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Coastal Habitats

NE; CCW; National Coastal Consultants; SNH

WHAT IS ALREADY HAPPENINGWHAT COULD HAPPEN
Same confidence Medium Confidence   Same confidence Low Confidence  
  • Coastal habitats are being affected by changes to the amount of sediment being supplied and removed as a result of natural processes and human intervention.
  • Past human intervention and modification of coastal habitats means they have a reduced capacity to adapt naturally to climate change impacts.
  • Continued sea-level rise, and other climate change related factors are expected to have an impact on the extent, distribution and quality of various coastal habitats.

Coastal margin habitats are varied and present around the UK in complex mosaics. They depend on the supply and movement of sediment by both marine and Aeolian processes as well as other processes including cycles of vegetation succession.

Most coastal habitats exhibit a degree of successional change and have the potential to re-establish after extreme events, hence in an unmodified state they could be relatively resilient to some elements of climate change. The legacy of past intervention has resulted in a reduced capacity for adaptation to coastal change without significant intervention in some places. In particular the reduction in sediment supply is critical as it underpins coastal form and function.

Most of the coastal habitats are not currently in favourable condition, with recent reporting on conservation status highlighting the poor future prospects for many habitats, especially sand dunes, largely in the light of climate change impacts.

Coastal habitats provide an important contribution to coastal risk management and other ecosystem services. Their importance is recognised by conservation and landscape designations.

There are close interactions with landward ecosystems and hydrology, with transitional habitats contributing to the overall value.

The changes in future are difficult to predict with certainty because of the presence of coastal management structures. Sea-level rise and climate change will impact on the extent, distribution and quality of coastal habitats, interactions with other impacts such as nutrient deposition may occur.

Social resistance to change is high and adaptation measures are difficult to implement. Long-term sustainable approaches to risk management are needed, with some indication that this is increasingly recognised at a policy level. In addition, protected/designated habitats at the coast need more adaptable approaches in order to move from a 'preservation' ethic to a more dynamic means of conservation of form and function which will contribute to adaptation measures, and knowledge gaps in this area need to be addressed.

What is already happening: Medium

 

Rationale: we are already observing some changes on coastal sites in terms of changes to sediment budgets and changes in composition. There has not been as much emphasis on supralittoral coastal habitats as there has been on littoral habitats, but increasing evidence on sand dune systems.

What could happen: Low

 

Because coastal systems are highly complex and dynamic, with a legacy of intervention in many areas, there is likely to be lower confidence in predictions of future scenarios, there is also a lack of long-term data sets to indicate trends: more needs to be done on this across a wide range of coastal habitat types. This uncertainty requires careful consideration of the adaptation responses. What is certain is that the coast will change!

The top priority knowledge gaps that need to be addressed in the short term to provide better advice to be given to policy makers are:

General

  • Coastal change needs to be fully evaluated at a coastal cell level against the UKCP09 predictions for a wide range of climatic factors to improve confidence in predictions and reduce uncertainty. This needs to include the responses of key species across a range of habitats.
  • Successional processes in vegetation will be affected by climate and other factors such as nutrient deposition. The work in Wales on dunes indicates that there is a need for more information on the interaction of these factors, which is relevant to future management strategies.
  • The studies in progress in Scotland indicate that the relationship between the coastal habitats and the landward areas is not fully understood. More work is needed to inform measures to restore the coastal flood plain in order to plan for and enable effective adaptation to climate change.

Shingle

  • Whilst there is reasonable knowledge of the status and evolution of the major shingle structures much less is known about the long lengths of shingle beaches. Assess the status of shingle beaches in relation to changing sea levels, human activities and determine their vulnerability.
  • Impact of offshore dredging. There are differing views about the impact of offshore dredging on the coast. Given the importance of shingle foreshore to sea defence this issue needs research that is more active.
  • Restoring shingle vegetation is difficult and there is only very limited research. Increase the effort on this aspect of management.

Machair

  • Information needed for improved contingency and management planning is currently being developed via SNH commissioned and in-house research. Understanding a wide range of hydrological and topographical relationships will be important to inform the human response to both extreme events and longer-term trends.

Sand Dunes

  • A number of knowledge gaps have been identified regarding the understanding of the hydrological, chemical and physical processes of dunes and how these could be managed in the context of climate change. More information is also needed on the restoration of processes and habitats to enable more effective adaptive measures to be implemented. It is unlikely that dune systems will be stable. Expanding the work in Wales of Pye & Saye (2005) to the rest of the UK will help understand where the greatest changes could occur.
  • Guidelines for the ecohydrology of dune slacks have been produced by the Environment Agency in 2010 (Davy et al., 2010). Research gaps have been included in this guidance.

Maritime Cliffs

  • Information is needed on the impacts of potential increased erosion on invertebrate communities on cliff slopes.
  • The relationship between sediment supply from erosion of cliffs and transport to other coastal or marine habitats will become increasingly important to understand in the context of coastal management.
  • A UK-wide vegetation survey of maritime cliffs ideally using Phase II (National Vegetation Classification) methodology is needed.

Coastal grassland and heath

  • Particular areas where knowledge is missing is the extent and distribution of the habitat types; the impacts on species composition of climate change; management requirements and trends.

General

A review of the implications of sea-level rise for the UK (de la Vega-Leinhart & Nicholls, 2008) suggests that although the UK has the potential to adapt to sea-level rise, there are a number of barriers to implementation. For example, public acceptance of coastal change is still very low, and funding of innovative approaches is limited. The development of new Shoreline Management Plans in 2010 for England and Wales will help to direct the future public funding of coastal management, these plans are increasingly geared towards long-term sustainable solutions rather than a 'hold the line' approach. A number of 'pathfinder' projects in England have recently been announced by Defra which will explore a range of situations where coastal change is an issue for local communities.

Also in 2010, a revised beach management manual will be published to help guide engineers and other beach managers to more sustainable methods of managing flood risk on low-lying coasts.

The integration of coastal management with land-use and marine planning will become more important in future, under the broader context of Integrated Coastal Zone Management. The economic value of coastal habitats and coastal processes needs to be more widely understood and promoted: this is often difficult due to the public and political expectation that risk of flooding and erosion can and should be controlled.

There are a number of key researchers working on this issue of stakeholder dialogue and coastal change, for example the Tyndall Centre for Climate Change Research (Milligan et al., 2006)

Dune systems: The prospect of future morphological changes arising from climate / sea level change and changing patterns of coastal erosion and accretion, combined with changing attitudes away from fixed coast and flood protection towards coastal erosion and flood risk management, provides a significant opportunity to increase the geomorphological and ecological dynamism of dune systems. However, the evaluation of future management options needs to be carefully assessed on a site by site basis, taking into account the nature of local physical processes, sediment supply, likely long-term morphological evolution, and the present and possible future uses of the dunes themselves and the hinterland. Approaches to managing the landward movement of dune systems need to be developed (Pye et al., 2007). In view of the likelihood of increased beach steepening, rising sea levels and more frequent storm events in the coming decades, rates of frontal dune erosion are also likely to increase and 'hard' dune defences will become unsustainable in some areas. The future of dune golf courses will need to be addressed specifically in relation to this habitat.

Machair: The future of this habitat is totally interwoven with the role of traditional management. It appears to be very vulnerable to extreme events, and as is often the case, hard defences are called for after the event to reduce flood risk. This may not be sustainable in the long-term however.

Shingle: Flood and coastal erosion risk management relies largely on the ability of natural coastal processes to move and retain sediment within systems. In some areas there has been a decrease in shingle volume to sustain past flood risk management techniques, but new, more adaptive approaches which depend on natural processes are difficult for the public to accept.

Cliffs: it is estimated that on average, over the next 50 years 1 property per year will succumb to coastal erosion. Experience in places with rapid erosion form a focus for stakeholder dialogue on erosion risk management.

Coastal grassland and heath: Many of the key locations are within protected landscapes and as such play an important socio-economic role. Low- intensity agricultural management will play a key role in securing these habitats across their whole range, and needs to be addressed in agri-environment incentive schemes.

Rees, S., S. Angus, P. Rhind and J.P.Doody (2010) Coastal Margin Habitats in MCCIP Annual Report Card 2010-11, MCCIP Science Review, 21pp. www.mccip.org.uk/arc