Atlantic, Baltic and Arctic sand beach
Quick facts
Red List habitat type | code RLB1.1a |
---|---|
Threat status | |
Europe | Vulnerable |
EU | Vulnerable |
Relation to |
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Source | European Red List habitat factsheet |
European Red List of habitats reports | |
European Red List of habitats (Excel table) |
Summary
The beaches along the west-coast of the Atlantic Ocean, the North Sea and the Baltic form a transition between the marine and terrestrial world. The lower parts of the beach (sublittoral/littoral foreshore), which are inundated most of the day, are considered under marine habitats. The higher (supralittoral or – in the Baltic – geolittoral) part, only rarely inundates during extreme high tides, is considered under terrestrial types. Sand beaches are found along sedimentary coasts, where the sediments deposited by waves and currents have a particle size of about 0.1 to 2 mm. Sedimentation of finer coastal particles results in salt marshes(habitat A2.5b and c). Sedimentation of coarser material results in shingle shores (habitat B2.1-3a), while shores with particular large cobbles and boulders (about >100 mm) are considered under rocky shores and cliffs (habitat B3.1_3a).
Sand beaches form a very dynamic habitat under the constant influence of disturbance by sea water, wind and salt spray, causing erosion and accretion, and by amounts of organic matter brought by the tides. The sediment is supplied from erosion of the coasts, carried shoreward from the sea bottom or brought in by rivers. On Iceland and Macaronesian islands sand beaches may be made up of black, volcanic (basaltic) sediments. In the Baltic tidal influence is limited and salinity is relatively low; here beaches are more influenced by freshwater.
Vegetation is scarce in space and time , restricted to the backshore (higher beach) and mainly restricted to litter deposits on the high-tide line. Typical species of such drift-lines are a range of Atriplex species (Atriplex caltheca, Atriplex glabriuscula, Atriplex laciniata, Atriplex littoralis, Atriplex longipes, Atriplex patula, Atriplex prostrata), Cakile maritima (incl. different subspecies) and Salsola kali. Beta vulgaris subsp. maritima is also frequently present, and grows on shingles as well. These are all annuals, adapted to dynamic, yearly changing conditions. Most of them have deep rooting systems in the freshwater floating on the deeper marine water. Seeds are dispersed by sea or wind and they have adaptations to deal with high salt concentrations. One of the few common perennial species on the Atlantic and North Sea beaches is Honckenya peploides, growing also in primary and white dunes, and often accompanied by primary dune species, like Elytrigia farctus subsp. boreoatlantica, Leymus arenarius, Ammophila arenaria and Calystegia soldanella. On the – less dynamic – Baltic Sea sand beaches perennial species are more common, including species associated with primary and white dunes, as well as helophytic species of wet conditions (Bolboschoenus maritimus, Scirpus tabernaemontani). Other typical species in the wet, lower parts of the Baltic beaches are often associated with pioneer habitat along rivers, like Potentilla anserina, Ranunculus sceleratus, Polygonum hydropiper, Rorippa palustris, Juncus bufonius, Polygonum lapathifoliym, Chenopodium rubrum and Agrostis stolonifera. Potentilla anserina is also common in boreal driftlines, for example in Iceland, Norway and Scotland, where it is accompanied by Mertensia maritima. Helophytic species may be found on Atlantic beaches as well, but only rarely, in places where freshwater leaches out of high dunes and forms streams to the sea. Also Salix shrubs may grow in such conditions. In the bay of Biscaye, Euphorbia peplis can grow on the upper part of sand beaches.
A group of typical invertebrates of beaches is associated with the drift lines and its vegetation, while several other invertebrates live oligophagous on characteristic plants species, like on Cakile maritima. Several bird species breed on beaches (for example ringed plover, little tern), often in places with many shells, but only in those places where there is no disturbance by tourism. The Sanderling (Calidris alba) is a typical feeder in the surf on the beaches during its migration.
Indicators of good quality:
The following characteristics are considered as indicators of good quality:
· Presence of drift-line vegetation
· Forming gradients and progressive morphologic profile towards primary dunes
· Presence and success of breeding birds in spring/summer
Threat status
Synthesis of Red List assessment
EU | |
Red List Category | Red List Criteria |
Vulnerable | C/D1 |
Europe | |
Red List Category | Red List Criteria |
Vulnerable | C/D1 |
Confidence in the assessment
Pressures and threats
- Urbanisation, residential and commercial development
- Discontinuous urbanisation
- Human intrusions and disturbances
- Trampling, overuse
- Intensive maintenance of public parcs / Cleaning of beaches
- Pollution
- Oil spills in the sea
- Marine macro-pollution (i.e. plastic bags, styrofoam)
- Invasive, other problematic species and genes
- Invasive non-native species
Habitat restoration potential
Trends in extent |
|
Average current trend in quantity |
|
Decreasing ![]() |
Decreasing ![]() |
EU28 | EU28+ |
Trends in quality |
|
Average current trend in quality |
|
Decreasing ![]() |
Decreasing ![]() |
EU28 | EU28+ |
Conservation and management needs
List of conservation and management needs
- Measures related to wetland, freshwater and coastal habitats
- Restoring coastal areas
- Measures related to spatial planning
- Establish protected areas/sites
- Legal protection of habitats and species
- Manage landscape features
- Measures related to urban areas, industry, energy and transport
- Managing marine traffic
Distribution
Geographic occurrence and trends
EU28 | Present or presence uncertain | Current area of habitat (Km2) | Recent trend in quantity (last 50 years) | Recent trend in quality (last 50 years) |
---|---|---|---|---|
Belgium | Present | 1.8 | Stable | Stable |
Denmark | Present | Unknown | Unknown | Unknown |
Finland mainland | Present | 8 | Decreasing | Decreasing |
Aland Islands | Present | 8 | Decreasing | Decreasing |
France mainland | Present | 2875 | Decreasing | Decreasing |
Germany | Present | 150 | Decreasing | Stable |
Ireland | Present | 1 | Decreasing | Decreasing |
Latvia | Present | 1 | - | Decreasing |
Lithuania | Present | 2 | Decreasing | Stable |
Netherlands | Present | 22.5 | Increasing | Stable |
Portugal mainland | Present | 14 | Decreasing | Decreasing |
Spain mainland | Present | 70 | Decreasing | Decreasing |
Sweden | Present | 12 | Stable | Stable |
United Kingdom | Present | 1322 | Unknown | Unknown |
Northern Island | Present | 1322 | Unknown | Unknown |
Poland | Present | 1 | Unknown | Unknown |
EU28 + | Present or presence uncertain | Current area of habitat (Km2) | Recent trend in quantity (last 50 years) | Recent trend in quality (last 50 years) |
---|---|---|---|---|
Faroe Islands | Present | Unknown | Unknown | Unknown |
Kaliningrad | Present | Unknown | Unknown | Unknown |
Norway Mainland | Present | Unknown | Unknown | Unknown |
Extent of Occurrence, Area of Occupancy and habitat area
Extent of Occurrence (EOO) (Km2) | Area of Occupancy (AOO) | Current estimated Total Area | Comment | |
---|---|---|---|---|
EU28 | 3564650 | 2672 | 3380 | Data missing from Denmark and some uncertancies what the data represent from some countries |
EU28+ | 2775 | 3380 | Data missing from Norway |
EOO = the area (km2) of the envelope around all occurrences of a habitat (calculated by a minimum convex polygon).
Characteristic species
Legal status
Relation to other habitat types mentioned in legal instruments
Vegetation types
Relation to vegetation types (syntaxa)
Not availableOther classifications
Classification | Code | Habitat type name | Relationship type |
---|---|---|---|
EUNIS Habitat Classification 200711 | B1.1 | Sand beach driftlines | overlap |
EUNIS Habitat Classification 200711 | B1.2 | Sand beaches above the driftline | overlap |