“Sites of Special Scientific Interest 6.4.24 SSSIs are of national importance.The Wildlife and Countryside Act 1981 as amended by theCountryside and Rights of Way Act 2000 , places a duty on all public bodies, including planning authorities, to take reasonable steps, consistent with the proper exercise of their functions, to further the conservation and enhancement of the features by reason of which a SSSI is of special interest. SSSIs can be damaged by developments within or adjacent to their boundaries, and in some cases, by development some distance away. 6.4.25 Development in a SSSI which is not necessary for the management of the site must be avoided. This is a matter of principle to ensure that these sites can continue to fulfil their role at the heart of resilient ecological networks. What may be necessary for the management of a site will need to be considered on a case by case basis but it is likely to be limited to activities needed to meet its conservation objectives, including restoration and nature recovery, as well as site management infrastructure, natural flood management and other appropriate nature based solutions. There may be desirable interventions in SSSIs relating to public access, active travel, educational projects and other minor development necessary to secure its role as a living landscape. This may include agricultural development, such as new barns, slurry stores required to reduce pollution, barn conversions to support tourism or other alterations or extensions to existing houses or buildings on existing employment sites where effects on the features for which a site has been designated can be considered to be acceptable. 6.4.26 There is a presumption against all other forms of development in a SSSI as a matter of principle and this presumption should be appropriately reflected in development plans and development management decisions. There is also a presumption against development not within a SSSI but likely to damage a SSSI. In such cases, proposals must be carefully assessed to ensure that effects on those nature conservation interests which the designation is intended to protect are clearly understood and development should be refused where there are adverse impacts on the features for which a site has been designated. International and national responsibilities and obligations for conservation should be fully met, and, consistent with the objectives of the designation, statutorily designated sites should be protected from damage and deterioration, with their important features conserved and enhanced and the capacity for restoration demonstrated by and through appropriate management. 6.4.27 In wholly exceptional circumstances and only where development is considered to be appropriate and is not likely to damage a SSSI and there is broad and clear agreement for mitigation and enhancement as part of a development plan should development be proposed. This means that development will be considered unacceptable in the absence of an agreed position in a development plan which indicates that it is acceptable in terms of its effect on the notified features of a SSSI. 6.4.28 Before authorising development outside of a SSSI but likely to damage any of the notified features of a SSSI, planning authorities must give notice of the proposed operations to NRW, and must take its advice into account in deciding whether to grant planning permission and in attaching planning conditions. Where local planning authorities are minded to grant planning permission against the advice of NRW they must notify Welsh Ministers. For the purposes of land use planning proposed SSSIs will be treated in the same way as notified SSSIs.”
“Nationally Protected Sites and Species (1) Development likely to have an adverse effect either directly or indirectly on the conservation value of nationally protected sites will only be permitted where it is demonstrated that: a) There is no suitable alternative to the proposed development; and b) It can be demonstrated that the benefits from the development clearly outweigh the special interest of the site; and c)Appropriate compensatory measures are secured; or d) The proposal contributes to the protection, enhancement or positive management of the site. (2) Development likely to have an adverse effect on nationally protected species will only be permitted where it is demonstrated that: a) The population range and distribution of the species will not be adversely impacted; b) There is no suitable alternative to the proposed development; c) The benefits of the development clearly outweigh the adverse impacts on the protected species; and d) Appropriate avoidance, mitigation and compensation measures are provided.” a) There is no suitable alternative to the proposed development; and b) It can be demonstrated that the benefits from the development clearly outweigh the special interest of the site; and c)Appropriate compensatory measures are secured; or d) The proposal contributes to the protection, enhancement or positive management of the site. a) The population range and distribution of the species will not be adversely impacted; b) There is no suitable alternative to the proposed development; c) The benefits of the development clearly outweigh the adverse impacts on the protected species; and d) Appropriate avoidance, mitigation and compensation measures are provided.”
“The site is of special interest because it supports over 3% of the national population of both breeding and non-breeding chough. Chough nest in crevices on cliffs between south Ceredigion and north Pembrokeshire. A rocky stretch of coastline at Craig yr Adar near New Quay supports an important seabird population including the only known breeding colony of kittiwakes in Ceredigion. The grassland plateau on Cardigan Island supports a significant breeding population of the lesser black-backed gull. Since the early 1990s, this species has been in decline from many other sites making this colony one of national importance.”
“Chough Disturbance of breeding and roosting sites Sheltered crevices and recesses on the cliff faces in some areas are used for breeding and roosting and it is important that these specific locations remain undisturbed, particularly during the breeding season from March to July and at dusk during the autumn and winter months. Maintenance of suitable feeding habitat Chough feed on invertebrates living in short unimproved turf and bare ground. Appropriate grazing of coastal grassland areas is therefore important to maintain these areas. In addition, invertebrates associated with dung, particularly of cattle and horses, can be an important food source so the use of ‘ivermectins’, should be avoided in key areas. The outwintering of stock is beneficial.”
“4.3 Policy 1 of the Pembrokeshire Coast National Park Local Development Plan 2 (LDP2) sets out the National Park’s purposes and duty, in order to ensure that development within the Park is compatible with these. Proposals within a countryside location need to demonstrate that they are essential in order to evidence that they comply with the conservation element of the National Park’s purposes. Matters of ecology and potential biodiversity impacts are also critical in understanding whether or not a proposal complies with the National Park purposes. Biodiversity matters are assessed in greater detail below.”
“8.1 PPW, TAN5 and LDP Policy 11 require biodiversity considerations to be taken into account in determining individual applications. The presence of a species protected under UK or European legislation is a material consideration when dealing with applications that are likely to result in disturbance or harm to the species or its habitat. 8.2 In order to comply withPlanning Policy Wales (2024) and the Environment (Wales) Act 2016 , planning authorities are expected to ensure every development positively contributes to biodiversity. Indeed, Planning Policy Wales 12 states that all development must result in a net benefit for biodiversity. Edition 12 of PPW also required that all application must be accompanied by a Green Infrastructure Statement and that this must show the step-wise approach has been followed.”
“8.5 Considerable public concern has been raised in terms of the potential for this application to contribute to a perceived level of disturbance at Ceibwr which borders the Cardigan Bay Special Area of Conservation.”
“8.16 In addition to the Habitats Regulation requirements the Local Planning Authority is separately required to consider its duty under theEnvironment (Wales) Act 2016 . Section 6 of this Act states that public authorities that exercise their functions in relation to Wales have a duty to maintain and enhance biodiversity and promote the resilience of ecosystems. The Authority still has a duty to consider potential impacts on nesting Auks habitat through the Environment (Wales) Act. There has been a recent study by an accredited Ecological surveyor commissioned by NRW on the disturbance levels experienced as a result of the coasteering activities at Ceibwr Bay. A copy of the draft report has been considered and informs the conclusion on potential impacts of the proposal, whilst the formal report has not yet been released by NRW. This recent study focused on the potential harm to nesting birds and concluded that there was not a significant risk from coasteering to the species studied who are increasing in number at other known sites. 8.17 Officers in discussion with the PCNPA Ecologist are content that the conditions, including that requiring an Access Management Plan to be submitted annually, alongside the other specific onsite measures relating to biodiversity provide a suitable mechanism to ensure that wider biodiversity is maintained and enhanced. 8.18 Subject to appropriate conditions to ensure that the biodiversity enhancements proposed with the scheme are delivered and maintained appropriately; that an appropriate access management plan is put in place and that any future external lighting is controlled, overall, the proposed development is considered acceptable in terms of its impact on biodiversity and as such is considered to comply with Policy 11 of the LDP, the requirements of theHabitats Regulations and the Environment (Wales) Act 2016 .”
“Both the range (in terms of viable seal pupping locations free from disturbance) and populations (where disturbed seals and pups could be put at risk if disturbed) could therefore be impacted if measures are not put in place to reduce this risk.”
“Although species may be present in close proximity to activities associated with the planning application, as the SPA is almost 50km away, it is not considered that individual Chough or their nests close to Ceibwr bay would be connected to or fundamental to the population size of the Skomer, Skokholm and Seas off Pembrokeshire SPA. For the above reason, impacts upon the SPA for this feature can be screened out and will not proceed to Appropriate Assessment.”
“The survey concluded that no evidence was found to suggest that the breeding success of seabirds was affected by coasteering group activities, although some actions observed that had the potential to be detrimental.”
“The existing operation must cross National Trust land in order to undertake their None – disturbance as a result of coasteering activities. The National Trust restrict access for such activity unless subject to Range the hub building providing the business is signed up to adherence to their Concordat. The Concordat was conditions written to safeguard the long-term use of National Trust land in Pembrokeshire increased opportunity for and balance the use with the wider environment by outdoor group activities. The more groups able to use Concordat applies to commercial coasteering activity providers and sets out a Ceibwr bay for outdoor code of conduct expected by all providers which includes measures to protect the activities. natural environment through the avoidance of wildlife disturbance (details are within the Concordat which is not a publicly available document). The Concordat includes specific measures associated with Ceibwr bay and the relevant operator to this application has agreed that they will not use the areas outlined within the relevant document (confidential) between 1st August and 30th November each year to prevent impact on seals and their pups. The operator is currently signed up to the concordat and must remain so in order to access through National Trust land. If the Concordat is breached the following course of action is taken by the National Trust: 1st breach – Verbal response to remind operators of obligations under the code and ask them to modify conduct accordingly 2nd breach – written warning 3rd breach – if no action taken by provider access under the concordat is revoked. Once the Concordat has been revoked the operator will lose rights to access via the land and therefore would be unable to operate form the area. This helps to provide confidence that impacts from the development will be kept to minimum and the National Trust as the owner of the Concordat are responsible for ensuring compliance and will otherwise revoke access. It is acknowledged that the Authority has no control under the Concordat and that it only applies to coasteering activity and not other outdoor activities including kayaking, climbing etc. The Authority therefore recommends imposing a condition to agree an access plan with the applicant to seek to manage access for all outdoor activities in a way that minimises impact on pupping seals, including restrictions on and requirements as to how access may be undertaken if pupping seals are present in Ceibwr bay while access is taken. In addition to the Coasteering Concordat, Pembrokeshire also operates a voluntary Marine Code which highlights Agreed Access Restrictions drawn up by conservation experts and coastal users. This Marine Code would be particularly applicable for kayaking. This includes limits on landing times on pupping beaches and keeping a minimum distance of 50 metres from seals in the water unless they approach an individual. As with the Concordat, this could be implemented by including appropriate elements in an Access Plan required by a planning condition. The Pembrokeshire Marine Code is available here: Pembrokeshire Marine Code. In order to ensure there is no large increase in the number of operators able to operate out of Ceibwr above existing levels, the new hub must only be available for use by the relevant operator associated this planning application. An appropriate condition will be added to any consent to secure this. To ensure customers are aware of the marine code and potential impacts upon wildlife as a result of coasteering activities, information boards must be erected on the front elevation of the main hub building. The information boards must include details of the Pembrokeshire Marine Code, details the Cardigan Bay SAC, information on wildlife likely to be encountered during outdoor activities in the area and what is considered disturbance to these species and details. Again, this will be secured via condition of any consent and will provide further confidence that disturbance impacts from the operations associated with the building will be kept to a minimum as far as possible. The above mitigation measures will ensure that NRW’s Conservation Objectives and vision for the Cardigan Bay Special Area of Conservation (SAC) are able to be delivered.”
“the coherence of its ecological structure and function across its whole area, that enables it to sustain the habitat, complex of habitats and/or levels of population of the species for which the site is (or will be) designated for.”
“Following mitigation discussed in Section 2a, would the proposal exacerbate or contribute to the identified threats and risks? Only disturbance has been identified as having the potential to impact grey seal in association with this application as all other existing known threats and risks to grey seal are not relevant... ...Disturbance can include: displacement, collision and noise & visual disturbance. Education awareness and activity surveillance are indicated as the most likely required actions. There is no suggestion in NRW’s package of information published under section 37 of the Habitats Regulations that these activities can cause a reduction in pupping success, but it remains a possibility. It should be noted that most the important pupping beeches, caves and Haul-out sites occur in Pembrokeshire, grey seals are known to range throughout Cardigan Bay and there are a significant number of pupping sites in south western Ceredigion. The population associated with the Cardigan bay SAC is not isolated a nd due to the known movements of grey seals in Pembrokeshire and Ceredigion is considered that the individuals within the Cardigan bay SAC are park of the South West Wales and England wider population. In a more local context, the population size in South West Wales is estimated to be approximately 5000 individuals. Pup production within the Cardigan Bay site therefore represent only a small proportion of the South-west Wales production. With the above in mind when considering ‘the coherence of its ecological structure and function across its whole area, that enables it to sustain the habitat, complex of habitats and/or levels of population of the species for which the site is (or will be) designated for’, although some disturbance to individual seals cannot be completely ruled out, the significance of the impact of this at a population scale and the ability of the feature to continue to function at a sustainable level, it is not considered that the outcome would be significant to either of these factors. Notwithstanding the above and the baseline situation, because of the potential for increased levels of outdoor activity and the potential for disturbance impacts upon individual seals, measures must be put in place to reduce these impacts from outdoor activity groups associated with the proposal, including through the Concordat and via relevant conditions. With such measures it is considered, on a site specific basis taking into account the likely levels of activity to Ceibwr bay through the proposal that the activity can be managed in such a way that there will be no possible effects on the site’s conservation objectives, accordingly the proposal will not adversely affect the integrity of the coherence of the sites ecological structure and function, across its whole area, that enables it to sustain the habitat, complex of habitats and/or the levels of populations of the species for which it was classified In short, these measures will ensure that there is no impact on the integrity of the SAC. Following the above assessment, is it considered necessary to undertake an in combination assessment to determine if potential effects arising from the current proposal will have in combination effects with other plans or projects.”
“It is noted that peregrine and chough do not currently breed at the site, but do breed nearby and suitable breeding habitat exists within Ceibwr Bay where the increased activities are proposed to take place. It is noted that chough are also a feature of the SSSI, and according to the SSSI management statement the chough population `should contribute towards maintaining the West Wales chough population’. PCNPA should take steps now to factor in the potential for these species to nest at the site as part of its decision-making. If these birds do choose to nest at the site, or where the activities will take place, access to these areas should be strictly restricted and provisions to enforce these restrictions should be in place as part of any permission decision.”
“When considering the objectives of the FCS and in particular the requirement for … “data on the species concerned indicates that it is maintaining itself on a long term basis as a viable component of its natural habitat(s)” in relation to this application, the question must be asked whether or not this proposal will adversely affect the ability of the SAC feature to meet its FCS and the aforementioned objective. It is acknowledged that an individual seals may pup on the beach at Ceibwr and nearby bays used by the activity provider, however the potential to disturbance is limited to these individuals alone. Taking into account the population as a whole and the level at which this potential disturbance would impact it, it cannot be concluded that the ability for the population to maintain itself will be compromised based on disturbance to a very few individuals. In short, individual disturbance does not equate to an adverse impact upon FCS or an adverse impact on integrity of the SAC.”
“That being said, as discussed within the HRA and the subsequent planning condition recommendations, measures can be put in place to reduce the possibility of disturbance impacts upon individual seals using the area and these will eliminate possibility of impact on the FCS of grey seal and eliminate any possibility of impact on the integrity of the SAC.”
“It should be noted that both the HRA and my responses to comments are made using my local expert knowledge and where necessary, in consultation with a network of experts who also have local knowledge of the relevant protected sites and species. I am in no doubt as to the extent of potential impacts and the ability to maintain FCS of the SAC Species, or the ability to comply with Environment (Wales) Act duties. Much has been made of the precautionary principle in representations which applies in circumstances of scientific doubt, but that is not the case here. I would also like to make the point of the overarching benefits of wildlife tourism for nature and biodiversity. For biodiversity to remain high on the agenda of importance, the general population must continue to be engaged with nature and enthused about Pembrokeshire’s special qualities and unique ecology. Interactions with nature can come in many forms, but for many, particularly those who do not have prior experience or indeed, the opportunity, to be in and close to nature, the connections arising from outdoor activities such as coasteering can be invaluable and for some, the start of a meaningful interest. It is acknowledged that this must be managed in an appropriate way to ensure no adverse impacts upon the SAC, however the benefits of this interaction where impacts on individual species are minimised should not go unmentioned. Through appropriate management plans, education and engagement with activity providers, knowledge and important messages about nature conservation can be passed on to those taking part in activities and subsequently create an ongoing interest in nature conservation. Paradoxically, these type of activities, managed in an appropriate way, can help to maintain FCS in an SAC even if there are individual disturbances. As an expert, a balanced approach to assessment of impacts is required and that is essentially an exercise of judgement. My assessment is not as simple as addressing all risks to individuals, but significant risks on a population conservation objective level. I have identified all such reasonably foreseeable risks and am satisfied that the mechanisms proposed for preventing them from arising are legally enforceable. I am in no doubt that in exercising judgements I have met the standards in regard to reasonable scientific doubt required for the impact assessments involved in this application.”
“should they become present with the areas associated with the outdoor activities, the Management Plan will ensure any necessary changes to practice are made”
“Some Members remained concerned regarding the potential for damage to the wildlife in Ceibwr bay, and whether sufficient baseline information was available to determine whether populations had decreased and therefore whether visitor numbers should be controlled. Officers clarified that NRW had undertaken a survey regarding sea bird breeding and it was recommended that this was repeated every five years. …The Director added that in terms of the HRA, the critical issue was regarding the population in the SAC as a whole. However when the management plan was submitted annually, the Authority would consult with NRW and the Ecologist who would be aware of any reports of disturbance, and access to certain areas could thereby be controlled. It was concluded that there would be no impacts on the integrity of the SAC.”
“…those documents relating to the subject matter of the report which— (a) disclose any facts or matters on which, in the opinion of the proper officer, the report or an important part of the report is based, and (b) have, in his opinion, been relied on to a material extent in preparing the report, but do not include any published works.”
“… There are two separate questions. The first question is whether the failure to comply with the relevant procedural requirement results in the decision being unlawful, applying the approach in R v Soneji[2005] UKHL 49 , [2006 1 AC 340, and A1 Properties Ltd v Tudor Studios RTM Co Ltd[2024] UKSC 27 ,[2024] 3 WLR 601 . If so, the second question that may arise is whether a remedy should be refused pursuant to section 31(2A) of the 1981 Act or as a matter of discretion on the part of the court. The two questions are analytically distinct and should be considered separately. …”
“In relation to section 31(2A), the court is concerned with evaluating the significance of the error on the decision-making process. It is considering the decision that the public body has reached, and assessing the impact of the error on that decision in order to ascertain if it is highly likely that the outcome (the decision) would not have been substantially different even if the decision-maker had not made that error. It is not for the court to try and predict what the public authority might have done if it had not made the error. If the court cannot tell how the decision-maker would have approached matters, or what decision it would have reached, if it had not made the error in question, the requirements of section 31(2A) are unlikely to be satisfied.” ii) At [74] he explained that the requirement that it is highly likely that there would have been no substantial difference is “a high test to surmount” adding: “The section emphatically does not require the court to embark on an exercise where the error is left out of account and the court tries to predict what the public body would have done if the error had not been made. Approaching section 31(2A) in that way would run the risk of the court forming a view on the merits and deciding if it thinks the public body would reach that view if it had not made the error. Rather, the focus should be on the impact of the error on the decision-making process that the decision-maker undertook to ascertain whether it is highly likely that the decision that the public body took would not have been substantially different if the error had not occurred.”