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4 Development Control in European Sites

13.160 Development in European sites – for example SACs and SPAs notified under the European Habitats and Wild Birds Directives – is subject to more stringent restrictions than those applicable in SIs.

Many activities that in practice have the potential to adversely impact on wildlife habitats do not require planning consent – most agricultural and forestry operations are, as we have seen, not considered ‘development’ for the purposes of planning control.315 These are subject to bespoke restrictions and statutory consultation requirements set out in the Conservation of Habitats and Species Regulations 2010, which are considered above.316

13.161 Where, however, an operation in a European site involves ‘development’ that requires planning permission,317 then the 2010 regulations apply more stringent planning rules that restrict the public bodies’ ability to grant planning permission more extensively than is the case in other protected areas (such as, for example, in an SI). The terms and conditions upon which the decision maker must proceed are the same as those applicable to non-planning matters (above) and replicate the same protective provisions in the Directive. They are integrated into the more complex decision making apparatus of the Town and Country Planning legislation in the manner set out below. The combined effect of Part IV of the Conservation Regulations 2010, and governmental guidance to local authorities and other decision makers,318 is to raise a stronger presumption against development of land in European sites than applies in other protected areas. Permitted development rights are also subject to extensive restrictions in European Sites. The special planning provisions apply to development in SACs and SPAs, and to development in potential SPAs (‘pSPA’) and candidate SACs (‘cSAC’) as if they had already been classified or designated.319

13.162 The discussion that follows will concentrate on the implementation of the Directive through planning law and development control.

It should be appreciated, however, that the controls required by the Directive apply to all ‘plans and projects’ requiring consent, and that their potential scope is somewhat wider than planning decisions – the controls discussed below can apply to a range of administrative consents required for various operations, other than the grant of planning permission,320 if they have significant impacts on protected habitats eg the grant of licences by public bodies to kill wildlife species that are considered pests.321

(a)Environmental Assessment

13.163 If the planning authority considers that a plan or project is likely to have a ‘significant’ effect on a European site, they must consult Natural England and carry out an ‘appropriate assessment’ of the project’s implications for the site in view of it’s conservation objectives. They can only agree to the development after having ascertained that it will not adversely affect the integrity of the European site.322 The assessment required by the Conservation Regulations 2010 should not be confused with the project-based environmental impact assessment (‘EIA’) required under the Town and Country Planning (Environmental Impact Assessment) Regulations 2011.323 The ‘appropriate assessment’ under the 2010 regulations is more narrowly focussed to an assessment of the impacts of development on the conservation status of the habitat and species, for the protection of which the site has been designated. A full EIA will look at a wider range of potential environmental impacts flowing from the development.324 Where a full EIA is also required, information gathered for the purposes of the latter can also be used for the purposes of the appropriate assessment required by the Habitats Directive.

13.164 The local planning authority’s power to grant planning permission is further restricted in that the regulations put a positive onus on the authority to satisfy itself that the proposal will not adversely affect the site’s conservation features.

If there is any uncertainty as to its effects the application must be notified to the secretary of state. This will give him the opportunity to consider whether to call in the application. If the secretary of state calls in the application and subsequently grants permission he must secure the necessary compensatory measures required by the Conservation Regulations 2010. Planning guidance indicates that he will expect to see, and be satisfied by, evidence that necessary compensatory measures will be secured when applications are referred to him by planning authorities proposing to grant planning permission in European sites.325

13.165 The requirements outlined above for the scrutiny of planning applications in European protected sites are also applied to require the review of existing permissions and consents granted before a site was designated a European site.326 The decision maker – for example the local planning authority – must review existing permissions and consents on the same terms as apply to applications for planning permission for new development in the site (above), and carry out an appropriate assessment of their impact on the site’s integrity. If their exercise is likely to cause significant disturbance to protected species or the conservation status of the site then the permission must be revoked – unless the imposition of planning conditions or planning obligations can avoid adverse impacts that have been identified.327 Revocation of consents or permissions will have implications for the payment of compensation eg in the case of the revocation of a planning permission.328

(b)Criteria for Environmental Assessment

13.166 The assessment under the Conservation Regulations 2010 must be carried out in accordance with criteria and guidance set out in the National Planning Policy Framework and supplementary planning guidance. If the development is not directly connected with or necessary to the site’s management then the authority329 must first determine whether the proposal will have a ‘significant’ effect on the European site.

This decision must be made on a precautionary basis, and an environmental assessment is required where there is a probability or a risk that the project will have significant effects on the site.330

13.167 The plan or project’s implications must be assessed in view of the sites conservation objectives, so as to ascertain whether it will prejudice the integrity of the site, either individually or in combination with other plans or projects.331 The maintenance of site integrity is the central objective of the assessment provisions, and this is defined to mean ‘the coherence of [the site’s] ecological structure and function, across its whole area, that enables it to sustain the habitat and/or the levels of populations of the species for which it was classified’.332 Natural England will advise on the technical aspects of the assessment eg on the impact of land-take issues or hydrology. An assessment must be made for each interest feature for which a site is classified and for each designation where a site is classified under more than one international obligation (for example both as an SPA and as a Ramsar site). Moreover, all aspects of the plan or project which can, either by themselves or in combination with other projects, affect the sites conservation objectives must be identified the light of the best scientific knowledge currently available.333

13.168 The planning authority cannot grant planning permission unless, having carried out an appropriate assessment, they determine that the proposal will not adversely affect the integrity of the site, taking into account all likely and foreseeable effects.334 If the project would adversely affect site integrity, or the effects are uncertain but could be significant, then planning permission should not be granted. The decision maker can only grant permission if it has made certain that the plan or project will not adversely affect the integrity of the site, in the sense that no reasonable scientific doubt remains as to the absence of adverse effects.335 This test requires the authority to have regard to the scientific evidence in order to ascertain the presence or absence of scientific doubt as to the likely impacts of the development, and in this endeavour the advice of the statutory conservation bodies (who will be statutory consultees on all planning applications of this nature) will be very important.

In giving advice, it is important that the conservation body has the primary test in view ie whether there is no reasonable scientific doubt as to the presence or absence of adverse impacts on site integrity flowing from the proposed development.336 This involves the prediction of future consequences, based on the available scientific evidence, and the court is unlikely to set aside a decision reached on the advice of the statutory consultees, including the nature conservation bodies, which necessarily involves an evaluation of the scientific evidence to make predictions of likely impacts on the site in the future.337 The planning authority must also consider the way in which the developer intends to carry out the proposal, and can impose planning conditions or planning obligations if they consider that this would avoid the adverse effects that have been identified.338 In this case the decision maker should identify the potential risks as far as may be reasonably foreseeable in the light of such information as can reasonably be obtained and put in place a legally enforceable framework with the aim of preventing the risks from materialising.339

13.169 If the decision maker is unable to ascertain that the development will not have adverse affects on the site’s integrity, then planning permission cannot be granted unless one of a number of closely defined circumstances applies.340 The planning authority must be satisfied that there are no alternative solutions that would have a lesser effect than the proposed development on the site’s integrity. If an alternative solution is identified then planning permission must be refused. If, on the other hand, no alternative solution is identified then permission can be granted only if the proposed development has to be carried out for imperative reasons of overriding public interest. These can include considerations of a social or economic nature, and the government will obtain the opinion of the European Commission as to whether particular reasons can be considered imperative and overriding for these proposes.341 In every case, the overriding importance of the public interest in development must be such as to override the ecological importance of the designation – and the Conservation Regulations require the planning authority to consult with and consider the views of other competent authorities before agreeing to the development.342 Planning guidance makes it clear that permission will be given in these circumstances in very few cases.

13.170 If the site host a ‘priority’ habitat or species type identified in the Habitats Directive then the grounds on which consent can be granted are narrower.343 The only considerations of overriding public interest which can justify a grant of planning permission are those relating to public health or safety, ‘beneficial consequences of primary importance for the environment’, or other reasons which the authority consider – having regard to the opinion of the European Commission – to be imperative reasons of overriding public importance.344 If there are other grounds, their status as imperative reasons must be confirmed by the European Commission. The court of appeal considered the meaning of this provision in Duke of Westminster’s Settlement v Welsh Assembly Government345 where it was held that the words ‘other imperative reasons of overriding public interest’ in the regulations346 could not allow the preservation of a protected species to itself constitute the ‘public interest’ legitimising the grant of a licence – their preservation was instead the objective of the regulations and the controls they impose on planning and licensing decisions.347

(c)Compensatory Measures

13.171 Where a plan or project is consented on grounds of overriding public interest – notwithstanding a negative assessment of its implications for a European site – the appropriate authority must secure that any necessary compensatory measures are taken to ensure that the overall coherence of the Natura 2000 network is protected.348 This might include, for instance, the designation of an alternative site hosting the same habitat type as that lost to the development. In the second reporting period for member state implementation of the Directive (2001-2006), the UK implemented compensatory measures for nine projects affecting SACs, and 7 affecting SPAs under the Birds Directive.349

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Source: Rodgers Christopher. Agricultural Law. Bloomsbury Publishing,2016. — 914 p.. 2016
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