“Similar habitats are available in the local surrounding landscape, which may reduce the magnitude of the predicted impacts for many species. However, black hairstreak has limited dispersal ability and alternative habitats may not be accessible. Research has shown that black hairstreak took 13 years for a new colony to become established from existing colonies only 400m away. The development is therefore predicted to have a direct negative impact upon invertebrate assemblages on the access road of up to Parish value and upon populations of grizzled skipper and glow worms of up to District Value. The development is also predicted to have a direct negative impact on black hairstreaks of up to County value.”
“Existing functional corridors of blackthorn across the main site would be maintained and enhanced. The access road scheme has been redesigned to protect the majority of the blackthorn scrub along the access road. Where cutting back or removal of blackthorn is unavoidable, hairstreak eggs would be translocated prior to these works commencing. The translocation plan would be designed and implemented through the Ecological Management Plan.”
“The LPA must consider whether Article 12 will be breached, and if it will be breached, the likelihood of the proponent gaining the necessary derogation licence from Natural England. The ES confirms that Article 12 would be breached … twice: 1) the destruction of bat roosts of low conservation significance for common pipistrelle and brown [long-eared] bats. 2) a risk of injury or killing; the potential for destruction of resting places and disturbance that could impair the ability of great crested newts to survive, to breed or to hibernate or migrate. In both cases, evidence is presented within the ES and other supporting documents to show that the impacts have been minimised; that mitigation measures proposed are in line with best practice and, as far as is possible, have been scrutinised by Natural England. Natural England has not raised an objection to the assessment of impacts or mitigation measures proposed for EPS. On this basis, it is our conclusion that EPS licences for these breaches are likely to be granted.”
“[Natural England] has not previously maintained an objection to the application in respect of impacts to bats and this position was confirmed in our recent meeting. [Natural England’s] view is that the mitigation measures proposed for lost bat roosts are broadly suitable and that detailed mitigation proposals, which are subject to scrutiny by [Natural England’s] licensing department, are likely to be suitable to avoid effects on favourable conservation status of the species concerned. [Natural England] also expressed the opinion that the impacts associated with foraging and commuting habitat, including Bechstein’s bats, would be addressed by the mitigation and compensation measures proposed in the EMP, which would ensure that the conservation status of local populations of bats would not be adversely affected.”
“[Natural England] has not previously maintained an objection to the application in respect of impacts to great crested newts (GCN) and this position was confirmed in our recent meeting. Natural England’s planning liaison and European Protected Species (EPS) licensing team have reviewed SLR’s 2011 GCN reports and proposed mitigation, through the formal “GCN Masterplan”, which accompanied the planning application. The most recent GCN Masterplan (August 2011, v 5) has been approved by [Natural England’s] licensing team through the recent grant of an EPS licence for a permitted phase of this masterplan … . Therefore, the appropriate authority (Natural England) has confirmed that the baseline data and mitigation proposed in the masterplan for the Greatmoor EfW is suitable to ensure that the favourable conservation status of local populations of GCN would not be adversely affected by the proposed development, in combination with other associated developments in the Calvert area.”
“… [In] considering alternative sites, I would advise that the evidence base for the [core strategy] has not identified a specific access road to the site. The evidence base has considered five alternative route options of which the proposed access road is one. As set out in paragraph [54] of this report, the applicant has also considered seven alternative access roads and a detailed assessment of one alternative was also carried out. … The applicant’s conclusion is that the proposed access road along the disused railway line is preferred as it would not involve the use of local roads and would lead to less disturbance to local residents and visual intrusion than the alternatives considered. It is a distinct former transport corridor providing direct access to the A41. The applicant also concludes that whilst there would be ecological impacts, the alternative raises similar concerns with less opportunity for mitigation.”
“… [The] applicant has also considered alternatives to the access road proposed, including one option in some detail. I would advise that as some of the European Protected Species interest relates to the proposed access road, members could take the view that, if there is a better-performing (i.e. less harmful) alternative access roads to the one proposed, then the second test would not be met. Taking account of the evidence base for the [core strategy] and the work carried out by the applicant with regard to alternative routes into the site, it would seem that with regard to impacts on residential amenity and other highway users, there is no better way of achieving a direct access to the A41 for road transport to and from the site, than along the disused railway line as proposed in this application. The applicant argues that the ecological impacts would be less, but it could be argued that the only way to gain a real comparison with the alternatives, in terms of the level of harm that would be caused to European Protected Species, would be for a planning application to have been brought forward with the same level of ecological survey work attached to it as has been provided in support of this application. There is also the need to consider alternative means of transport, which in this case is most obviously by rail.”
“… A new access road is essential if the removal of the existing impact of heavy vehicles using local roads to the Brackley Lane access to the site is to be achieved and I consider that, without this, the additional heavy vehicles impact would be unacceptable. Whilst I cannot advise members with certainty that the impact on Protected Species would not be less if an alternative access to that proposed in this application were to be brought forward for consideration, it does seem to me that on the basis of the work that has been carried out, there is sufficient evidence that other impacts would be considerable and hard to overcome. On the basis of an assessment of the available evidence, I therefore consider that, on balance, there is no satisfactory alternative access route which would be less harmful and so that there is no satisfactory alternative and in this respect the second test is met.”
“Therefore, if members are satisfied that the need for this facility to come forward constitutes an over-riding public interest, that there is no satisfactory alternative site including the proposed access road and that the impact to bats and Great Crested Newts would not be detrimental to the maintenance of their populations at a favourable conservation status in their natural range, then the above test for the impact on European protected species is met. Planning permission could therefore be granted and in this respect the development is in accordance with the provisions of theHabitats Directive and the Conservation of Habitats and Species Regulations 2010 and the guidance in PPS9.”
“… [If] members are satisfied that there would be no significant and lasting adverse impact on the nationally protected species or their habitats and that in the longer term there would be a significant enhancement to the biodiversity value of the application site, I consider that the application meets the requirements of Policy 25 of the MWLP and NRM5 and NRM15 of the SEP. If Natural England withdraws its objection then I also consider that in respect of the SSSIs there would be no conflict with policy 24 of the MWLP nor policies NRM5 and NRM15 of the SEP.”
“… The Planning Officer stated that Buglife had referred to the NPPF and suggested guidance which indicated that in certain circumstances the application should be deferred or delayed. The Planning Officer advised that this was not the case. The NPPF says ‘if significant harm is unavoidable, or cannot be adequately mitigated against or – as a last resort – compensated for, then planning permission should be refused.’ Buglife had interpreted this as meaning the application should be refused, but this is not the intention of the NPPF. It states that harm to biodiversity should be avoided or mitigated. If it cannot be avoided, compensation should be given as a last resort. It was noted that Natural England accepted what would be put in place if the application was approved. The member stated that the NPPF also says ‘Planning permission should also be refused if it would result in the loss or deterioration of irreplaceable habitats.’ The Ecological Adviser from Jacobs stated that the habitat on the site was not irreplaceable and not structural so it could be replaced. With regard to where the habitat would be situated this would form part of the ecological management plan which would need to be submitted in more detail for approval. The Planning Officer had made reference to invertebrate groups and in this connection it was possible to move and relocate their habitat structure.”
“A member stated that Buglife stated that loss of habitat structures and corridors would have an impact on wildlife and asked for clarification. The Ecological Adviser said he believed this was incorrect. The mitigation would retain many network features in the areas and much of the vegetation was being retained. Other corridors were being strengthened. With regard to timescale and monitoring of translocation, it was noted that this scheme would … also be submitted for approval in due course.”
“There is an overriding need for an Energy from Waste recovery facility to be provided by 2016 which outweighs the significant adverse impact on the settings of Lower Greatmoor Farmhouse and Finemeerhill House Grade II Listed Buildings. Subject to the provision of a Section 106 legal agreement relating to [these] buildings and their settings and other matters and a Section 278 Highways Act agreement and conditions set out above, the proposed development is considered to be generally in compliance with policies 10-13, 17-22, 25, 28-31, 33, 36-39 of the Buckinghamshire Minerals and Waste Local Plan 2004-2016; Policies GP38-GP40, GP45, GP60, GP84, RA29 and RA36 of Aylesbury Vale District Local Plan; CC1, CC2, CC4, CC6, CC8, NRM1, NRM2, NRM4, NRM11, NRM13, NRM14, NRM16, W3-W5, W7, W11-W15, W17, M4, C4, C6 and BE6 of the South East Plan; Planning Policy Statement 10; The Waste Strategy for England 2007; The Government Review of Waste Policy in England 2011; National Policy Statement EN-1 and EN-3; Written Ministerial Statement: Planning for Growth (23 March 2011 ); The EC Landfill Directive 2007/76/EC; The Waste Incineration Directive 2000/76/EC; The Revised Waste Framework Directive 2008/98/EC; The Renewable Energy Directive 2009/28/EC and the National Planning Policy Framework 2012.”
“No part of the development including the proposed access road (the disused railway line) shall take place until the Ecological Management Plan … has been reviewed and updated and the amended document has been submitted to and approved in writing by the County Planning Authority. The Ecological Management Plan as submitted shall include:- … v) The creation of all habitats within and outside of the application boundary, including the enhancement area … as early as appropriate to minimise the time lag between the destruction of habitats and the creation of replacements. … xxii) The annual submission for five years of the results of surveys of black and brown hairstreak butterflies in accordance with Table 9-2 of the EMP. The carrying out of mitigation measures, if negative impacts, attributable to the development, are observed on the populations, … . xxiii) Confirmation of the volumes of railway ballast that will be made available from the ground preparation works along the disused railway line to develop more of the “open mosaic” (early successional) habitat for the butterflies to recreate the track bed habitat that is being lost; xxiv) Confirmation of the locations and areas of the habitat to be created, in accordance with recommendations made by the County Planning Authority in consultation with Natural England; xxv) The submission of a programme for monitoring general invertebrate interest along and adjacent to the line of the proposed new access road … and within newly created habitats to be submitted to and approved in writing by the County Planning Authority before the commencement of works on site. All subsequent work shall comply with the provisions of the agreed monitoring strategy. … xxx) The management of the blackthorn scrub along the proposed access road … to initially restore the balance between younger and older age classes and ultimately to establish a small patch cutting regime on approximately a 30 years rotation … to give a range of age classes spread along the length of the railway; xxxi) The retention of all cut scrub from the disused railway line and the use of this to create foraging habitat for newts and reptiles within the road margins. … xxxv) The implementation of the initial stages of the EMP as approved prior to the commencement of the development where specified and the continuance of works in accordance with the EMP throughout the operation of the development. …”
“The planning committee must grant or refuse planning permission in such a way that will ‘establish a system of strict protection for the animal species listed in Annex IV(a) in their natural range …’ If in this case the committee is satisfied that the development will not offend article 12(1)(b) or (d) it may grant permission. If satisfied that it will breach any part of article 12(1) it must then consider whether the appropriate authority, here Natural England, will permit a derogation and grant a licence under regulation 44. Natural England can only grant that licence if it concludes that (i) despite the breach of regulation 39 (and therefore of article 12) there is no satisfactory alternative; (ii) the development will not be detrimental to the maintenance of the population of bats at favourable conservation status; and (iii) the development should be permitted for imperative reasons of overriding public importance. If the planning committee conclude that Natural England will not grant a licence it must refuse planning permission. If on the other hand it is likely that it will grant the licence then the planning committee may grant conditional planning permission. If it is uncertain whether or not a licence will be granted, then it must refuse planning permission.”
“In my judgment this goes too far and puts too great a responsibility on the planning committee whose only obligation under regulation 3(4) is, I repeat, to “have regard to the requirements of the Habitats Directive so far as [those requirements] may be affected by” their decision whether or not to grant a planning permission. Obviously, in the days when the implementation of such a permission provided a defence to the regulation 39 offence of acting contrary to article 12(1), the planning committee, before granting a permission, would have needed to be satisfied either that the development in question would not offend article 12(1) or that a derogation from that article would be permitted and a licence granted. Now, however, I cannot see why a planning permission (and, indeed, a full planning permission save only as to conditions necessary to secure any required mitigating measures) should not ordinarily be granted save only in cases where the planning committee conclude that the proposed development would both (a) be likely to offend article 12(1) and (b) be unlikely to be licensed pursuant to the derogation powers. After all, even if development permission is given, the criminal sanction against any offending (and unlicensed) activity remains available and it seems to me wrong in principle, when Natural England have the primary responsibility for ensuring compliance with the Directive, also to place a substantial burden on the planning authority in effect to police the fulfilment of Natural England’s own duty.”
“Where, as here, Natural England express themselves satisfied that a proposed development will be compliant with article 12, the planning authority are to my mind entitled to presume that that is so. The planning committee here plainly had regard to the requirements of the Directive: they knew from the officers’ decision report and addendum report … not only that Natural England had withdrawn their objection to the scheme but also that necessary measures had been planned to compensate for the loss of foraging. … I cannot agree with Lord Kerr JSC’s view … that regulation 3(4) required the committee members to consider and decide for themselves whether the development would or would not occasion such disturbance to bats as in fact and in law to constitute a violation of article 12(1)(b) of the Directive.”
“[44.] … In my view, it is quite unnecessary for [an officers’] report [to committee] such as this to spell out in detail every single one of the legal obligations which are involved in any decision. Councillors were being advised to consider whether the proposed development would have an adverse effect on species or habitats protected by the 1994 Regulations. That in my view is enough to demonstrate that they “had regard” to the requirements of the Habitats Directive for the purpose of regulation 3(4). That is all they have to do in this context, whereas regulation 48(1)(a) imposes a more specific obligation to make an “appropriate assessment” if a proposal is likely to have an effect upon a European site. … [45.] Furthermore, the United Kingdom has chosen to implement article 12 of the Directive by creating criminal offences. It is not the function of the planning authority to police those offences. Matters would, as Lord Brown JSC points out, have been different if the grant of planning permission were an automatic defence. But it is no longer. And it is the function of Natural England to enforce the Directive by prosecuting these criminal offences (or granting licences to derogate from the requirements of the Directive). The planning authority were entitled to draw the conclusion that, having been initially concerned but having withdrawn their objection, Natural England were content that the requirements of the regulations, and thus the Directive, were being complied with. Indeed, it seems to me that, if any complaint were to be made on this score, it should have been addressed to Natural England rather than to the planning authority. They were the people to assess the meaning of the updated bat survey and whether it did indeed meet the requirements of the Directive. The planning authority could perhaps have reached a different conclusion from Natural England but they were not required to make their own independent assessment.”
“With regard to the updated bat survey, there is no reason to believe that Natural England did not, when evaluating this, understand both the legal requirements and their general role and responsibilities at the stage at which they were approached by the council. … The important point is … that Natural England was well placed to evaluate this survey, and having done so, gave the advice they did. … .”
“It may well be that, if Natural England had unambiguously expressed the view that the proposal would not involve any breach of the Habitats Directive and the committee had been informed of that, it would not have been necessary for the committee members to go behind that view. But that had not happened. It was simply not possible for the committee to properly conclude that Natural England had said that the proposal would not be in breach of the Habitats Directive in relation to bats. Absent such a statement, they were bound to make that judgment for themselves and to consider whether, on the available evidence the exercise of their functions would have an effect on the requirements of the Directive. I am afraid I am driven to the conclusion that they plainly did not do so.”
“This exercise is in no way a substitute for the licence application which will follow if permission is given. But it means that if it is clear or perhaps very likely that the requirements of the directive cannot be met because there is a satisfactory alternative or because there are no conceivable “other imperative reasons of overriding public interest” then the authority should act upon that, and refuse permission. On the other hand if it seems that the requirements are likely to be met, then the authority will have discharged its duty to have regard to the requirements and there would be no impediment to planning permission on that ground. If it is unclear to the authority whether the requirements will be met it will just have to take a view whether in all the circumstances it should affect the grant or not. But the point is that it is only by engaging in this kind of way that the authority can be said to have any meaningful regard for the directive.”
“… Of course, Natural England may not in terms have expressed itself satisfied that the proposals in the Masterplan would comply with Art. 12 of the Habitats Directive. Natural England was only not objecting to the proposals – presumably on the basis that the impact on the foraging and roosting habitats of bats would be relatively modest. But the upshot was that when the Secretary of State was obliged to have regard to the requirements of the Habitats Directive to the extent that they may be affected by his planning functions under the 1990 Act, he was entitled to have regard to Natural England’s views about the impact of the proposals on the foraging and roosting habitats of bats, and to grant planning permission unless it was likely that (a) a licence under reg. 53 would be required and (b) when it was applied for, it would be refused.”
“Judgment in Morge was handed down on9 January 2011 , a few weeks after the Secretary of State made the decision which is being challenged in this case. At that time, the test was the more onerous one adopted by the Court of Appeal in Morge … and [Woolley], … namely that if the planning committee was uncertain whether or not a licence under reg.53 would be granted, planning permission should be refused. So if the Secretary of State took the view that it was likely that a licence under reg.53 would be granted if it was sought, all the more so for him to have thought that it was unlikely that it would not be granted if it was sought.”
“The analysis of whether “there is no other satisfactory alternative” presumes that a specific problem or situation exists and needs to be tackled. The competent national authorities are called upon to solve this problem or situation by choosing, among the possible alternatives, the most appropriate that will ensure the best protection of the species while solving the problem/situation. To ensure the best protection of species, these alternatives must be assessed with regard to the prohibitions listed in Article 12. They could involve alternative locations (or routes), different development scales or designs, or alternative activities, processes or methods.”
“Evidently, the requirement to consider seriously other alternatives is of primary importance. The discretionary power of Member States is limited, and where another solution exists, any arguments that it is not “satisfactory” will need to be convincing. Moreover, it should be stressed that another solution cannot be deemed unsatisfactory merely because it would cause greater inconvenience to or compel a change in behaviour by the beneficiaries of the derogation.”
“There was no sentence-by-sentence analysis of PPS9. However, its overall tenor was not ignored, the adverse effects being carefully analysed. The respondents were entitled to conclude that the harm was not, in the terms of the circular, significant. They were entitled to take the mitigation proposed, and the assessment of its effect, into account when making their decision. They were entitled to give considerable weight to the representations of Natural England, the expert statutory consultees. Indeed, it would have been surprising if, having regard to the public interests involved, they did not give them such weight. The planning conditions imposed and the detailed section 106 agreement were, as Natural England accepted, a valuable safeguard. Natural England withdrew its objection to the planning application.”
“When determining planning applications, local planning authorities should aim to conserve and enhance biodiversity by applying the following principles: • if significant harm resulting from a development cannot be avoided (through locating on an alternative site with less harmful impacts), adequately mitigated, or, as a last resort, compensated for, then permission should be refused; • proposed development on land within or outside a Site of Special Scientific Interest likely to have an adverse effect on a Site of Special Scientific Interest … should not normally be permitted. Where an adverse effect on the site’s notified special interest features is likely, an exception should only be made where the benefits of the development, at this site, clearly outweigh both the impacts that it is likely to have on the features of the site that make it of special scientific interest and any broader impacts on the national network of Sites of Special Scientific Interest; … • the following wildlife sites should be given the same protection as European sites: - potential Special Protection Areas and possible Special Areas of Conservation; - listed or proposed Ramsar sites; and - sites identified, or required, as compensatory measures for adverse effects on European sites, potential Special Protection Areas, possible Special Areas of Conservation, and listed or proposed Ramsar sites.” • if significant harm resulting from a development cannot be avoided (through locating on an alternative site with less harmful impacts), adequately mitigated, or, as a last resort, compensated for, then permission should be refused; • proposed development on land within or outside a Site of Special Scientific Interest likely to have an adverse effect on a Site of Special Scientific Interest … should not normally be permitted. Where an adverse effect on the site’s notified special interest features is likely, an exception should only be made where the benefits of the development, at this site, clearly outweigh both the impacts that it is likely to have on the features of the site that make it of special scientific interest and any broader impacts on the national network of Sites of Special Scientific Interest; … • the following wildlife sites should be given the same protection as European sites: - potential Special Protection Areas and possible Special Areas of Conservation; - listed or proposed Ramsar sites; and - sites identified, or required, as compensatory measures for adverse effects on European sites, potential Special Protection Areas, possible Special Areas of Conservation, and listed or proposed Ramsar sites.”
“Where on the other hand the members have followed their officers' recommendation, and there is no indication that they have disagreed with the reasoning in the report which lead to that recommendation, then a relatively brief summary of reasons for the grant of planning permission may well be adequate. …”