real
commitment on behalf of the statutory agencies to this process.
For example, the Worldwide Fund for Nature told us that they were
"impressed" with the Government's approach to this problem
and the "very rigorous process" which was being undertaken
to address the inadequacies of the original list.[112]
48. In August 2000, the Government put forward a
new list of UK sites for consultation which contained 576 sites,
a substantial expansion from the original 340 proposed. The European
Commission have informed seven Member States (including the UK)
that failure to submit an adequate list of sites could result
in the loss of regional aid.[113]
The UK now has a "period of grace" to resolve this matter.
As a general point, we regret that the European Commission appear
to have made no policy link between designating sites and costing
the protection of such sites: it is inevitable that any designations
made without the resources to back them up will merely be empty
gestures.
BUFFER ZONES
49. Inevitably, there are differences in the way
that the various Member States choose to implement the requirements
of the Directive. This is most apparent in the selection of Natura
2000 sites where some of the southern European Member States (such
as Greece and Italy) have designated large areas as sites, within
which so-called 'buffer zones' surround the core area. The aim
of buffer zones is to bring land around core sites under sympathetic
land-management practices. In the UK, smaller sites have been
selected which consist solely of the core area. The Worldwide
Fund for Nature told us of the pros and cons of the two different
approaches:
"The positive side of
including those buffer zones is that it gives you a lot more flexibility
to restore and recreate and try and make these areas bigger. Particularly
in coastal and marine areas that is very important where you have
other processes going on and maybe have some loss due to sea level
rise or coastal squeeze; you can actually accommodate that because
you have larger boundaries. The down side, and this is where I
do have some sympathy with the approach the UK has taken, is that
you have really quite draconian requirements under Article 6 of
the Directive which are quite difficult to apply if you applied
them to areas which have no existing nature conservation value."[114]
Despite their sympathy with the Government's approach,
the Worldwide Fund for Nature recommended that the UK should designate
some buffer zones. Similarly, the Woodland Trust lamented the
lack of buffer zones: "It means that designation is doing
nothing to actually address the threats external to the sites,
it is not actually promoting positive management of surrounding
land, and it probably limits us as a country in our ability to
gain EU LIFE funding..."[115]
The designation of buffer zones would also fit with the Biosphere
Reserves model (outlined to us by the Environment Agency) in which
a core area is defined (of sufficient size to meet long-term conservation
objectives), with a buffer zone (in which only activities compatible
with the conservation objectives are permitted) and an outer transition
area (in which only sustainable resource management is permitted).[116]
Representatives of farmers and landowners did not favour the use
of buffer zones but did not put major arguments against their
use. [117]
50. It is transparently the case that wildlife within
a protected site does not necessarily confine itself to the site:
for this reason, it is argued, sympathetic management of a much
larger area is important if we are to genuinely protect the wildlife
in the site. Certainly, with current agricultural policy and practices,
we believe that the value of sites could be compromised by the
inappropriate management of adjacent and nearby land. However,
the merits of buffer zones and their appropriate size will vary
dramatically according to the species which is being conserved
and the type of habitat: there is no simple answer as to whether
a large designated area with no buffer zone is better than a smaller
area with a buffer zones. We recommend that the Government
look again at the potential of establishing buffer zones around
Natura 2000 sites. Where a site itself cannot be enlarged, or
it would be a poor use of resources, buffer zones could be an
effective method of offering limited protection to a larger area.
However, the most practical method of improving the prospects
for biodiversity in areas around Natura 2000 sites remains reform
of the agricultural support system.
72 Ev p2, p8, p24, p26, p61 (HC441-II) Back
73
Ev p8 (HC441-II) Back
74
Ev p13 (HC441-II) Back
75
Q543 Back
76
Q33 Back
77
Ev p19, p42 (HC441-II); Q547 Back
78
Ev p2 (HC441-II) Back
79
Ev p62 (HC441-II) Back
80
Ev p42 and p19 (HC441-II) Back
81
Q593 Back
82
Q508; Back
83
Ev p2, p19, p42, p80 (HC441-II); Q594; Q504; Q190;Q138; Q33 Back
84
Ev p74 (HC441-II) Back
85
Q138 Back
86
Ev p62 (HC441-II) Back
87
Q594 Back
88
Q595 Back
89
QQ602-603 and Q506 Back
90
Q745 Back
91
Ev p19, p72 (HC441-II) Back
92
Q596 Back
93
Q599 Back
94
Ev p62 (HC441-II) Back
95
Q643 Back
96
Q472 Back
97
Ev p81, p93, p111 (HC441-II); Q472 Back
98
Q140 Back
99
Q523 Back
100
Q267 Back
101
Ev p1, p74 (HC441-II); Q635 and Q583 Back
102
Ev p45 (HC441-II) Back
103
Q64 Back
104
Q435 Back
105
Ev p37 (HC441-II) Back
106
Website of Ministry of Agriculture, Fisheries and Food Back
107
Q112 Back
108
Q584 Back
109
Ev p3 (HC441-II) Back
110
Q191 Back
111
Q105 Back
112
Q191 Back
113
Q104 Back
114
Q192 Back
115
Q224 Back
116
Appendix to Environment Agency Memorandum (Ev not printed) Back
117
Q300 Back