Guidance for the Management of Coastal Vegetated Shingle 
 
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Coastal defence - summary of human actions

Sea defence (the protection of land from flooding) and coastal protection (protection of land from erosion) can both apply to shingle beaches and structures. Building structures (e.g. sea walls and groynes) to 'improve' their coastal defence capability has occurred on or behind many shingle shores. To some extent the value of shingle to coastal defence is not recognised until it is too late, as for example the case of Hallsands (Annex 02) vividly illustrates.

There are four broad approaches to the stabilisation of shingle beaches:

  1. erection of structures such as groynes and beakwaters;
  2. beach reprofiling;
  3. beach nourishment;
  4. recycling shingle material.

Each of these has a different impact on the nature of the beach, its ability to sustain any nature conservation interest and coastal defence capability. In summary defence works may result in changes to the movement of material both on and offshore and alongshore. In its turn erosion due to the interruption of long-shore drift can result in the need for protection further along the beach. These can all have important consequences for the natural dynamics of the habitat. The structures themselves can also cause loss of habitat. Beach nourishment, feeding and re-profiling are also significant activities, the former having both positive and negative impacts on the habitat, the latter almost always having negative effects. Beach recycling represents an ongoing activity, which may have a negative impact on many designated sites.

Guidance: Shingle beaches are mobile structures developed in dynamic high-energy environments. As such they are themselves highly efficient dissipators of wave energy and may provide an important natural defence function. This role should be more readily recognised when considering coastal defence strategies.

 
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