Choose a period, a group and then a country. Optionally, further refine your query by selecting one of the available biogeographical regions for that country.
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 | |||||||||||||||||||||||||||||||||
| 6120 - Xeric sand calcareous grasslands | CON | 7553 | 2.08 | = | ≈ | N/A | N/A | 1.24 | estimate | b | 0.09 | - | >> | 0.07 - 0.27 | 0.97 - 1.17 | N/A - N/A | U2 | = | good | bad | bad | U2 | U2 | = | U2 | x | N/A | N/A | 3600 | b | 1.08 | |||||||||||||||||||||||||||||||
| 6210 - Semi-natural dry grasslands and scrubland facies on calcareous substrates (Festuco Brometalia)(*important orchid sites) | ATL | 9420 | 2.61 | = | ≈ | N/A | N/A | 3 | estimate | b | 0.18 | - | >> | 0.36 - 1.51 | 1.49 - 2.64 | N/A - N/A | U2 | - | good | bad | bad | U2 | U2 | - | U2 | x | N/A | N/A | 2600 | b | 1.47 | |||||||||||||||||||||||||||||||
| 6210 - Semi-natural dry grasslands and scrubland facies on calcareous substrates (Festuco Brometalia)(*important orchid sites) | CON | 29440 | 4.05 | = | ≈ | N/A | N/A | 38 | estimate | b | 0.59 | - | >> | 10.78 - 26.01 | 11.99 - 27.22 | N/A - N/A | U2 | - | good | bad | bad | U2 | U2 | - | U2 | x | N/A | N/A | 19200 | b | 4.23 | |||||||||||||||||||||||||||||||
| 6230 - Species-rich Nardus grasslands, on siliceous substrates in mountain areas (and submountain areas, in Continental Europe) | ATL | 13470 | 5.11 | = | ≈ | N/A | N/A | 35 | estimate | b | 6.33 | = | ≈ | 10.33 - 28.66 | 6.34 - 24.67 | N/A - N/A | U1 | - | good | good | poor | U1 | U1 | - | U2 | = | N/A | N/A | 8900 | b | 6.97 | |||||||||||||||||||||||||||||||
| 6230 - Species-rich Nardus grasslands, on siliceous substrates in mountain areas (and submountain areas, in Continental Europe) | CON | 29540 | 7.65 | = | ≈ | N/A | N/A | 116 | estimate | b | 15.35 | = | ≈ | 27.16 - 79.64 | 36.36 - 88.84 | N/A - N/A | U2 | - | good | good | bad | U2 | U2 | - | U2 | x | N/A | N/A | 21400 | b | 9.34 | |||||||||||||||||||||||||||||||
| 6410 - Molinia meadows on calcareous, peaty or clavey-silt-laden soils (Molinion caeruleae) | ATL | 13470 | 3.47 | = | ≈ | N/A | N/A | 23 | estimate | b | 2.44 | = | ≈ | 3.66 - 9.83 | 13.17 - 19.34 | N/A - N/A | U2 | = | good | good | bad | U2 | U2 | = | U1 | = | N/A | N/A | 7700 | b | 3.92 | |||||||||||||||||||||||||||||||
| 6410 - Molinia meadows on calcareous, peaty or clavey-silt-laden soils (Molinion caeruleae) | CON | 29540 | 5.42 | = | ≈ | N/A | N/A | 68 | estimate | b | 2.08 | = | >> | 11.70 - 29.61 | 38.39 - 56.30 | N/A - N/A | U2 | = | good | bad | bad | U2 | U2 | = | U2 | x | N/A | N/A | 15000 | b | 3.95 | |||||||||||||||||||||||||||||||
| 6430 - Hydrophilous tall herb fringe communities of plains and of the montane to alpine levels | ATL | 13020 | 2.84 | x | ≈ | N/A | N/A | 35.70 | estimate | a | 3.11 | x | ≈ | 0.80 - 0.80 | 34.90 - 34.90 | N/A - N/A | U2 | x | good | good | bad | U2 | U2 | x | U2 | = | N/A | N/A | 11800 | a | 4.25 | |||||||||||||||||||||||||||||||
| 6430 - Hydrophilous tall herb fringe communities of plains and of the montane to alpine levels | CON | 28410 | 3.60 | x | ≈ | N/A | N/A | 63.90 | estimate | a | 0.66 | x | ≈ | 2.80 - 2.80 | 61.20 - 61.20 | N/A - N/A | U2 | x | good | good | bad | U2 | U2 | x | U2 | = | N/A | N/A | 24900 | a | 4.32 | |||||||||||||||||||||||||||||||