Rhodolith beds in the Mediterranean
Quick facts
| Red List habitat type | code MEDA5.51 |
|---|---|
| Threat status | |
| Europe | Data Deficient |
| EU | Data Deficient |
| Relation to |
|
| Source | European Red List habitat factsheet |
| European Red List of habitats reports | |
| European Red List of habitats (Excel table) |
Summary
Mediterranean rhodolith beds could be found between 20-150 m depth in normal marine conditions. The most common species is Lithothamnion corallioides and Phymatolithon calcareum is recorded less frequently. Different dominant species characterize the Mediterranean rhodolith beds, probably on the basis of biogeography and local environmental conditions.Characteristic associations include: Association with rhodoliths in coarse sands and fine gravels under the influence of bottom currents; and Association with rhodoliths on coastal detritic bottoms.
Rhodolith beds are defined by those sedimentary bottoms characterised by any morphology and species of unattached nongeniculate calcareous red algae (incompletely-coated grains excluded) with >10% of live cover. They occur in coarse clean sediments of gravels, clean sands and coastal detritic areas under the influence of bottom currents, which occur either on the open coast or in tide-swept channels of marine inlets (the latter often stony).
In general, fluent unidirectional hydrodynamism and laminar currents affect the seafloor. In the Mediterranean, the most favourable environment for this habitat to occur in biotopes with laminar bottom currents with a regular course. Changes in hydrodynamic conditions and intensity of light differentiate the presence of different associations, particularly in the community of the coastal detritic bottoms (circalittoral). The most frequent species of epiflora are Arthrocladia villosa and Sporochnus pedunculatus. Differences in intensity and typology of hydrodynamism and in species composition are able to determine differences in the growth form, structure and shape of the rhodoliths that can be summarized into three main morphologies: small and compact pralines, unattached branches, and large, irregular, boxwork rhodoliths. In the lower infralittoral zone this assemblage forms patches of organogenous pebbles of branched rhodoliths in various development stages. In the circalittoral zone the free calcareous algae formation can cover up to several square kilometres. Rhodolith beds can be considered as authentic carbonate factories, since they are among the highest producers of biogenic particles in European seas. The living part of the association is limited only to the surface of some centimetres of thickness. Subhabitat scomposed of non-nucleated, unattached growths of branching, twig-like coralline can be distinguished as maerl beds.
Threat status
Synthesis of Red List assessment
| EU | |
| Red List Category | Red List Criteria |
| Data Deficient | - |
| Europe | |
| Red List Category | Red List Criteria |
| Data Deficient | - |
Confidence in the assessment
Pressures and threats
- Biological resource use other than agriculture & forestry
- Suspension culture
- Benthic or demersal trawling
- Benthic dredging
- Human intrusions and disturbances
- Shallow surface abrasion/ Mechanical damage to seabed surface
- Penetration/ Disturbance below surface of the seabed
- Pollution
- Pollution to surface waters by industrial plants
- Pollution to surface waters by storm overflows
- Other point source pollution to surface water
- Toxic chemical discharge from material dumped at sea
- Natural System modifications
- Landfill, land reclamation and drying out, general
- Removal of sediments (mud...)
- 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 |
|
Unknown ![]() |
Unknown ![]() |
| EU28 | EU28+ |
Conservation and management needs
Marine reserves and MPAs have worked well in protecting local rhodolith beds from the effects of towed fishing gear as in the case of Tabarca Island. Rhodolith beds are considered as being vulnerable habitats by France and have been included within a proposed network of conservation areas termed ‘Natura 2000’ sites.
However, the lack of relevant geospatial data of the distribution of this habitat in the Mediterranean countries, significantly hinders the effective implementation of these policies. Among key conservation and management measures proposed are:
- Change the term "maerl" in the legal EU and Barcelona policy documents to "rhodoliths" as to conform the origin of the terms and their international scientific use, and to cover also the calcareous Peyssonnelia beds;
- Development of a moratoria on the issue of further permits for the siting of aquaculture units above rhodolith grounds;
- Setting up monitoring programmes of the health of rhodolith beds; including the collection of quantitative data about community composition;
- Designation of ‘no-take’ reserves and MPAs where these habitats occur;
- Establishing measures to limit the impacts that might affect water quality above rhodolith beds;
- Other Mediterranean endemics should be considered for protection (i.e.: Lithophyllum racemus, Lithothamnion minervae, Lithothamnion valens)
- Given its importance and current threats, should be evaluated as priority habitats for the Annex I of Habitat Directive
List of conservation and management needs
- Measures related to wetland, freshwater and coastal habitats
- Restoring/Improving water quality
- Measures related to marine habitats
- Other marine-related measures
- Measures related to spatial planning
- Establish protected areas/sites
- 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 | Unknown | Unknown | 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 | 2,182,108 | 136 | Unknown | 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+ | 2,244,540 | 146 | Unknown | 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 |
|---|---|---|---|---|---|
| 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 | Sandbanks which are slightly covered by sea water all the time | 1110 | Overlap | http://ec.europa.eu/environm...rective/index_en.htm |

