Red List habitat classification > RL - Marine habitats > RLNEA - Atlantic > NEAA5.33 Marine Atlantic infralittoral sandy mud

Marine Atlantic infralittoral sandy mud

Quick facts

Red List habitat type code NEAA5.33
Threat status
Europe Near Threatened
EU Near Threatened
Relation to
Source European Red List habitat factsheet
European Red List of habitats reports
European Red List of habitats (Excel table)

Summary

Infralittoral, cohesive sandy mud, typically with over 20% silt/clay, in depths of less than 15-20 m. This habitat is generally found in sheltered bays or marine inlets and along sheltered areas of open coast. Tidal streams can vary from negligible to moderately strong (1-3kn). Six associated biotopes have been identified dominated by different species. 

Indicators of quality:

Both biotic and abiotic indicators have been used to describe marine habitat quality. These include; the presence of characteristic species (especially those which are sensitive to the pressures the habitat may face), water quality parameters, levels of exposure to particular pressure as well as and more integrated indices which describe habitat structure and function, such as trophic index, or successional stages of development in habitats that have a natural cycle of change over time. 

There are no commonly agreed indicators of quality for this habitat, although particular parameters may have been set in certain situations e.g. protected features within Natura 2000 sites, where reference values have been determined and applied on a location-specific basis.

Key driving influences and output processes of shallow sublittoral mud habitats that are likely to be sensitive to pressures and may be useful for monitoring to identify anthropogenic causes of change include habitat structure changes, removal of particular species such as those which are key in bioturbation and biodeposition, or nutrient and biogeochemical cycling, changes in siltation rates and organic enrichment.

Characteristic species
For full habitat description, please download the habitat factsheet.

Threat status

Synthesis of Red List assessment

This habitat has a widespread distribution. There are no precise figures on its extent of however a combination of survey data and modelling indicates that it cannot be considered to have a restricted geographical distribution nor to occur in only a few locations in the North East Atlantic.
Most sedimentary benthic systems on the continental shelf of Europe have been modified by fishing activities in the last 100 years and this pressure continues today. There is a lack of comprehensive data however expert opinion is that this habitat should be assesssed as Near Threatened for both the EU 28 and EU 28+ because of both past and likely future declines in quality.
EU
Red List Category Red List Criteria
Near Threatened C/D1
Europe
Red List Category Red List Criteria
Near Threatened C/D1

Confidence in the assessment

low
Red List of habitat categories and criteria descriptions

Pressures and threats

  • Urbanisation, residential and commercial development
    • Discharges
  • Biological resource use other than agriculture & forestry
    • Fishing and harvesting aquatic resources
    • Professional active fishing
  • Pollution
    • Pollution to surface waters (limnic, terrestrial, marine & brackish)
    • Nutrient enrichment (N, P, organic matter)
  • Natural System modifications
    • Human induced changes in hydraulic conditions
    • Modification of hydrographic functioning, general

Habitat restoration potential

Timescale between incidents of damaging activity, the type of damaging activity and the predominant species, influences recovery. Studies have shown that recovery times following dredging were significantly shorter for short-lived species (<1 – 3 years), free-living and tube-dwelling species and for scavenging or opportunistic species, than for medium-lived species (3 – 10 years), burrow-dwelling species and suspension feeders. In trawled areas, recovery times were significantly shorter for free-living species, species covered by an exoskeleton or a hard tunic and species that produce pelagic or benthic eggs than for epiphytic/zoic species, species that grow attached to the substratum and have an erect or stalked body form, and species that reproduce asexually. Areas with high levels of natural disturbance have community compositions and functions that are more resilient than those found in areas with less natural disturbance.
Recovery times following oxygen depletion and pollution has been investigated in several studies of the Gullmarsfjord, Sweden showing and reported to be between 2-8 years. Differences in the recoverability of different species groups following fishing may result in changes in community composition and ecosystem functioning over the long term.

Trends in extent

Average current trend in quantity

Unknown Unknown
EU28 EU28+

Trends in quality

Average current trend in quality

Decreasing Decreasing
EU28 EU28+

Conservation and management needs

This habitat can benefit from the regulation of the use of fishing gears that damage or disturb seabed communities. This may be achieved by spatial and temporal controls as well as gear design and deployment using fisheries management measures as well as conservation legislation in marine protected areas. Spatial planning (including zoning) can be used to address potential threats from coastal development and fish farming and the regulation of discharges and run off from agricultural land to the marine environment can be used to avoid eutrophication effects associated with nutrient enrichment.

List of conservation and management needs

  • Measures related to marine habitats
    • Other marine-related measures
  • Measures related to spatial planning
    • Other marine-related measures
    • Establish protected areas/sites
  • Measures related to hunting, taking and fishing and species management
    • Regulation/Management of fishery in marine and brackish systems

Distribution

For each habitat a distribution map was produced from a wide variety of sources indicating known and potential occurrences of the habitat in 10x10 km grids within Europe. Occurrences in grid cells were given in two classes: actual distribution from relatively reliable sources (surveys, expert knowledge), and potential distribution based on models or less reliable indicators. Please download the fact sheet to see the map.

Geographic occurrence and trends

Seas Present or presence uncertain Current area of habitat (Km2) Recent trend in quantity (last 50 years) Recent trend in quality (last 50 years)
Bay of Biscay and the Iberian Coast Present Unknown Decreasing Unknown
Celtic Seas
Kattegat
Greater North Sea
Macaronesia

Extent of Occurrence, Area of Occupancy and habitat area

Extent of Occurrence (EOO) (Km2) Area of Occupancy (AOO) Current estimated Total Area Comment
EU28 3,172,859 177 >354 The area estimate for this habitat has been derived from a synthesis of EUNIS seabed habitat geospatial information for the European Seas but is recognised as being an underestimate.
EU28+ >177 >354 EOO and AOO have been calculated on the available data. Although this data set is known to be incomplete the figures exceed the thresholds for threatened status.
AOO = the area occupied by a habitat measured in number of 10x10 km grid cells.
EOO = the area (km2) of the envelope around all occurrences of a habitat (calculated by a minimum convex polygon).

Characteristic species

The full list of characteristic species and genus are available above from the Summary. The species available in the EUNIS database are shown here.
Invertebrates Ampelisca brevicornis
Invertebrates Ascidiella aspersa
Invertebrates Capitella capitata
Invertebrates Carcinus maenas
Invertebrates Chaetozone gibber
Invertebrates Liocarcinus depurator
Invertebrates Macoma balthica
Invertebrates Mysella bidentata
Invertebrates Nucula nitidosa
Invertebrates Pagurus bernhardus
Invertebrates Scoloplos armiger
Invertebrates Virgularia mirabilis
Species scientific name English common name Species group
Ampelisca brevicornis Invertebrates
Ascidiella aspersa Invertebrates
Capitella capitata Invertebrates
Carcinus maenas Invertebrates
Chaetozone gibber Invertebrates
Liocarcinus depurator Invertebrates
Macoma balthica Invertebrates
Mysella bidentata Invertebrates
Nucula nitidosa Invertebrates
Pagurus bernhardus Invertebrates
Scoloplos armiger Invertebrates
Virgularia mirabilis Invertebrates

Vegetation types

Relation to vegetation types (syntaxa)

Not available

Other classifications

Not available
European Environment Agency (EEA)
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1050 Copenhagen K
Denmark
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