The road infrastructure is unable to cope with current volume of traffic without adding more to it.

Extract of Proposals Map from Proposed Replacement Plan
It is noted that that the allocation proposes that the site can accommodate 135 dwellings. It is also noted that site is allocated in the current adopted Local Development Plan and is considered suitable to be ‘rolled forward’ as an RLDP housing allocation, as it is considered to be deliverable and accords with the Strategy of focusing new development within principal settlements such as Barry. It is not clear why since the adoption of the Local Plan i.e. in 2017, little if any progress has occurred to bring the site forward for development.
It is stated that the site is actively being progressed by the Council’s housebuilding team as an affordable housing led development as part of the Cardiff and Vale Housing Partnership.
The principal concern of the owners of Pencoedtre Farmhouse is the impact on the extensive woodland, that lies to the north of the ****** and to the west of the site, as well as the potential impact on Pencoedtre Lane which runs past their property.
Dealing first with the ecological impact, it is stated in the adopted Local Plan, at Appendix 3, that in addition to site specific matters raised under each allocation, a range of supporting information may be necessary to accompany proposals (presumably planning applications for development) that include:
• Environmental Statements (subject to Environmental Impact Assessment [EIA] Screening)
• Transport Assessments
• Design and Access Statements
• Masterplans
• Landscape Assessments
• Travel Plans and, where necessary, improvements to encourage sustainable transport e.g. supported bus services, new or improved footways, public open space, improvements to education facilities or increased capacity.
• Ecological Assessments – while site specific comments have been made on some sites regarding possible features of biodiversity importance, an ecological assessment agreed with the Council’s ecologist or where appropriate Natural Resources Wales, will be required for all sites.
The adopted plan goes onto say that the undertaking of a Habitats Regulation Assessment for the Deposit Local Development Plan does not remove the need for project level Habitats Regulation assessments of individual development sites where they could have an adverse effect on the integrity of a European Protected site.
The various site allocations in the plan may have the potential to support European Protected Species as well as habitats of biodiversity importance. In allocating these sites a precautionary approach has been adopted by the Council and appropriate species surveys, and where relevant appropriate mitigation, will be required to accompany any planning application for the development of the sites in order to comply with the requirements as set out in the Conservation of Habitats and Species Regulations 2010 (as amended). This is to ensure that the proposal does not result in any likely detriment to the maintenance of the favourable conservation status of European Protected Species.
The allocation in the current adopted plan is detailed as a 4.45 hectare Greenfield site that is located to the north west of Pencoedtre, Barry. Part of the site has previously gained planning permission for B1 Business use (planning application 2000/00860/FUL refers) as part of a larger historic employment allocation, however, this permission has not been implemented and parts of the historic employment allocation to the east have since gained consent for residential use.
Therefore, given its size and relationship to the residential development to the east this site has been allocated for residential use providing at least 137 dwellings. The western part of the site currently forms part of the grounds of Bryn Hafren Comprehensive School which has been deemed to be surplus to the school’s requirements. The development of the site will facilitate the delivery of new improved recreational facilities to serve the school and potentially the wider community.
Natural Resources Wales (NRW) is aware that a European protected species has been recorded in the vicinity of the site and an ecological assessment will be required in support of any future planning application. In addition, NRW has advised that the site is within close proximity to the Coedydd y Barri/ Barry Woodland Site of Special Scientific Interest (SSSI) which lies roughly 200 metres to the east and that the designated site should be protected at all times. NRW has encouraged the retention of mature trees and hedgerows on the proposed site for their conservation and aesthetic value.
The Council’s Engineers have advised that a suitable safe access is required that conforms to the current design criteria and future planning applications must be supported by a comprehensive and robust Transport Assessment that evaluates and determines mitigation measures which alleviate any detrimental impact the development will have on the local highway network and associated road junctions. Glamorgan Gwent Archaeological Trust has advised that an archaeological evaluation of the site will be required and that some parts of the site may be required to be retained as open space in order to protect archaeological features
Therefore it would appear that the woodland to the east and south of the site appears to be a Site of Scientific Interest. Consequently in line with NRW advice, it is considered that this site should be protected from any development. Appropriate and fitting ecological assessments should be undertaken prior to any development and it is hoped that the Council will ensure that this is the case when any planning applications are submitted.
In respect of access, currently the lane pass the farmhouse only affords access to that property with the rest of the lane being a pedestrian/cycle route to the residential dwellings at Heol Leubren. It is considered that this should remain the case and that any new accesses should be off Port Road. The existing access at Pencoedtre Lane should remain as pedestrian/cycle only and not used by vehicles.
We trust these comments will be taken into account and particularly when discussions take place between the Council and prospective developers.
Please keep us informed on progress of the plan.

a lot more depth of hedgerows left all round the estate.
a roundabout by the estate entrance that's already there
proper surveys for the animals Bats (at the right time of the year), dormice (when active and not when they are hibernating) and badgers all have act's protecting them

We are objecting to the plans for the land to the west of Pencoedtre Lane. We live in Pencoedtre Lane and this will have a significant impact on our lives due to my Husband who very ill and the noise and disruption will have a major impact of his health.
The development will also have a huge impact and harm on the local wildlife
We would loose more woodland that would affect all the animals that call it home are house is opposite and
we see bats, baggers, dormice, turtle doves, woodpeckers, hedgehogs, cuckoos and squirrels to name but a few.
we would loose more hedgerow and trees.
plus we will have a loss of privacy and all the increase in noise not only at build stage but with the cars from the 126 houses all going past our Home

An alternative site is needed for the re-build of Richard Gwyn school. Flooding is a strong constraint on the idea of rebuilding on the same site. No assessment re predicted higher flood levels; no solution for walking access via the tunnel during flooding; no assessment of completing the active travel access from Coldbrook with a tunnel to meet WGovt standards.
We anticipate the WGovt rejects the rebuild on the present site on grounds of flooding. This site at Pencoedtre is one of the few alternatives. It was school land so the education departement should reclaim it for new RichardGwyn.

Thank you for consulting Natural Resources Wales (NRW) on the Vale of Glamorgan Replacement Local Development Plan (RLDP) Deposit Plan, which we received on 28 January 2026.
We have reviewed the deposit plan and published documents and have recommendations on matters relating to coherence and consistency. We advise these are addressed prior to submission of the RLDP.
1. Summary
We welcome that the Vale of Glamorgan Council has declared a ‘nature emergency’ and in 2021 committed to a target of no net loss of biodiversity in the Vale of Glamorgan. The deposit plan takes this a step further through its vision, objectives and policies in seeking
the achievement of net biodiversity benefit. We also welcome the recognition within the deposit plan and supporting documents that additional growth within the Vale has the potential to lead to negative effects on nationally and locally designated biodiversity. We
appreciate that the deposit plan’s policies seek to mitigate against these potential adverse effects with detailed wording and requirements.
However, we consider that the deposit plan would benefit from more specific mention of designated conservation sites especially where these are related to specific allocations and their associated policies. We note this issue was raised within the Integrated Sustainability Assessment (ISA) (see Section 2 below) however we do not see this recommendation properly reflected within the deposit plan itself. We consider this is a gap that should be addressed to ensure clarity within the policy requirements for any future planning applications.
General Approach to Designated Sites
In line with our role in development planning and our consultation remit, we advise that where new development may occur within or be likely to affect statutory designated sites including Special Areas of Conservation (SAC), Special Protection Areas (SPA), Sites of Special Scientific Interest (SSSI), National Nature Reserves (NNR) and Marine Conservation Zones (MCZ) this could be more clearly identified as a key consideration especially with respect to site allocations (housing and employment). We consider that the issue of avoiding or mitigating potential impacts and utilising opportunities for supporting and enhancing these sites (as noted by para 6.401 of the deposit plan) could have more substantial recognition across the deposit plan and its supporting documents. This would improve the clarity of approach.
We have furthermore noted that Policy SP20 (Biodiversity and Ecosystem Resilience) currently excludes specific mention of designated sites (although it does refer to protected species and habitats) and we suggest that this is addressed – our comments on SP20 are set out in Section 3 of this letter.
By across the plan, we mean there is scope to include mention of relevant statutorily designated sites within the constraints text for the sites listed in Appendix B of document BP44 Infrastructure Delivery Plan (perhaps summarising in line with the approach taken to the Historic Environment Record) and within document BP32A Green Infrastructure Assessment of Key Sites, evidence which can then be reflected as appropriate in Key Sites Policies (HG1 KS1 to KS5) to inform their master planning. The Preliminary Ecological Appraisals already undertaken for Key Sites (Key Site Supporting Information) would appear to hold relevant information in this respect.
We note that document BP32A has a useful general paragraph on biodiversity assets at paras 3.7-3.8 linked to the evidence collated in the Green Infrastructure Assessment (GIA). In short, where designated sites are identified in proximity to allocated sites it would be
helpful to make clear reference to them in a consistent manner. This would bring the deposit plan more fully into alignment with the ISA findings. For any employment sites
within proximity of designated sites, we consider that the employment background paper BP12A could potentially be updated to similar effect.
With reference to omissions on this matter, we refer you to our comments on sites set out in Section 4 of this letter, including sites KS1, HG1 (1), SP14 1. and SP14 4.
Overall, we consider that the recognition of designated sites appears somewhat inconsistent in the deposit plan, although we recognise that much of this is done by the
Green Infrastructure Strategy (GIS) which incorporates the GIA.
It may be that Policy SP20 (please see our suggested amendments in Section 3 of this letter) together with addressing the meaning of “areas of high ecological value” will also go some way towards resolving the points we raise.
Master Planning
We welcome the illustrative master plans included in the deposit plan but would caveat that at the detailed stages schemes must be able to adapt, where necessary, to site
specific environmental constraints (including protected sites, species and habitats), for example in response to updated ecological appraisals or detailed species surveys.
Designs need to be flexible enough to ensure compliance with the stepwise approach (avoid, minimise, mitigate) in achieving Net Biodiversity Benefit (NBB) and improving the resilience of ecosystems as required by Planning Policy Wales, edition 12 (PPW12) and Policy 9 of Future Wales, the National Plan. We note the plan has good reference to this within Policy SP20 and supporting paragraph 6.405, thus enabling thorough consideration
at the project/planning application level and in master planning.
Please see our detailed site-specific comments in Section 4 in order to consider where our comments may lead to adjustments in master plans. For example, the species protection issues we highlight with regard to KS3 at Readers Way, Rhoose.
Strategic Opportunity at Bro Tathan
In addition to the above points, we advise that the Bro Tathan area of the Vale includes a number of different allocations and is already known as an important ecological area for great crested newts (GCN) and dormice, in particular. Given the commitments already
made under previous planning applications at the site and the necessary requirement for future biodiversity provisions, we advise a more strategic overview of the area should be considered and either set out within the deposit plan or secured within an updated GIS.
This will ensure that development in the area:
• does not cause detriment to the maintenance of the favourable conservation status of protected species;
• results in green spaces and infrastructure that is meaningfully spatially connected and sufficient in size.
Overall, we consider piecemeal development of the St Athan area will not lead to effective conservation delivery and will make the planning process less efficient at project level.
Areas of High Ecological Value
As previously noted within our preferred strategy response (Ref: CAS-244275-Q4F4, dated: 14th February 2024), the deposit plan continues to make reference to avoiding
areas of ‘High Ecological Value’ (criterion 1 of SP20). We have not been able to establish where these areas are or how their ecological value is being determined. We consider this issue needs to be clarified and ideally a definition provided.
2. Integrated Sustainability Assessment (ISA)
With regards to Section 9.9 of the ISA, we agree that additional growth in the Vale has the potential to lead to negative effects on nationally and locally designated biodiversity. The ISA concludes that the housing-specific policies set out within the deposit plan work well to
mitigate the potential adverse effects, through design stipulations and policy inclusions.
The ISA then goes on to recommend that Key Site policies are updated, where appropriate, to reference specific designated sites which they are in proximity to, in
order to help establish appropriate protection and/or enhancement measures.
We agree with these recommendations and would go further in advising that all allocations and their associated policies should reference specific designated sites relevant to that site. For instance, we would advise Barry Woodlands SSSI and Walters Farm SSSI is identified in relation to Key Site 1 – Land at North West of Barry, and Barry Woodlands SSSI should also be identified for Housing Allocation HG1 (1) Land to the West of
Pencoedtre Lane. Please refer to our site-specific comments in Section 4 below.

3. Plan and Policy Wording
Strategic Policies
Strategic Policy SP19 – Green Infrastructure
We welcome that the GIS and GIA has informed the master planning of the Key Site allocations (6.395). To ensure this approach is carried forward for other development proposals, we consider there should be a stronger “policy hook” within Policy SP19 to link the content and evidence of the GI work to the policy and its influence on decision-making. Without this we consider there may be a risk of a policy gap/mismatch when determining planning applications.
This could be resolved by a new criterion such as:
“the provision of green infrastructure must have regard to any adopted or emerging guidance including the Green Infrastructure Strategy/Green Infrastructure Assessment
(and the Assets listed therein), and Green Infrastructure (Action) Plan for the Vale.”
To strengthen Policy SP19 we also recommend an addition to the wording of criterion 2 to read:
“Protect and enhance connectivity between existing green infrastructure assets and be planned wherever possible to positively support areas of high ecological value”.
We furthermore note that criterion 3 of SP19 refers to achieving net benefit for biodiversity whilst the policy overall seeks to provide, protect and enhance high quality multi-functional green infrastructure. We have previously commented that multi-functional green spaces may not always be compatible with biodiversity. It should be recognised that multifunctional uses of space can be to the detriment of the natural environment and so must be carefully considered. We recommend that paragraph 6.397 wording is updated to reflect this potential conflict so that NBB required by PPW (and as promoted by para 6.396 together with Policy SP20) is able to be prioritised and not compromised.
This point could also be raised under Policy SP4 Placemaking – at para 6.32. It should not be assumed that multifunctional spaces will also be delivering for nature in every situation and in some cases separate provision of spaces to meet biodiversity goals will be essential.
Paragraph 6.401 is welcomed regarding the opportunities that exist for the protection, maintenance and further enhancement of green infrastructure assets.
Strategic Policy 20 (SP20) – Biodiversity and Ecosystem Resilience
We welcome the inclusion of SP20 which recognises the importance of natural assets and aims to protect these. We have made comments regarding the term “high ecological value” in our Summary section at the start of this letter.
We also note that whilst reference is made to sites and areas of European, national and local importance (para. 6.402), this is not distinctly carried through within SP20 or within a specific detailed policy in the deposit plan. We advise that a more detailed policy for the Natural Environment (similar to DNP4 for the Historic Environment) could be included within the deposit plan and this should include reference to the protection of statutorily designated sites. Alternatively, SP20 itself could be updated to include reference to these in a similar manner to the approach taken to non-statutory designated sites provided by criterion 5 of SP20. We consider this would strengthen the deposit plan’s alignment to
section 6.4.3 of PPW12. This issue is also reflected in our feedback to the ISA as set out in Section 2.
By adding a detailed policy for the wider protection of the natural environment, there is scope to ensure a clearer message within the deposit plan regarding the need for natural resources (including land, air, water and soils) in the Vale to be protected for themselves and the essential ecosystem services they deliver. This is opposed to merely preventing pollution (deposit plan Policy DNP5). Taking such an approach would enable an
opportunity to add the consideration of Sustainable Management of Natural Resources (SMNR) into the plan policy framework rather than confining this to the deposit plan context (para 2.11) and the policy context of the GIS (page 53).
We note that Policy CC4: Renewable, Low and Zero Carbon Energy Generation is more distinct in seeking to safeguard a range of assets (including nature conservation interests and soil conservation interests) and we consider a similar policy approach may be useful
for all development proposals. We also suggest that the placemaking strategic policy (Policy SP4) could be altered in order to highlight the Natural Environment alongside its
current reference to the Historic Environment. We note that placemaking principles (Figure 11 - Identity) includes the need for development to respond to natural physical attributes of the site. This is an issue is linked to our site-specific comments (Section 4 below) where we cite, for example, the need to buffer woodlands, hedgerows and watercourses and preserve linear corridors.
Ensuring an SMNR approach will impact positively on the ground to safeguard and improve ecological networks and protect and enhance ecosystems, essential to meeting
the nature emergency. Topics we draw your attention to include river restoration where, in particular, the removal/remediation of physical modifications can make a significant impact upon water quality. The GIS provides scope to capture various projects and wider initiatives, including those based on catchment scale improvements and we welcome the opportunity to be continually involved in this work. We note and welcome the recognition of
nature-based solutions within Policies SP16, SP19 and SP20 and in detailed Policy CC6.
With regards to natural assets and water resources, we consider that specific reference to water quality is lacking within the strategic and/or detailed policies. Whilst we note that water quality is mentioned within criterion 9 of Policy SP16, we consider the deposit plan should include more direct reference to the Water Framework Directive. We consider there is an opportunity for SP20 to be updated to ensure developments protect water quality and quantity. Alternatively, as mentioned above, this could fit within a detailed policy for the protection of the natural environment.
As a minor point, please note that the South Central Area Statement is not hyphenated (para 2.10 and 2.11). Please note also that, referring to paragraph 6.404 and 6.405, the
requirements for developments to demonstrate NBB is based on PPW12, rather than The Environment (Wales) Act 2016.

Detailed Policies

Infrastructure
Whilst we note that the infrastructure requirements (such as sewerage capacity) have been investigated for certain key sites within the deposit plan, we consider there could be scope for a detailed policy to cover infrastructure requirements for all development.

Policy DNP7
We welcome Policy DNP7 of the deposit plan, which recognises the importance of preserving the natural darkness of the night sky and minimising light pollution, which we consider to be important in limiting adverse impacts upon local biodiversity and ecological
connectivity.

Policy DPN8
Please refer to comments made with regards to this policy under Section 6: Habitats Regulation Assessment (HRA).

Policy HG5 - Affordable Housing Exception Sites
We advise that, particularly given these sites are permissible outside of settlements and could be in countryside locations, criterion 6 should be amended to:
“There is no loss of land with significant recreational, amenity, agricultural, ecological or natural heritage value”.

EMP1 – Employment Regeneration Opportunity Areas
We note that the Former Aberthaw Power Station has been identified as an employment regeneration opportunity area. There are otter and water vole records on the site and we are aware of GCN records within the local area. We would advise against the inclusion of
the Aberthaw Nature Reserve within the allocation and advise that any application on the site would need to be supported by up-to-date ecological survey information and
appropriate conservation measures. Given the nature of the site, future applications will also need to be supported by appropriate land contamination investigations.

CC3 – Renewable Energy Local Search Areas
This policy identifies several sites where the potential for wind and solar development are the greatest (known as ‘search areas’). There are significant search areas located between Llantrithyd and St Hilary; no ecological information has been provided for these search areas, however given the records for GCN, water vole and otter local to these areas, it is likely that provision in the form of suitable habitats will need to be made for these species.
This could be substantial in scale, however without further ecological information we cannot advise further at this time. Notwithstanding, given the scale of the search area in this location and the likely ecological impacts, we advise that this area would benefit from spatial planning of biodiversity provision, at a greater than individual site scale.

Paragraph 2.81 – The Vale Nature Recovery Action Plan
We note reference to ‘6 broad habitat types’ including Woodland, Freshwater, Grassland, Coastal, Agriculture and Urban. We suggest this is amended to ‘6 broad ecosystems’ to reflect correct terminology and the State of Natural Resources Report 2025.

4. Strategic Sites
Overview
We previously provided detailed comments on the RLDP’s Strategic Sites, as set out in our response ref: CAS-234819-C1V3, dated 4th October 2023, which we refer you to. We welcome the additional information provided and note the inclusion of Green Infrastructure
Strategies for each of the Key Sites. However, we note that these do not include reference to protected species specifically and as a result we are unable to confirm that the provision for each site is appropriate. We observe that the road infrastructure for many of these sites severs woodlands and other substantial linear corridors. We advise that such sites are designed to minimise fragmentation in the landscape and advise that the road layouts and consequent severance is re-visited.

KS4 and KS5 are located within the vicinity of St Athan. This area is important for (and we are aware of) multiple records of GCN and dormice. Some of the area is already secured as compensation for impacts on these species associated with previous developments. We advise that the wider St Athan area is subject to spatial planning of biodiversity provision at a greater than individual site scale (as we have referenced in the Section 1 of this letter), in order to determine that:
• It does not cause detriment to the maintenance of the favourable conservation status of both GCN and dormice (strategic conservation plans should be established for both species);
• To ensure that green spaces and infrastructure are meaningfully spatially connected and sufficient in size;
We consider piecemeal development of these areas will not lead to effective conservation delivery and will cause the delivery of these sites to be less effective during the planning process.

Spatial Planning of Biodiversity
A masterplan or spatial biodiversity or GI plan should demonstrate the retention, provision and enhancement of essential areas for protected species. It should ensure that individual site-based habitat provisions are not designed in isolation but considered in association with nearby sites to demonstrate how habitat connectivity and resilience will be provided both across the site and to the wider landscape. Note that functional separation of public
open space and areas for biodiversity compensation may be required. Suitable buffers will need to be applied to any woodland and retained or created habitats on site. A sensitive lighting strategy will also likely be required for these sites. This point was raised previously during our review of the strategic candidate sites (ref: CAS-234819-C1V3, dated 4th October 2023).

Updated Surveys and Appropriate Buffer Zones
Further to the above comments, we welcome reference within the Infrastructure Delivery Plan for the requirement for updated ecological surveys and appropriate buffer zones to watercourses and retained habitat features for KS1 and KS2. Given the various ecological
constraints for each key site, we consider this advice should be included for each of the key sites.

Site Specific Comments
KS1 – Land at North West Barry
Protected Species – Dormice and bats are present on site. We advise that the masterplan is informed by surveys to ensure that biodiversity interests are maintained and enhanced. The site may require some areas to be retained an/or provision for habitats to support them. Dark areas and/or bespoke lighting scheme may also be required at project stage.
Protected Sites – The site is located in close proximity to Walters Farm and Barry Woodlands SSSI. As raised in our previous responses (CAS-234819-C1V3, dated: 4th
October 2023 and CAS-276923-N7H6, dated 17th April 2025), we have some concerns with the potential for increased and inappropriate use of the protected sites through recreational activities. We welcome that requirements have been detailed within HG1 KS1
under Green Infrastructure, Recreation Spaces and Biodiversity, which includes reference to emerging guidance for Suitable Alternate Natural Greenspace (SANG).

KS2 – North of Dinas Powys, off Cardiff Road
Protected Species – We note the supporting Preliminary Ecological Appraisal (PEA) (13th September 2022) which identifies potential for this site to support GCN, dormouse and bats. In the absence of species specific surveys, we are unable to advise whether the housing number aspirations for the site are realistic. We advise the scheme is designed to minimise severance of ecological corridors.

KS3 – Land at Readers Way
Protected Species – GCN are known to be present on this site (Readers Way Pond). The current masterplan indicates that the pond will be surrounded by built development and therefore built upon much of the terrestrial habitat which supports this pond. It is essential
that the masterplan provides a wide corridor from this pond to the wider countryside, other than via the closely managed grassland at Cardiff Airport. Any masterplan should make provision for this and any loss of habitat should be compensated for.

KS4 – Land at Church Farm
Protected Species - There are records of dormouse and GCN in the wider area. However, the supporting PEA indicates no direct impacts on the latter of the species. There appears to be extensive green space proposed in the illustrative masterplan, which we support.

KS5 – Land to the West of St Athan
Protected Species - The St Athan area is important area for GCN and dormouse. We would generally concur with the lower risk assessed for these species in association with this site. However, this is a substantial site and this and other sites in the St Athan area would benefit from spatial planning of biodiversity provision at a greater scale as reaffirmed elsewhere in this response.

5. Housing And Employment Allocations
Housing Allocations

HG1 (1) Land to the West of Pencoedtre Lane
Protected Sites: The site is within close proximity (200m) to Barry Woodlands Site of Special Scientific Interest (SSSI) and there is a risk from increased recreational use as a result of residential development, which could lead to impacts on the SSSI. Green space design must consider any emerging guidance for SANG to reduce recreational pressure on adjacent sites of biodiversity importance.
HG1 (2) Land at the Mole
Land Contamination: Given previous land use at site, a Preliminary Risk Assessment would be required at planning application stage to determine risk of land contamination.
Marine: An adjacent watercourse forms a hydrological link to the Severn Estuary European Marine Site (EMS). A HRA at project level will therefore be required.

HG1 (3) Land at Hayes Lane
Land Contamination: Given previous land use at site, a Preliminary Risk Assessment would be required at planning application stage to determine risk of land contamination.

HG1 (4) Land at Neptune Road
Land Contamination: Given previous land use at site, a Preliminary Risk Assessment would be required at planning application stage to determine risk of land contamination.
Marine: An adjacent watercourse forms a hydrological link to the Severn Estuary EMS. A HRA at project level will therefore be required.

HG1 (5) Land between the Northern Access Road and Eglwys Brewis Road (Site C - Central Parcel)
Flood Risk: The site is located partially within Flood Zone 2 and 3 for Rivers, with the southern area of the site located within Flood Zone 3. We refer you to Sections 10.20 and 10.21 of TAN 15, which state that highly vulnerable development in Zone 3 should be avoided. Notwithstanding, we acknowledge that at masterplanning stage, there is scope to locate residential development away from areas of flood risk. We also welcome that
Appendix B of your Infrastructure Delivery Plan notes the requirement for an FCA at project level for this site.
Watercourse: Boverton Brook (Main River) runs through the site and any development will need to ensure no adverse impacts to the watercourse with appropriate buffers and design considerations.

HG1 (6) Land adjoining St Athan Road
Land Contamination: The site is located over a principal aquifer. Any development would need to consider the hydrological setting of the site and vulnerability of pollution.

Rural Affordable Housing Led Sites
HG4 (1) Land to the East of Colwinston
Land Contamination: The site is located over a principal aquifer. Any development would need to consider the hydrological setting of the site and vulnerability of pollution.

Major Employment Allocations
SP14 (1) Land east of Cardiff Airport, Rhoose
Protected Species and Protected Sites: The site is within close proximity (360m) of Barry Woodlands SSSI and there also appears to be significant potential for the site to support dormouse, GCN, otter and water vole. There are large areas of semi-natural habitats associated with this site including woodland, mature hedgerow and watercourses. These should be retained and significantly buffered from development. Connectivity between the
site and the wider environment should also be maintained. It is therefore currently not possible to advise whether the full aspirations of the site could be fulfilled.
Land Contamination: Given previous land use at site, a Preliminary Risk Assessment would be required at planning application stage to determine risk of land contamination.

SP14 (2) Land south of Port Road (Model Farm), Rhoose
Land Contamination: Given previous land use at site, a Preliminary Risk Assessment would be required at planning application stage to determine risk of land contamination.

SP14 (3) Bro Tathan Aerospace and Business Park
Protected Species: The site is located within an important area for GCN and dormice. As mentioned, this area would benefit from spatial planning of biodiversity provision at a
greater scale to better inform allocation.
Land Contamination: Given previous land use at site, a Preliminary Risk Assessment would be required at planning application stage to determine risk of land contamination.

SP14 (4) Land to the South of Junction 34 of the M4, Hensol
Protected Sites: The site is located directly adjacent to Ely Valley SSSI. Given the biodiversity interest at the site, previous applications at the site include planning
commitments to conserve and enhance grasslands habitats on the site. These commitments have not yet materialised and the requirement for these provisions should be noted within the LDP.
Flood Risk: The site is located partially within Flood Zone 3 for Sea. We advise that an FCA will be required at project level to determine any flood risk implications at the site.

Local Employment Allocations
SP14 (5) Atlantic Trading Estate, Barry
Land Contamination: Given previous land use at site, a Preliminary Risk Assessment would be required at planning application stage to determine risk of land contamination. The site is located over a principal aquifer. Any development would need to consider the hydrological setting of the site and vulnerability of pollution.
Marine: An adjacent watercourse forms a hydrological link to the Severn Estuary EMS. A HRA at project level will therefore be required.

SP14 (6) Windmill Park, Hayes Road, Barry
Land Contamination: Given previous land use at site, a Preliminary Risk Assessment would be required at planning application stage to determine risk of land contamination. The site is located over a principal aquifer. Any development would need to consider the hydrological setting of the site and vulnerability of pollution.
Flood Risk: The site is located partially within Flood Zone 3 for Sea. We advise that an FCA will be required at project level to determine any flood risk implications at the site.
Marine: An adjacent watercourse forms a hydrological link to the Severn Estuary EMS. A HRA at project level will therefore be required.

SP14 (7) Vale Business Park, Llandow
Land Contamination: Given previous land use at site, a Preliminary Risk Assessment would be required at planning application stage to determine risk of land contamination.

SP14 (8) Land at Llandow Trading Estate
Land Contamination: Given previous land use at site, a Preliminary Risk Assessment would be required at planning application stage to determine risk of land contamination.

6. Habitats Regulations Assessment (HRA)
Marine and Coastal Physical Processes
Coastal Squeeze
We note that coastal squeeze has been screened in and taken through to Appropriate Assessment where a conclusion of no adverse effect was reached. The justification for this is that it “is unlikely that the Vale of Glamorgan RLDP will allocate many developments on
greenfield sites adjoining the estuary”.
We also note that Policy CC6 specifically relates to Coastal Defences and Shoreline Management, with reference to the Shoreline Management Plans. We recommend the use of NRW’s Assessment of Coastal Squeeze at the project level for anyone proposing to
undertake works to coastal structures.

Loss of Functionally Linked Habitat
As part of the Preferred Strategy consultation, we advised that consideration was given to potential impacts on migratory fish features of the Severn Estuary EMS. In particular, we referenced the River Ely and its tributaries providing supporting habitat for essential life cycle processes of some or all the diadromous fish species.
Within the deposit plan HRA, it is noted that likely significant effects to the migratory fish features of the Severn Estuary EMS has been ruled out, as none of the sites allocated in the RLDP lie in close proximity to the River Ely and connected watercourses. We therefore
agree with this conclusion.
In relation to bird features, Table 8 of the Appropriate Assessment identifies many key sites and allocations with high to medium potential for functional linkage to the Severn Estuary EMS. We note that loss of functionally linked habitat has been screened in and taken through to Appropriate Assessment where a conclusion of no adverse effect was reached. The justification for this is the inclusion of ‘Policy DNP8 – Severn Estuary Recreational
Pressure’ within the deposit plan.

Policy DNP8
We advise that clarification is needed in relation to this policy, as while we welcome the supporting text regarding functionally linked land outlined in paragraph 6.76 of the HRA, the policy is mainly focused on recreational pressure and is titled as such. We also note a discrepancy between the policy wording in paragraph 6.76 and Policy DNP8 in the deposit plan itself.

Visual and Noise Disturbance (During Construction)
Within the deposit plan HRA, visual and noise disturbance has been screened in and taken through to Appropriate Assessment where a conclusion of no adverse effect was reached. The justification for this is through the inclusion of recommendations outlined in 6.83 of the HRA to the supporting text of Policy SP20, which we welcome.
We also welcome the recommendation in relation to potential functionally linked land as outlined in paragraph 6.84 of the HRA.

Recreational Pressure
Within the deposit plan HRA, recreational pressure has been screened in and taken through to Appropriate Assessment where a conclusion of no adverse effect was reached. Again, the justification for this is the inclusion of ‘Policy DNP8 – Severn Estuary Recreational Pressure’ within the deposit plan, which as above, we advise needs
clarification.
We note that no visitor data has been collected from access points within the Vale of Glamorgan, but we welcome reference to the visitor surveys undertaken by
Monmouthshire and Torfaen, as well as the 2022 visitor survey commissioned by Stroud District Council.
We note that paragraph 6.25 of the HRA states that “three Key Sites and several other housing allocations lie within the 12.6km core recreational catchment that has been
deemed most appropriate for the Severn Estuary SAC/SPA/Ramsar”. However, we also note that Table 6 in the HRA only includes two Key Sites requiring mitigation, with KS3 being omitted. We advise that clarification is needed at the project level as to whether developments are situated within the 12.6km catchment area.

7. Strategic Flood Consequence Assessment (SFCA)
We have reviewed the submitted SFCA and agree with the scope of the assessment made.
We note there is currently an upper catchment Natural Flood Management (NFM) / Nature Based Solutions (NbS) project on the Cadoxton to reduce flood risk to Dinas Powys, Any updated SCFA should have regard to NFM schemes being progressed in their area and
proposals should be clearly outlined in the Development Plan (in accordance with TAN 15 2025).

8. Green Infrastructure Strategy (GIS)
We understand that the published GIS has not been updated to reflect the latest stage of the deposit plan and refers only to the preferred strategy stage (para 2.2.3). We previously provided advice on the Green Infrastructure Assessment (GIA) (re: CAS-252087-F0H1, dated 14th May 2024) which is included within the GIS. We refer you to these comments, noting that the GIS will be kept under continual review (para 1.2.5).

Vale of Glamorgan Replacement Local Development Plan (RLDP) 2022-2037
Thank you for consulting Welsh Water on the Vale of Glamorgan Deposit LDP, we appreciate and welcome the opportunity to engage in the Local Development Plan process.
Settlement boundaries
SSC1 – development within settlement boundaries
We welcome the requirement for new development to make efficient use of land and benefit from existing infrastructure provision or, where necessary, make provision for new infrastructure without any unacceptable effect on the natural environment (10).
Housing delivery
HG1 - housing allocations
A. Key sites (Policy HG1 KS1-5)
Our representation on the above sites are included in appendix 1.
B. Housing allocations (HG1 (1) to HG1 (9))
Our representation on the above sites are included in appendix 1.
C. Major landbank sites (HG2 (1) to HG2 (5))
These sites are existing commitments and Dwr Cymru Welsh Water has made representations on the planning applications submitted for these sites.
D. Housing led redevelopment opportunity (HG3 (1))
Our representation on the above site is included in appendix 1.
E. Rural affordable housing led sites (HG4 (1) to HG4(4))
Our representations on the above sites are included in appendix 1.
Our representations on the proposed allocated sites are included in appendix 1. Where planning applications have already been submitted and are pending a decision, we have made representations during the planning application consultation process regarding the capability of our infrastructure to accommodate the proposed development. If capacity does not exist within our infrastructure to accommodate the demands arising from a development site, the planning authority can make planning permission conditional upon there being adequate infrastructure available to cater for the development. A developer has a right to connect to our sewerage networks provided that a development site benefits from planning permission and there are no overriding planning conditions attached to the permission that controls the location or timing of that physical connection.
Gypsy and traveller accommodation (GT)
SP9 - gypsy and traveller site provision
Our representation on the site allocation is included in appendix 1.
Retail, commercial and service centres (RCS)
SP12 - retail floorspace provision
Our representations on the site allocations are included in appendix 2.
Community infrastructure (CI)
SP13 - community infrastructure and planning obligations
We support the provisions within the policy that the Council will secure new and improved community infrastructure where appropriate and within a timely manner, and the specific reference to utilities infrastructure. Where existing water and sewerage infrastructure requires reinforcement to serve a development it must be provided as part of the development to mitigate any adverse impacts. In circumstances where the development generates the need for infrastructure improvements that are not programmed for delivery by infrastructure providers then it must be funded by the development. Therefore, it is important for developers to engage early with relevant infrastructure providers, including the statutory sewerage and water undertaker. We welcome that the policy states that improved infrastructure must be undertaken in a timely manner. The delivery of reinforcements to the sewerage and water networks can controlled either through planning condition or a commercial agreement between the developer and Welsh Water.
Adequate potable water supply and drainage infrastructure is key to ensuring new development sites are sustainable, viable and deliverable. Hydraulic modelling assessments (HMA) may be required to determine an adequate point of connection to the water network and/or public sewers, and developers would be strongly recommended to fund investigations at pre-planning stage. Once commissioned and completed the HMA would identify suitable connection points and/or the necessary reinforcement works required to accommodate the development (for example upsizing sewers/water mains, additional storage tanks etc). In certain circumstances surface water removal could be an alternative option for allocations where foul sewer HMAs are being requested, and we would welcome early engagement with the site developer.
The reinforcements required to the network would be established by the HMA and costings would be provided at detailed design stage. The developer would need to fund a scheme by way of the requisition provisions of the Water Industry Act or via a legal/commercial agreement with Welsh Water.
Community facilities
CI3 – new community facilities
Our representations on the site allocations are included in appendix 2.
CI5 - cemetery and crematorium provision
Our representation on the site allocation is included in appendix 2.
Productive and enterprising places
SP14 - employment growth
Our representations on the site allocations are included in appendix 2.
We support sustainable economic development, however the LPA and potential developers should be aware that the obligations of a water and sewerage undertaker only extend to the ‘domestic’ supply part of an employment development (sinks, toilets, kitchen facilities etc). We are not obliged to provide potable water for use in any industrial process. Where an employment development results in higher demands of water supply and/or trade effluent discharge consent, under Section 118 of the Water Industry Act 1991, we recommend and welcome early consultation with developers. The capability of our infrastructure to service future employment allocations will be assessed when the potential demands arising from the developments are known.
EMP1 - employment regeneration opportunity areas
Our representations on the site allocations are included in appendix 2.
Climate change and transition towards net zero (CC)
SP16 - climate change mitigation and adaptation
We are supportive of this policy as the protection of water resources are key in ensuring we maintain a safe, healthy and reliable water supply. Incorporating water efficiency measures into developments will help minimise adverse impacts on localised and wider water supply networks including the quality of water resources.
We are also pleased that the policy includes particular emphasis on the importance of sustainable urban drainage systems (SuDS), in conjunction with Schedule 3 of the Flood and Water Management Act 2010. The tackling of surface water at source is a vital component of sustainable development and will mitigate against overloaded sewers which can ultimately lead to flooding. Disposing of surface water in a sustainable manner by ensuring that it does not communicate with the public sewerage network, including rainwater harvesting systems, protects the environment and assists in ensuring that there is sufficient capacity in the public sewerage network for foul-only flows from development sites.
SP19 – Green Infrastructure
In conjunction with SAB applications, under Schedule 3 of the Flood and Water Management Act 2010, we welcome provision within this policy to integrate green infrastructure with sustainable drainage systems.
Environmental protection
DNP5 – environmental protection
We welcome provisions within the policy to protect the natural environment from unacceptable impact from pollution of land, surface water, ground water and the air as well as flooding risks.
We hope that the above will assist you as you continue to progress the LDP. If you require any further information, then please do not hesitate to contact us on 0800 917 2652 or forward.plans@dwrcymru.com.

Appendix 1 – HG1 Housing Allocations, SP9 Gypsy & Traveller Site
Our representations on site allocations are provided in the table below. The following caveats are applicable to all sites:
• In accordance with the Water Industry Act 1991, Welsh Water retains rights of access to its assets at all times. Where there are sewers and/or water mains crossing sites then protection measures in respect of these assets will be required, usually in the form of an easement width or in some instances a diversion.
• Where insufficient hydraulic capacity exists within the public sewerage network or water supply network to accommodate/serve a development site, hydraulic modelling assessments (HMA) may be required, and developers would be strongly recommended to fund investigations during pre-planning stages. The findings of the HMA will identify the extent of any reinforcement required to accommodate the development, which can be procured via the requisition provisions of the Water Industry Act 1991 (as amended). If the sewerage network system in the locality is currently at capacity, there may be an opportunity to overcome our concerns by delivering a surface water removal scheme. This approach would ensure that there is no net increase in volume of flows communicating with the public sewer network, and therefore no further detriment to the public sewer network downstream of the development.
• In some instances, off-site water mains or public sewers may be required to connect to a suitable point on the existing networks at the developers’ cost. We may seek to control points of connection to the public sewerage network via appropriate planning conditions. Where assets need to be laid over private land, developers will need to comply with the requisition provisions of the Water Industry Act 1991.
• If there is limited or no capacity available at a Wastewater Treatment Works (WwTW), developers may need to fund a Developer Impact Assessment (DIA) to identify required reinforcement works. In these instances, a commercial agreement would be required between the developer and Welsh Water to deliver the necessary reinforcement works.
• Where capacity is currently available in the water supply network to accommodate development, we reserve the right to reassess our position at the time of the formal application for the provision of new water mains under Section 41 and Section 51 of the Water Industry Act (1991) to ensure there is sufficient capacity available to serve the development without causing detriment to existing customers’ supply as demands upon our water systems change continually.
• Please note the below comments are subject to change as the LDP progresses and/or as planning applications are submitted.

See tables in attachment for site specific comments.

Appendix 2 - Employment sites & other uses
Capacity comments for employment allocations can only be provided once the type of development and occupier/end-user of a site is known. Once requirements are confirmed, usually through the planning application process, further assessments will be undertaken. High-level comments are provided in the table below regarding any watermains/sewers crossing the proposed allocations, and the WwTW catchment that the sites are located within.
The following provisions are applicable to all allocated employment sites:
• the obligations of a water and sewerage undertaker extend to ‘domestic’ supplies only. We are not obliged to provide potable water for use in any industrial process. Where an employment allocation results in higher demands of water supply and/or trade effluent discharges we recommend and welcome early consultation with Welsh Water.
• The individual plots available for development can represent a substantial area of land for which the potential demands upon our assets are unknown at present. It is essential that we understand these demands to allow us to assess the impact on our assets. It may be necessary for water and/or sewerage hydraulic modelling assessments (HMAs) to be undertaken at the developer’s expense to establish where the proposed development could connect to the existing networks, and to identify any required infrastructure reinforcement works. Water mains and/or sewerage infrastructure required for any potential development site can be acquired through the requisition provisions of the Water Industry Act 1991 (as amended).
• In accordance with the Water Industry Act 1991, Welsh Water retains rights of access to its assets at all times. Where there are water mains and/or sewers crossing sites then protection measures in respect of these assets will be required, usually in the form of an easement width or in some instances a diversion of the asset.
• Where there is limited or no capacity at a WwTW, dependant on the scale and pace of development, developers may need to fund a Developer Impact Assessment (DIA) to identify required reinforcement works. In these instances, a commercial agreement would be required between the developer and Welsh Water to deliver the necessary reinforcements.
• If any development site gives rise to a new discharge (or alters an existing discharge) of trade effluent, directly or indirectly to the public sewerage system, then a Discharge Consent under Section 118 of the Water Industry Act 1991 is required from Welsh Water. Please note that the issuing of a discharge consent is independent of the planning process and a consent may be refused despite planning permission being granted.

See tables in attachments for site specific comments