Communities of Mediterranean circalittoral caves and overhangs
Quick facts
Red List habitat type | code MEDA4.71 |
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Threat status | |
Europe | Least Concern |
EU | Least Concern |
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
Caves and overhangs constitute typical features of the Mediterranean circalittoral rocky bottoms. They support a great variety of species and host a considerable proportion of the total Mediterranean diversity of certain phyla, such as Brachiopoda, Bryozoa, and Porifera. Several protected and rare species, including recently described species, as well as deep-sea species have been reported. Most of our knowledge comes from caves in the north-west Mediterranean as cave biodiversity is extremely understudied in the southern and eastern basins. They are characterised by high morphological complexity, reflected in abiotic gradients and marked biological zonation along the longitudinal cave axis, from the entrance to the inner cave sectors. Light availability and water confinement are acknowledged as the main driving forces shaping this zonation. Thus, circalittoral caves support a variety of sciaphilic assemblages, usually distributed according to the following scheme: (i) a sciaphilic algae-dominated community at the entrance zone, (ii) a semi-dark zone where sessile filter-feeding invertebrates (mainly sponges and anthozoans) dominate, favored by the disappearance of macroalgae, and (iii) a dark zone which is sparsely colonized by sponges, serpulid polychaetes, bryozoans and brachiopods.
The shift from semi-dark to dark cave communities is evidenced through a sharp decrease in biotic coverage, biomass, three-dimensional biotic complexity, species richness, and the appearance of a black mineral coating of Mn-Fe oxides on the substrate. Additional zones, such as a transitional zone between semi-dark and dark cave communities and an azoic zone at the aphotic cave edge, have been occasionally identified. The limits of these zones might vary among caves with different morphology (e.g. inner zones tend to appear closer to the cave entrance in deeper waters), while in some caves some specific zones might be absent. Semi-dark caves are community is typically dominated by sponges, bryozoans, brachiopods and polychaete species. Serpulid polychaetes (e.g. Protula spp.) can form aggregations, which in some cases constitute the basis for the creation of biogenic structures; these ‘biostalactites’ are constructed by invertebrates (serpulids, sponges, and bryozoans), foraminiferans and carbonate-forming microorganisms. A number of deep-sea species belonging to various taxonomic groups (e.g. sponges, anthozoans and bryozoans) have also been recorded in sublittoral dark caves, regardless of depth
Indicators of quality:
Marine caves are characterised by high levels of individuality and heterogeneity which, coupled to the poor understanding of the ecosystem functioning, make it difficult the assessment of their ecologic quality. However, a number of indicators of quality have been recently suggested for the marine cave ecosystem, such as:
- Presence of invertebrates offering three-dimensional complexity to the substrate, and particularly fragile slow-growing species (e.g. red coral, erect bryozoans)
- High spatial coverage of suspension feeders (i.e. anthozoans) and large filter feeders (e.g. massive sponges)
- Presence of large mysid swarms
- Presence of various omnivorous and carnivorous mobile species (e.g. fish and decapods)
Threat status
Synthesis of Red List assessment
EU | |
Red List Category | Red List Criteria |
Least Concern | - |
Europe | |
Red List Category | Red List Criteria |
Least Concern | - |
Confidence in the assessment
Pressures and threats
- Urbanisation, residential and commercial development
- Urbanised areas, human habitation
- Discharges
- Human intrusions and disturbances
- Speleology
- Recreational cave visits
- Scubadiving, snorkelling
- Pollution
- Marine macro-pollution (i.e. plastic bags, styrofoam)
- Invasive, other problematic species and genes
- Invasive non-native species
- Climate change
- Temperature changes (e.g. rise of temperature & extremes)
Habitat restoration potential
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
The clear biogeographic patterns exhibited by the Mediterranean marine cave assemblages from different regions suggest the need for protecting marine caves (e.g. management of visitation and other activities) in different regions in order to safeguard representativeness of the habitat type at the Mediterranean scale. Finally, the notable presence of several alien species in southeastern Mediterranean caves (though mostly in semi-submerged and shallow semi-dark caves and tunnels) should be monitored.
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
- Legal protection of habitats and species
- Measures related to hunting, taking and fishing and species management
- Regulation/Management of fishery in marine and brackish systems
- Measures related to special resouce use
- Regulating/Managing exploitation of natural resources on sea
Distribution
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) |
---|---|---|---|---|
Adriatic Sea | Present | 76,721 | Decreasing | Unknown |
Aegian-Levantine Sea | ||||
Ionian Sea and the Central Mediterranean Sea | ||||
Western Mediterranean Sea |
Extent of Occurrence, Area of Occupancy and habitat area
Extent of Occurrence (EOO) (Km2) | Area of Occupancy (AOO) | Current estimated Total Area | Comment | |
---|---|---|---|---|
EU28 | 2,208,454 | 1,063 | 75,436 | 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. |
EU28+ | 1,094 | 76,721 | 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. |
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
Legal text | Annex | Name in legal text | Code in legal text |
Habitat type relationship |
More information |
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Council Directive 92/43/EEC of 21 May 1992 on the conservation of natural habitats and of wild fauna and flora - consolidated version 01/01/2007 | Annex I: natural habitat types of community interest whose conservation requires the designation of special areas of conservation | Submerged or partially submerged sea caves | 8330 | Narrower | http://ec.europa.eu/environm...rective/index_en.htm |