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Note: Rows in italic shows data not taken into account when performing the assessments (marginal presence, occasional, extinct prior HD, information, etc)
| Member States reports | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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| Habitat | Region | Range (km2) | Area (km2) | Structure and functions (km2) | Future prospects | Overall assessment | Distribution area(km2) | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Surface | Status (% MS) |
Trend | FRR | Min | Max | Best value | Type est. | Method | Status (% MS) |
Trend | FRA |
|
Not good | Not known | Status | Trend | Range prosp. |
Area prosp. |
S & f prosp. |
Status | Curr. CS | Curr. CS trend |
Prev. CS | Prev. CS trend |
Status Nat. of ch. |
CS trend Nat. of ch. |
Distrib. | Method | % MS | ||||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9110 - Luzulo-Fagetum beech forests | ATL | 4827 | 7.21 | = | ≈ | N/A | N/A | 1.50 | estimate | b | 0.36 | x | ≈ | N/A - N/A | 1.50 - 1.50 | N/A - N/A | U2 | - | good | good | bad | U2 | U2 | - | U2 | = | N/A | N/A | 1400 | b | 2.97 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9110 - Luzulo-Fagetum beech forests | CON | 22623 | 3.17 | = | ≈ | N/A | N/A | 175.56 | estimate | b | 1.09 | x | ≈ | N/A - N/A | 175.56 - 175.56 | N/A - N/A | U2 | - | good | good | bad | U2 | U2 | - | U2 | = | N/A | N/A | 10700 | b | 2.16 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9120 - Atlantic acidophilous beech forests with Ilex and sometimes also Taxus in the schrublayer (Quercion robori-petraeae or Ilici-Fagenion) | ATL | 2430 | 1.01 | = | ≈ | N/A | N/A | 2.55 | estimate | b | 0.06 | x | ≈ | N/A - 0.13 | 2.42 - 2.55 | N/A - N/A | U2 | u | good | good | bad | U2 | U2 | x | U2 | = | N/A | N/A | 700 | b | 0.51 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9120 - Atlantic acidophilous beech forests with Ilex and sometimes also Taxus in the schrublayer (Quercion robori-petraeae or Ilici-Fagenion) | CON | 7180 | 8.32 | = | ≈ | N/A | N/A | 32.41 | estimate | b | 0.33 | x | ≈ | N/A - 2.40 | 30.01 - 32.41 | N/A - N/A | U2 | u | good | good | bad | U2 | U2 | x | U2 | = | N/A | N/A | 3400 | b | 4.58 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9130 - Asperulo-Fagetum beech forests | ATL | 2433 | 1.17 | = | ≈ | N/A | N/A | 2.42 | estimate | b | 0.04 | x | ≈ | N/A - N/A | 2.42 - 2.42 | N/A - N/A | U2 | - | good | good | bad | U2 | U2 | - | U2 | = | N/A | N/A | 1100 | b | 0.86 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9130 - Asperulo-Fagetum beech forests | CON | 26521 | 3.04 | = | ≈ | N/A | N/A | 377.77 | estimate | b | 0.95 | x | ≈ | N/A - 0.66 | 377.12 - 377.78 | N/A - N/A | U2 | - | good | good | bad | U2 | U2 | - | U2 | = | N/A | N/A | 22200 | b | 3.66 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9150 - Medio-European limestone beech forests of the Cephalanthero-Fagion | CON | 2895 | 1.47 | = | ≈ | N/A | N/A | 6.66 | estimate | b | 0.33 | x | ≈ | N/A - 0.37 | 6.29 - 6.66 | N/A - N/A | U2 | - | good | unk | bad | U2 | U2 | - | U2 | = | N/A | N/A | 1900 | b | 1.55 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9160 - Sub-Atlantic and medio-European oak or oak-hornbeam forests of the Carpinion betuli | ATL | 4661 | 2.92 | = | ≈ | N/A | N/A | 9.90 | estimate | b | 1.18 | x | ≈ | N/A - N/A | 9.90 - 9.90 | N/A - N/A | U2 | - | good | good | bad | U2 | U2 | - | U2 | = | N/A | N/A | 1900 | b | 1.88 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9160 - Sub-Atlantic and medio-European oak or oak-hornbeam forests of the Carpinion betuli | CON | 25704 | 5.19 | = | ≈ | N/A | N/A | 90.30 | estimate | b | 1.55 | x | ≈ | N/A - 1.52 | 88.78 - 90.30 | N/A - N/A | U2 | - | good | good | bad | U2 | U2 | - | U2 | = | N/A | N/A | 18000 | b | 5.02 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9170 - Galio-Carpinetum oak-hornbeam forests | CON | 225 | 0.03 | = | > | N/A | N/A | 0.75 | estimate | b | 0 | x | >> | N/A - N/A | 0.75 - 0.75 | N/A - N/A | U2 | u | unk | bad | bad | U2 | U2 | x | U2 | = | N/A | N/A | 300 | b | 0.06 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9190 - Old acidophilous oak woods with Quercus robur on sandy plains | ATL | 11186 | 6.80 | = | ≈ | N/A | N/A | 13.34 | estimate | b | 3.16 | x | ≈ | N/A - N/A | 13.34 - 13.34 | N/A - N/A | U2 | - | good | good | bad | U2 | U2 | - | U2 | = | N/A | N/A | 4300 | b | 3.78 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 9190 - Old acidophilous oak woods with Quercus robur on sandy plains | CON | 13864 | 3.80 | = | ≈ | N/A | N/A | 30.57 | estimate | b | 2.25 | x | ≈ | N/A - N/A | 30.57 - 30.57 | N/A - N/A | U2 | - | good | good | bad | U2 | U2 | - | U2 | = | N/A | N/A | 7300 | b | 2.87 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 91D0 - Bog woodland | ATL | 13473 | 11.41 | = | ≈ | N/A | N/A | 8.10 | estimate | b | 4.55 | x | ≈ | N/A - N/A | 8.10 - 8.10 | N/A - N/A | U2 | - | good | good | bad | U2 | U2 | - | U2 | = | N/A | N/A | 4700 | b | 6.63 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 91D0 - Bog woodland | CON | 29544 | 7.16 | = | ≈ | N/A | N/A | 44.84 | estimate | b | 3.90 | x | ≈ | N/A - N/A | 44.84 - 44.84 | N/A - N/A | U2 | - | good | good | bad | U2 | U2 | - | U2 | = | N/A | N/A | 11200 | b | 4.33 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 91E0 - Alluvial forests with Alnus glutinosa and Fraxinus excelsior (Alno-Padion, Alnion incanae, Salicion albae) | ATL | 13473 | 2.02 | = | ≈ | N/A | N/A | 7.81 | estimate | b | 0.40 | x | ≈ | N/A - N/A | 7.81 - 7.81 | N/A - N/A | U2 | u | good | good | bad | U2 | U2 | x | U2 | = | N/A | N/A | 3100 | b | 0.83 | ||||||||||||||||||||||||||||||||||||||||||||||||||||
| 91E0 - Alluvial forests with Alnus glutinosa and Fraxinus excelsior (Alno-Padion, Alnion incanae, Salicion albae) | CON | 29544 | 2.61 | = | ≈ | N/A | N/A | 185.28 | estimate | b | 4.01 | x | ≈ | N/A - 2.35 | 182.93 - 185.28 | N/A - N/A | U2 | u | good | good | bad | U2 | U2 | x | U2 | = | N/A | N/A | 19900 | b | 2.18 | ||||||||||||||||||||||||||||||||||||||||||||||||||||