5.1.2    Assessing certain types of operation

a.   Plans and projects

In addition to relevant authorities’ functions in managing activities through the management scheme, they and other competent authorities have certain specific statutory functions to decide on applications for consents, authorisations, licences and permissions. These are “plans or projects” (p/ps) under the Habitats Directive. At present, only certain types of operations affecting marine and coastal areas (e.g. planning applications, discharge consents, transport and works orders) are specifically defined as p/ps in the UK Habitats Regulations. However, guidance from the European Commission [101] makes it clear that the ‘Habitats’ Directive indicates a broad interpretation should be taken to ‘plan’ and ‘project. Further UK Regulations are to be enacted to apply the Directive’s requirements about p/ps to other types of operation, but at time of writing it is not known to which types of operation the new Regulations will apply.

The 1994 Habitats Regulations set out the procedure that must be followed for the consideration of a p/p. This is summarised in Figure 17. , which is taken from Planning Guidance issued by the former Welsh Office (Planning Guidance (Wales) Technical Advice Note (TAN) 5: Nature Conservation and Planning. Welsh Office, November 1996). In essence, the process is as follows: For any proposed p/p, the competent authority should make an initial consideration, in consultation with CCW, to establish whether or not it is likely to have a significant effect. They may proceed where it is not likely to have such an effect. If a significant effect is likely, either alone or in combination with other p/ps, an appropriate assessment must be undertaken to establish whether the p/p will have an adverse effect on the integrity of the site. If the assessment reveals that it will not have an adverse effect, the p/p may proceed.

Although the process outlined in Figure 17. is applied specifically to the consideration of proposed developments by planning authorities, similar steps are applied by the Regulations to any type of p/p. A p/p for which consent has been given but which has not yet been implemented, must be reviewed as soon as practicable by the competent authority, under a similar process to that set out in Figure 17.

The decision about whether or not to give consent to a p/p affecting an SAC is made by the competent authority which would normally be responsible for authorising it. This authority should seek the advice of CCW who will, on request, advise on the significance of any activity or p/p which has the potential to affect the Bottlenose dolphins.

A fuller account of the procedure relating to PPs is contained in:

  • Planning Guidance (Wales) Technical Advice Note (TAN) 5: Nature Conservation and Planning (Welsh Office, November 1996);
  • European marine sites in England & Wales (Welsh Office and DETR, June 1998);
  • The Birds and Habitats Directives: Outline Government Position (DETR, May 1998);
  • Managing Natura 2000 sites: The provisions of Article 6 of the ‘Habitats’ Directive 92/43/EEC. (European Commission April 2000).

Figure 17. Consideration of development proposals affecting SACs

Figure 17.   Consideration of development proposals affecting SPAs and SACs.

b.   Environmental Impact Assessment

Box 3.

Environmental Impact Assessment

It is important not to confuse an “appropriate assessment” of a plan or project in an SAC with an “Environmental Impact Assessment” (EIA). Under EIA legislation, which is separate to the Habitats Directive, certain types of development (e.g. planning consents, highway construction, afforestation) must undergo an assessment of their environmental effects. These requirements [102] apply irrespective of whether there is an SAC involved, and would normally address a wider range of nature conservation and environmental aspects than the features of an SAC. Where an SAC is likely to be affected by a development requiring an EIA, it will be taken into account as part of the EIA, and the EIA may itself be used to fulfil the requirement for an appropriate assessment.

It is not practical to identify in this management plan the types of operation likely to affect the bottlenose dolphin population or its habitat which would be subject to EIA. It is considered sufficient to identify which should be considered as plans or projects under the Habitats Directive and hence which may require appropriate assessment. In each case, the competent authority responsible for considering a proposed operation must ensure that it complies with both sets of requirements. Some types of operation will require appropriate assessment but not EIA, and vice versa.