Temperate and submediterranean thermophilous deciduous woodland
Quick facts
Red List habitat type | code RLG1.7a |
---|---|
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
These thermophilous broadleaved deciduous woodlands form a wide, but interrupted, belt across the submediterranean zone of Europe, with milder winters and warmer drought-prone summers than sustain the broadleaved temperate woodlands, but colder, intermittently frosty and snowy winters than are typical for the evergreen broadleaved woodlands and scrub of the Mediterranean. To the north, they tend to occupy lower altitude, drier and warmer sites, to the south, rainier sites at higher altitudes, but the relief and parent materials differ widely across the range and the weakly base-rich to moderately acidic soils are of varied types. The canopy, rarely very tall, is dominated by thermophilous and drought-resistant deciduous (and some evergreen) trees, among which oaks are the commonest contributors to an upper tier. Quercus petraea and Q. robur remain important in the sub-Continental thermophilous woodlands of the Czech Republic, Poland, Slovakia, Romania, Ukraine and the northern Balkans but, across much of the range through France, northern Spain, Switzerland, northern Italy, the Pannonian Basin, around the Adriatic and in Greece, Q. pubescens is the leading oak, with Q. cerris and Q. frainetto becoming important from Italy eastwards. Q. dalechampii, Q. polycarpa and Q. virgiliana are common associates, with Q. trojana in the Balkans. In the Iberian Peninsula, Q. pyrenaica, Q. faginea ssp. faginea, Q. faginea ssp. broteroi and Q. canariensis replace these oaks as dominants. In less modified stands there is a second tier of trees with, across much of the range, Sorbus torminalis, S. domestica, S. aria, Ulmus minor, Acer campestre, A. monspessulanum and Pyrus pyraster, with Fraxinus ornus, Ostrya carpinifolia and Carpinus orientalis commoner in the south-eastern regions, Acer tataricum and Tilia tomentosa mainly in the more Continental east. The light shade cast by the oaks and thinning of the canopy characteristically permit a dense shrub layer among which Cornus mas, Viburnum lantana, Ligustrum vulgare, Ruscus aculeatus, Crataegus monogyna, Prunus spinosa and Cotinus coggygria are frequent along with more mesic shrubs like Corylus avellana, Cornus sanguinea and Euonymus europaeus. To the west, Buxus sempervirens and Rubus ulmifolius occur, to the southeast Paliurus spina-christi, Hippocrepis emerus, Pistacia mutica and Juniperus excelsa and, in the warmer south, evergreen Mediterranean species such as Phillyrea latifolia, Arbutus unedo, Pistacia lentiscus, P. terebinthus, Viburnum tinus and Erica arborea. Lianas are common with Clematis vitalba, Lonicera caprifolium, L. etrusca, Tamus communis, Rubia peregrina and Hedera helix the most consistent species throughout. The herb layer is rich with sub-Mediterranean species making a prominent contribution: Lithospermum purpurocaeruleum, Lathyrus venetus, Melittis melissophyllum, Tanacetum corymbosum, Silene coronaria, Potentilla micrantha, Vincetoxicum hirundinaria, Physospermum cornubiense, Hellebrous odorus, H. foetidus, Mercurialis ovata and Viola hirta are characteristic through much of the range, with many other species occurring in particular regional types.
Indicators of quality:
• 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
• Survival of larger stands of forest without anthropogenic fragmentation and isolation (to support fauna which needs large undisturbed forests)
• Absence of non-native species in all layers (flora & fauna)
• No signs of eutrophication or pollution
• No man-induced very high population levels of ungulates
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
- Forestry clearance
- Grazing in forests/ woodland
- Invasive, other problematic species and genes
- Invasive non-native species
- Natural System modifications
- Burning down
- Natural biotic and abiotic processes (without catastrophes)
- Species composition change (succession)
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 forests and wooded habitats
- Adapt forest management
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) |
---|---|---|---|---|
Austria | Present | 200 | Decreasing | Decreasing |
Bulgaria | Present | 9350 | Decreasing | Decreasing |
Croatia | Present | 3784 | Increasing | Increasing |
Czech Republic | Present | 167 | Decreasing | Decreasing |
France mainland | Present | 13470 | Decreasing | Increasing |
Germany | Present | Unknown | Decreasing | Stable |
Greece (mainland and other islands) | Present | 11448 | Stable | Stable |
Hungary | Present | 2090 | Decreasing | Stable |
Italy mainland | Present | 24818 | Decreasing | Stable |
Sardinia | Present | 24818 | Decreasing | Stable |
Sicily | Present | 24818 | Decreasing | Stable |
Poland | Present | 18 | Decreasing | Decreasing |
Portugal mainland | Present | 77 | Unknown | Increasing |
Romania | Present | 4600 | Decreasing | Decreasing |
Slovakia | Present | 210 | Decreasing | Decreasing |
Slovenia | Present | 1064 | Stable | Increasing |
Spain mainland | Present | 4027 | Increasing | Increasing |
Balearic Islands | Present | 4027 | Increasing | Increasing |
EU28 + | Present or presence uncertain | Current area of habitat (Km2) | Recent trend in quantity (last 50 years) | Recent trend in quality (last 50 years) |
---|---|---|---|---|
Albania | Present | - | - | |
Bosnia and Herzegovina | Present | 5000 | Increasing | Increasing |
Kosovo | Present | - | - | |
Former Yugoslavian Republic of Macedonia (FYROM) | Present | 1782 | Decreasing | Increasing |
Montenegro | Present | 1749 | Unknown | Stable |
Serbia | Present | - | - | |
Switzerland | Present | 85 | Increasing | 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 | 5148500 | 16073 | >117446 | Current estimated Total Area is an underestimated minimum value because of missing data from some countries. |
EU28+ | 17793 | >126062 | Current estimated Total Area is an underestimated minimum value because of missing data from some countries. |
EOO = the area (km2) of the envelope around all occurrences of a habitat (calculated by a minimum convex polygon).