February 2022
1. Introduction
All planning documents are required to consider whether they will have a significant adverse effect on the integrity of internationally designated sites of nature conservation importance including “European sites” which are designated within the local and wider area. This consideration is undertaken through a process known as Habitats Regulations Assessment (HRA) which is a requirement of the Conservation of Habitats and Species Regulations (2010) (the Habitats Regulations).
European sites provide important habitats for rare, endangered or vulnerable natural habitats and species of exceptional importance. These sites consist of Special Areas of Conservation (SACs, designated under the EU Directive 92/43/EEC on the conservation of natural habitats and of fauna and flora (Habitats Directive)) and Special Protection Areas (SPAs, designated under EU Directive 2009/147/EC on the conservation of wild birds (the Birds Directive)).
Government policy, National Planning Policy Framework (NPPF, 2021) and Circular 06/05 (ODPM, 2005) requires that Ramsar sites (designated under the International Wetlands Convention, UNESCO, 1971) are treated as if they are fully designated European sites for the purposes of considering development proposals that may affect them.
There are two stages of HRA; the screening which determines the likelihood of significant effects; and a full HRA which is only undertaken if the screening indicates that significant effects are likely or cannot be discounted at screening stage. Where a full HRA is carried out, a plan may only be adopted after having ascertained that it will not have significant adverse effects on the integrity of the site concerned.
2. Purpose of this report
This assessment has been undertaken to identify whether any European sites exist within or in proximity to the neighbourhood area which could potentially be affected by any policies within the Neighbourhood Plan.
This assessment draws on the conclusions of relevant HRA screening and detailed assessment reports that have already been undertaken for the Brighton & Hove City Plan area, which includes the Brighton Marina area. Its purpose is therefore to summarise these reports and consider whether the existing HRAs are sufficient to assess the effects of the Brighton Marina Neighbourhood Plan, or whether the Brighton Marina Neighbourhood Plan should carry out its own HRA screening and assessment.
3. Local European Sites
The Castle Hill SAC lies partly within the city’s boundary and partly within Lewes District Council’s boundary, although is located entirely within the South Downs National Park Authority Area. There are no Special Protection Areas or Ramsar sites within the city’s boundary. There are also some European sites within 20km of the city including Lewes Downs SAC, Ashdown Forest SAC/SPA and Arun Valley SPA. The Castle Hill SAC designation relates to the presence of chalk grassland and some rare and scarce species; the Lewes Down designation also relates to the presence of chalk grassland and some rare and scarce species; the Ashdown Forest designation is due to the largest single continuous blocks of lowland heath in the southeast; and the Arun Valley designation is due to the wintering population of tundra swans. There are no SACs or SPAs located within the Brighton Marina Neighbourhood Plan area. The Castle Hill SAC is in closest proximity to the Neighbourhood Area, located approximately 5,000m from the boundary.
4. Brighton Marina Neighbourhood Plan
The Brighton Marina NP does not allocate any sites for housing or any other uses. The policies are focused on design, open space/public realm, the natural environment, energy use, is supportive of retail, commercial, leisure and community facilities and housing where it delivers the Strategic Allocation allocated in City Plan Part 1.
5. Brighton & Hove City Plan Part 1 – HRA screening
An HRA screening was undertaken on the City Plan Part 1 at various stages of its development, with the most recent at Proposed Modification stage 2014, relating to the adopted City Plan Part 1 (2016). This assessed the potential for impacts of all City Plan Part 1 policies on the Castle Hill SAC and on European sites outside the city including Lewes Downs SAC, Ashdown Forest SAC & SPA and Arun Valley SPA.
The screening included an initial assessment of the potential for environmental impacts resulting from each policy that needed to be considered by the HRA screening. The assessment concluded that DA2 could result in increased resource use, which could have implications for water and hydrocarbons, and could result in moderate increase in traffic volume and air pollutants, and increased recreational pressure.
The adopted City Plan set out a minimum housing target of 13,200 dwellings to be delivered over the plan period, as well as other quantums of development. The HRA screening assessed the likely impacts of the proposed amounts of development set out in the City Plan and concluded that the possible impacts amount to water abstraction, air pollution and recreational pressure. Of these:
- Water abstraction would not have a significant effect on any European site because there are no such sites which are vulnerable to water abstraction within the water catchment area of Brighton and Hove.
- Despite policies which promote travel choice and minimise air pollution, it is still possible that air pollution may worsen as a result of the City Plan Part 1. However localised air pollution of this nature would not have a significant effect on any European site, according to Natural England advice.
- Recreational pressure on downland in the vicinity of Brighton and Hove may increase as a consequence of the City Plan Part 1. However only one of the European sites assessed is vulnerable to recreational pressure (Ashdown Forest) and studies elsewhere have shown that this site is far enough away from Brighton and Hove to safely conclude that there would be no significant recreational impact on it as a result of the City Plan Part 1.
Therefore, the HRA screening on the City Plan Part 1 discounted all possible significant impacts that would affect the designations of the SACs or SPA and therefore did not progress to a full Habitats Regulations Assessment (Appropriate Assessment)
6. Brighton & Hove City Plan Part 2 – HRA screening and assessment During the preparation of City Plan Part 2, an updated Habitats Regulations screening was undertaken to reconsider the effects of the growth associated with the entire City Plan Part 1, in combination with growth anticipated from other areas, as well as effects arising from draft City Plan Part 2. This screening assessment discounted the likelihood of significant effects on Castle Hill, Lewes Downs, Arun Valley and Pevensey Levels European sites.
However the screening could not discount the likelihood of significant adverse effects of the Plan on the Ashdown Forest SAC/SPA, therefore a detailed assessment of air quality impacts (Appropriate Assessment) on Ashdown Forest was undertaken. This involved modelling the potential impact of traffic flows and vehicle exhaust emissions associated with planned development in Brighton & Hove in combination with neighbouring local authorities on the Ashdown Forest SAC. The model covered the period to 2033 and therefore allowed for a higher amount of housing than the City Plan target. The analysis concluded that the expected growth in Brighton and Hove to 2033 (as identified in the adopted City Plan Part 1 and emerging City Plan Part 2) makes virtually no contribution to changes in ammonia concentrations, NOx concentrations or nitrogen deposition within Ashdown Forest SAC.
The City Plan housing target set out in Policy CP1 is to deliver at least 13,200 new homes over the period 2010-2030. The model assessed traffic growth to 2033 from a base date of 2017, assuming delivery of 11,845 dwellings and 111,500 sqm employment floorspace in Brighton & Hove over the period 2017-2033. In addition, 3,000 net dwellings were already built in Brighton & Hove between 2010-2017 which will already be included within the traffic data for the baseline year (2017).
The detailed assessment confirmed that growth resulting from City Plan Part 1 and City Plan Part 2, with an increased trajectory to 2033, would not result in adverse effects that would affect the integrity of the Ashdown Forest SAC/SPA, either alone or in combination with growth from other areas.