South-Aegean Phoenix grove
Quick facts
Red List habitat type | code RLG2.5a |
---|---|
Threat status | |
Europe | Least Concern |
EU | Least Concern |
Relation to |
|
Source | European Red List habitat factsheet |
European Red List of habitats reports | |
European Red List of habitats (Excel table) |
Summary
This habitat includes woods, in contact with the underground water table, often riparian, formed by the palm tree Phoenix theophrasti, found on the island of Crete and south-western Anatolia. The majority of occurrences of Phoenix theophrasti in Crete, and all existing records made outside Crete and southwest Turkey, are represented only by scattered or isolated trees. Within the EU, Crete holds the only palm groves that are representative for the habitat type. Only two sites are known in Crete with several hundreds of trees: Vai and Preveli, the former is the most extensive (ca. 20 ha). The tertiary relict Phoenix theophrasti woods of Crete and south-western Anatolia (Datça peninsula) are restricted to damp, mostly sandy coastal valleys below 250 m; here are included: a) the most extensive grove in Crete, the forest of Vai in the east of the island, characterized by the luxuriant palm growth, accompanied by a thick shrubby undergrowth rich in Nerium oleander, and b) a few other smaller coastal groves, notably on the south coast of the prefecture of Rethimnon. The westernmost occurrence is in southwest Crete, on coastal plains south of the monastery of Chrisoskalitissa. Phoenix theophrasti trees are known also from some Greek islands (Crete, Karpathos, Kos, Rodhos, Thira, Nisyros, Amorgos) and from the Turkish southeast Aegean sites of Datça and Kumluca-Karaöz, with additional populations in Bodrum-Gölköy, all in southwest Anatolia. In the Aegean palm groves, Phoenix theophrasti is a rather rare constituent of the Aegean Nerio-Tamaricetea vegetation and is restricted to semiarid climate (generally with 400-600 mm annual precipitation). The habitat may be either riparian (with the palm forming temporarily inundated gallery forest along permanent fresh or brackish waters), or related to seasonally or episodically flooded coastal valleys. In the latter, the palm trees are generally more scattered, and they may be restricted to rocky low slopes. Underground water level is high and sufficiently permanent to control habitat ecology and species combination. The soils are frequently sandy but the habitat type does not include mobile dunes. The vegetation belongs to the alliance Rubo sancti-Nerion oleandri but more isolated trees or clusters are surrounded by Pistacio-Rhamnetalia or Cisto-Micromerietalia vegetation. Associated of Phoenix theophrasti are species of wet or semiwet habitats, as well as species with a wider ecological range (see the list of characteristic species below).
Indicators of quality:
- No forest exploitations in the majority of the area covered by the habitat
- Intact natural hydrology
- Natural composition of canopy
- Structural diversity/ complexity with (semi)natural age structure or completeness of layers
- Typical flora and fauna composition of the region
- Presence of old trees and a variety of dead wood (lying or standing) and the associated flora, fauna and fungi
- Presence of natural disturbance such as treefall openings with natural regeneration
- Long historical continuity (ancient woodland) with high species diversity
- Absence of non-native species in all layers (flora & fauna)
- No signs of eutrophication or pollution
The indicators of good quality are primarily related to the maintenance of the natural structure of the Phoenix theophrasti woods. The presence of rejuvenation of Phoenix theophrasti in all sites of its occurrence, as well as the undisturbed soil (no significant trampling or erosion), the natural relief, the stratified stands (tree, shrub, herb layer present), the closed canopy of Phoenix theophrasti woods ≥25% and Phoenix individuals mostly higher than 3 m are indicators that the structure and functions of the habitat are in favourable conservation status to a significant part of its distribution. Its adjacency to, or its interdigitation with Mediterranean salt meadows of the Juncetalia maritimi (1410 - Annex I of the Dir. 92/43/EEC), and/or Mediterranean tall humid herb grasslands of the Molinio-Holoschoenion (6420 -Annex I of the Dir. 92/43/EEC) are also considered as indicators related to the long-term conservation of the habitat.
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
- Sylviculture, forestry
- Grazing in forests/ woodland
- Human intrusions and disturbances
- Trampling, overuse
- Natural System modifications
- Burning down
- Groundwater abstractions for agriculture
Habitat restoration potential
Trends in extent |
|
Average current trend in quantity |
|
Stable ![]() |
Stable ![]() |
EU28 | EU28+ |
Trends in quality |
|
Average current trend in quality |
|
Stable ![]() |
Stable ![]() |
EU28 | EU28+ |
Conservation and management needs
List of conservation and management needs
- Measures related to forests and wooded habitats
- Restoring/Improving forest habitats
- Measures related to wetland, freshwater and coastal habitats
- Managing water abstraction
- Measures related to spatial planning
- Legal protection of habitats and species
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) |
---|---|---|---|---|
Crete | Present | 1.3 | Stable | Stable |
EU28 + | Present or presence uncertain | Current area of habitat (Km2) | Recent trend in quantity (last 50 years) | Recent trend in quality (last 50 years) |
---|
Extent of Occurrence, Area of Occupancy and habitat area
Extent of Occurrence (EOO) (Km2) | Area of Occupancy (AOO) | Current estimated Total Area | Comment | |
---|---|---|---|---|
EU28 | 13600 | 31 | 1.3 | |
EU28+ | 31 | 1.3 |
EOO = the area (km2) of the envelope around all occurrences of a habitat (calculated by a minimum convex polygon).