Guidance for the Management of Coastal Vegetated Shingle 
 
     HomeThe HabitatPressuresStatesHAPManagement • Restoration • Coastal DefenceLegislationMonitoringCase Studies  
      RestorationStabilisationDestabilisationRestoring vegetation
        

 

Shingle beaches - State 1, Erosional to State 2, Accretional or semi-stable

Stabilisation of shingle beaches is normally associated with attempts to maintain their coastal defence capabilities. Thus the techniques employed involve the use of engineered structures and/or beach nourishment. For both approaches the primary aim is to maintain the beach in its existing position. The methodologies used to create stability or at least hold the beach in a position where it affords protection to the hinterland can be broken down into two basic approaches:

  1. Preventing erosion

Traditionally the approach adopted is concerned with 'improving' the sea defence capability of the beach or structure by building groynes and breakwaters (coastal defence structures). This may be accompanied by beach reprofilling.

  1. Promoting accretion

Promoting accretion requires there to be a suitable source of new material to 'feed the beach'. This can include beach nourishment using material derived from sources outside the sediment cell within which the shingle structure exists. Other approaches are concerned with the reuse of material by recycling or 'by-pass' from the down drift to the updrift side where long shore movement takes place.

The direction of movement is as shown in the Figure opposite. The preferred direction of movement from a sea defence perspective is shown in the figure in blue. Note that in a few cases, and for the restoration of more natural shingle forms, a reversal of the process to restore shingle movement may be considered i.e. State 2 to State 1 by allowing natural processes such as realignment to dominate.

 

Caption: The principle route for creating or re-creating stability on shingle beaches.

 

Undertaking engineering works designed to prevent erosion can, potentially at least, also provide the means for creating more stable areas where vegetation becomes established. Both toe protection along the base of the sea walls and breakwaters can be used to reduce scour. Buried revetments, e.g. at Sovereign Harbour in Eastbourne have helped to build up the base of the beach. As a result less material is needed to build the shingle up to a level suitable for flood protection. The top of the ridge is broader, and hence more suitable for the development of vegetation communities. At Pevensey investigations are taking place into the use of tyre bales for a similar purpose. These may have the added advantage that the bales are not solid structures and can provide gaps for the shingle to penetrate and hold the beach together, as well as voids for root systems.

Summary guidance - creating stability, engineering approaches

It is clear that beaches can be stabilised using artificial structures. Because these are associated with coastal protection measures, other activities usually take place, such as beach replenishment and/or reprofiling. As a result the establishment of new shingle communities is rare. The case of Black Rock where stable vegetated shingle developed following building coastal protection structures may be an isolated example.

 
Guide to colour codes 
Jargon buster 
Key reading 
site map 
top of page  
© English Nature 2003