Guidance for the Management of Coastal Vegetated Shingle 
 
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Shingle - State 2, Accretional or semi-stable to State 1, Erosional

A key issue when considering the restoration of coastal shingle lies in determining the principle aims, and whether these are for sea defence purposes or nature conservation and amenity. Whilst sea defence requirements seek to create stable structures, there is an increasing recognition of the value of allowing the natural dynamic to reassert itself. It has been argued that this can be a healing force in degraded systems, especially where the surface shingle has been removed or grossly disturbed (Doody 1992b).

 

Caption: Allowing 'nature to take its course'. A route to restoring damaged and degraded shingle structures by allowing the natural dynamic to become re-estabished.

Reversing the usual policy of protecting eroding beaches i.e. moving from the paradigm of creating stability (moving from State 1 - State 2) and allowing erosion to take place may be difficult to implement given the history of intervention and attitudes towards 'giving up land to the sea'.

A number of scenarios where this approach has or could be implemented are identified:

  1. breach in a shingle bar with associated 'roll-back' and flooding of the land behind. An example of this is Porlock Weir on the Somerset coast;
  2. rollover of a shingle barrier onto terrestrial land (including grazing marsh), tidal areas (including lagoons) or other coastal habitats, such as is occurring at Slapton on the south Devon coast;
  3. remobilisation of progressive ness formation which has been arrested by artificial interference with its natural progression. An example is Dungeness where erosion takes place from west to east as the ness attempts to move in an easterly direction. Shingle recycling is used to keep the beach in front of the power station in place.

Comment: At the present time this is a little used and little understood method of restoration. However, it is implicit in the Habitat Action Plan for shingle that for some 'protected' areas the dynamics within individual sites should be allowed to become re-established. Given the major losses that have occurred at many of the larger sites, this approach could generate considerable conservation benefit. Discussions are currently taking place at Orfordness and Cley-Salthouse where consideration is being given to the cessation of beach nourishment.

References

Doody, J.P. 1992b. Sea defence and nature conservation: threat or opportunity. Journal of Aquatic Conservation, 2., 275-283. Abstract...

 
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