Relict mire of Mediterranean mountains
Quick facts
| Red List habitat type | code RLD2.2b |
|---|---|
| Threat status | |
| Europe | Near Threatened |
| EU | Vulnerable |
| Relation to |
|
| Source | European Red List habitat factsheet |
| European Red List of habitats reports | |
| European Red List of habitats (Excel table) |
Summary
Oligo- to mesotrophic mires of the montane and subalpine belts of Mediterranean mountains of the High Atlas (Morocco), Sierra Nevada and Corse, and of high mountains (above 1900 m altitude) of the Western Balkan peninsula. These mires occur on the edges of glacial lakes and around mountain streams, forming waterlogged ‘blankets’ in relatively flat areas with impermeable soils, where a peat layer has developed on siliceous bedrocks. The type is differentiated from mires and grasslands with a similar physiognomy in the Alps, Pyrenees and rest of the Balkan by the presence and dominance of narrow-endemic relict species, and by the lower frequency of Sphagnum species. The sites of this habitat in the South-European mountains are characterised by relative cold and humid conditions, creating a distinct green habitat in a dry landscape. Water supply and temperature vary relatively little during the year, compared to surrounding habitats. In the high mountains of the Balkan this habitat is covered by snow most of the year.
The mires are bordered by streams, springs and lakes on the lower edges, and by moist grasslands with Nardus stricta (E3.2b) on the drier edges. The habitat is dominated by Carex nigra ssp. intricata in the Sierra Nevada and Corse, and by Carex nigra var. macedonica in the Balkan. In Spain also Festuca frigida may dominate, while in Corse along streams Trichophorum cespitosum may be dominant. Common species in both Mediterranean regions are Carex echinata, Carex nevadensis, Agrostis canina and Viola palustris. Different characteristic endemic species are found in the different regions. For several genera, vicariant endemic species are found in the different mountain regions. Such species are considered tertiary relicts. Examples in these mires are Pinguicula nevadensis, Pinguicula corsica and Pinguicula balcanica, and also Narthecium reverchonii (Corse) and Narthecium scardicum (Balkan). Some of the characteristic species also grow outside the mires, like Pinguicula corsica and Narthecium reverchonii along waterfalls on wet rocks. Together with the adjacent Nardus grasslands of E3.2b, these conspicuous habitats are called Pozzines in Corse and Borreguiles in the Sierra Nevada.
Indicators of good quality:
In wet conditions these grasslands are relatively stable. Desiccation causes a succession towards Nardus grasslands of E3.2b. Abandonment leads to the development of tall herb vegetation. The type may expand slowly by vegetation succession in open water. Indicators of good quality are:
- presence of endemic species
- high vegetation cover
- low cover of (encroaching) tall herbs and shrubs
- situated in a gradient from water to drier grassland
Threat status
Synthesis of Red List assessment
| EU | |
| Red List Category | Red List Criteria |
| Vulnerable | B2 |
| Europe | |
| Red List Category | Red List Criteria |
| Near Threatened | B2 |
Confidence in the assessment
Pressures and threats
- Human intrusions and disturbances
- Outdoor sports and leisure activities, recreational activities
- Pollution
- Pollution to surface waters (limnic, terrestrial, marine & brackish)
- Natural System modifications
- Human induced changes in hydraulic conditions
- Natural biotic and abiotic processes (without catastrophes)
- Biocenotic evolution, succession
- Climate change
- Changes in abiotic conditions
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/Improving the hydrological regime
- Managing water abstraction
- Measures related to spatial planning
- Establish protected areas/sites
- Measures related to hunting, taking and fishing and species management
- Specific single species or species group management measures
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) |
|---|---|---|---|---|
| Corsica | Present | 1.3 | Stable | Stable |
| Spain mainland | Present | 51 | Decreasing | Decreasing |
| Bulgaria | Present | 1.3 | Decreasing | Decreasing |
| EU28 + | Present or presence uncertain | Current area of habitat (Km2) | Recent trend in quantity (last 50 years) | Recent trend in quality (last 50 years) |
|---|---|---|---|---|
| Former Yugoslavian Republic of Macedonia (FYROM) | Present | unknown | Decreasing | Decreasing |
| Albania | Present | Unknown | Unknown | Unknown |
| Bosnia and Herzegovina | Uncertain | - | - | |
| Kosovo | Present | Unknown | Decreasing | Stable |
Extent of Occurrence, Area of Occupancy and habitat area
| Extent of Occurrence (EOO) (Km2) | Area of Occupancy (AOO) | Current estimated Total Area | Comment | |
|---|---|---|---|---|
| EU28 | 436850 | 40 | 55 | |
| EU28+ | 45 | >55 | not exactly determined |
EOO = the area (km2) of the envelope around all occurrences of a habitat (calculated by a minimum convex polygon).

