Map of the Potential Natural Vegetation of the Czech Republic

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Reduced Czech version

Authors: Zdenka Neuhäuslová  and coll.
Neuhauslova@ibot.cas.cz

The new vegetation map of the Czech Republic, Map of the Potential Natural Vegetation at a scale of 1:500 000, prepared in the years 1994-1996 and published in 1997, is a collective work by many Czech, Moravian and Silesian botanists. It was compiled on the basis of field work and the evaluation of all maps and phytosociological studies published until the end of 1996.

In comparison with the first geobotanical map of the Republic, the Map of Reconstructed Vegetation, published in 1968-1972 (see Mikyška 1968-1972, Geobotanická mapa ČSSR. 1. České země, ed. NČSAV Praha), this new map bears witness to the considerably increased knowledge of our vegetation and its distribution. In its compilation the principles of habitat analogy were again used, but irreversible changes of habitat resulting from human activity were also taken into account. The map depicts the equilibrium between present-day habitat conditions and the vegetation. While the legend of the Map of Reconstructed Vegetation contained 19 mapping units based on the floristic-phytocenological differentiation of the vegetation (Braun- Blanquet classification), the new map includes 51 units, mostly representing individual associations or two associations; only in special cases are complexes of higher syntaxa depicted (alliances to classes, e.g. mapping unit 13 - alliance Tilio-Acerion, MU 47, 48, 5O - mires distinguished at the level of order's, or small-areas covering alpine and subalpine vegetation - MU 46, representing syntaxa of several classes).

In the legend, singular mapping units are included within the supraordinated phytosociological categories. The structure of the legend, with very short characteristics of the individual mapping units, is given as follows:
 

Alluvial woodlands (Alnion incanae)

Hygrophilous to meso-hygrophilous, deciduous woodlands (dom. Quercus robur, Ulmus minor, U. laevis, Alnus glutinosa, A. incana, Fraxinus excelsior, F. angustifolia subsp. danubialis, Populus nigra), very rarely mixed woodlands with Picea abies, periodically or episodically flooded and influenced by groundwater, on alluvial and gley soils from planar to montane levels:

  1. Pruno-Fraxinetum (dom. Fraxinus excelsior, rarely Alnus glutinosa on moister sites or Tilia cordata on drier sites, frequent Padus avium) on gley soils or fluvisols at colline levels.
  2. Quercus robur-Padus avium comm. and Alnus glutinosa-Padus avium comm., more or less without Fraxinus excelsior, in the flat relief of the South-Bohemian basins, frequently flooded.
  3. Piceo-Alnetum (dom. Alnus glutinosa, frequently Picea abies) on flat sites with slow-flowing water, on gley soils at (sub)montane levels.
  4. Querco-Populetum (dom. Quercus robur, with Populus nigra), rich in pre-vernal geophytes, partly in complex with Querco -Ulmetum, in large river valleys of Central Bohemia.
  5. Querco-Ulmetum (dom. Quercus robur, with Ulmus laevis, U. minor, Alnus glutinosa on moister sites Fraxinus excelsior, Tilia cordata; on drier sites Acer campestre, Carpinus betulus) in large river valleys in the lowlands.
  6. Fraxino pannonicae-Ulmetum (dom. Quercus robur, Fraxinus angustifolia subsp. danubialis, with Ulmus minor, U. laevis), with Leucojum aestivum, partly in complex with Fraxino-Populetum (Populus nigra, P. alba, P. canescens), in the warmest part of S.Moravian river valleys.
  7. Oak-hornbeam and oak-lime woodlands (Carpinion)

    Mostly mesophilous, broad-leaved (dom. Carpinus betulus, Quercus petraea, Q. robur, Tilia cordata), rarely mixed, climax woodlands with Abies alba or Picea abies, on mesotrophic to eutrophic brown earths, from planar to colline, or submontane levels:

  8. Melampyro nemorosi-Carpinetum (dom. Quercus petraea, Carpinus betulus, with Tilia cordata or T. platyphyllos, Quercus robur and many other [hygro]mesophilous woody species) at planar to supracolline levels, with the optimum at colline levels.
  9. Tilio-Betuletum (dom. Quercus petraea, rarely Tilia cordata or Q. robur), on poorer, mostly drier soils, transitional type to acidophilous oak woodland at lower levels of Bohemia.
  10. Primulo veris-Carpinetum (dom. Carpinus betulus, Quercus petraea or Q. robur), with many thermophilous species in Pannonian part of S. Moravia.
  11. Carici pilosae-Carpinetum (dom.Carpinus betulus or Quercus petraea, with frequent Tilia cordata and Fagus sylvatica), with Carex pilosa, Euphorbia amygdaloides, Symphytum tuberosum, Salvia glutinosa etc. at lower levels of the W. Carpathians.
  12. Tilio-Carpinetum (dom. Carpinus betulus, Tilia cordata, Quercus robur, with natural occurrence of Picea abies, Populus tremula and Sorbus aucuparia), with many hygrophilous species at colline levels of Silesia and adjoining parts of Moravia.
  13. Stellario-Tilietum (dom. Tilia cordata or Quercus robur, with absence of Q. petraea and Carpinus betulus), in the river valleys of S. Bohemia.
  14. Scree and ravine woodlands (Tilio-Acerion)

    Permanent communities of broad-leaved (Carpinus betulus, Acer pseudoplatanus, A. platanoides, Fraxinus excelsior, Ulmus glabra), rarely mixed woodlands with Taxus baccata or Abies alba on scree and boulder slopes with immature soils at colline to montane levels. There is only one mapping unit:

  15. including Aceri-Carpinetum, Lunario-Aceretum, Mercuriali-Fraxinetum and Scolopendrio-Fraxinetum.
  16. Herb-rich beech woodlands (Eu-Fagenion)

    Beech, silver fir-beech and lime-beech climax or sub-climax woodlands (Fagus sylvatica, Abies alba, Tilia cordata, T. platyphyllos) with frequent herbs, rarely sedges or grasses, on siliceous brown earths at submontane and montane levels:

  17. Tilio platyphylli-Fagetum (dom. Fagus sylvatica, with frequent Tilia platyphyllos), locally conditioned unit at submontane levels on tertiary eruptives of N Bohemia.
  18. Tilio cordatae-Fagetum (dom. Fagus sylvatica, with Carpinus betulus, Tilia cordata, Quercus petraea, less frequently Abies alba) at submontane levels of Central, S and W Bohemia.
  19. Melico-Fagetum (dom. Fagus sylvatica), herb- and Melica uniflora-rich, mostly at submontane levels of N and Central Moravia.
  20. Carici pilosae-Fagetum (dom. Fagus sylvatica, with frequent admixture of Quercus petraea), with predominant Carex pilosa, mostly at submontane levels of the Carpathians.
  21. Dentario enneaphylli-Fagetum (dom. Fagus sylvatica with Acer pseudoplatanus and Abies alba, at higher levels Picea abies) with Dentaria eneaphyllos, at (sub)montane levels. The most frequent beech woodland of the whole Republic.
  22. Dentario glandulosae-Fagetum, a similar unit, with Dentaria glandulosa, at montane levels in E Moravia.
  23. Festuco altissimae-Fagetum with the same woody species as the two foregoing units, with a relatively species-poor herb layer (dom. Festuca altissima), on relatively poor substrates at (sub)montane levels.
  24. Violo reichenbachianae-Fagetum (dom. Fagus sylvatica, with Acer pseudoplatanus, Fraxinus excelsior), with frequent Hordelymus europaeus, at (sub)montane levels of NW Bohemia.
  25. Calcicolous beech woodlands (Cephalanthero-Fagenion)

    Beech woodlands (Fagus sylvatica) on rendzina soils on substrates rich in carbonates or with an admixture of CaCO3, mostly at submontane, rarely montane, levels:

  26. Cephalanthero-Fagetum (dom. Fagus sylvatica, with many broad-leaved woody species), with numerous orchids (Cephalanthera damasonium, C. rubra, Epipactis helleborine, Corallorhiza trifida, Neottia nidus-avis) and some thermophilous species.
  27. Herb-rich silver fir forests (Galio-Abietenion)

    Fir forests (Abies alba) rich in species, on heavy, gley or pseudogley, poorly drained soils of depressions or convex slopes, mostly at submontane levels of SW. and Central Bohemia:

  28. Saniculo europaeae-Abietetum (dom. Abies alba, rarely with other woody species), with indicators of fir woodlands (Galium rotundifolium, Sanicula europaea, Luzula pilosa).
  29. Acidophilous beech and fir woodlands (Luzulo-Fagion)

    (Hygro)mesophilous- to mesophilous species-poor beech and fir woodlands (Fagus sylvatica, Abies alba) on oligotrophic siliceous soils at submontane to supramontane levels, and waterlogged oak-beech woodlands on pseudogleys at lower levels in NE Moravia:

  30. Luzulo-Fagetum (dom. Fagus sylvatica, at lower levels with Quercus petraea) with prevailing (sub)acidophytes, species-poor, on oligotrophic brown earths at (sub)montane levels.
  31. Calamagrostio villosae-Fagetum (dom. Fagus sylvatica, Picea abies, with Acer pseudoplatanus and Abies alba), mostly on semipodsols at (supra)montane levels.
  32. Carici brizoidis-Quercetum (dom. Quercus robur, Fagus sylvatica, on moist sites with Alnus glutinosa, Betula pubescens, with B. pendula, Populus tremula), with prevailing (sub)acidophytes, on pseudogleys at lower levels of NE and E Moravia.
  33. Deschampsio flexuosae-Abietetum, fir stands on oligotrophic sites, influenced by climatic inversions, mostly in deep submontane valleys of SW Bohemia.
  34. Perialpidic basiphilous thermophilous oak woodlands (Quercion pubescenti- petraeae)

    Thermophilous oak woodlands (Quercus pubescens and/or Q. petraea) on (moderately) nutrient-rich substrates containing CaCO3, mostly at planar and colline levels in warm and dry areas.

  35. Lathyro versicoloris-Quercetum pubescentis (dom. Quercus pubescens), with Lathyrus pannonicus, and Torilido-Quercetum (Quercus petraea) with frequent Buglossoides purpurocaerulea, both with many other (sub)thermophilous species, in the warmest and driest areas of Bohemia.
  36. Pruno mahaleb-Quercetum pubescentis (dom. Quercus pubescens and Cerasus mahaleb) on extremely dry sites) and Corno-Quercetum (Quercus petraea, with Fraxinus excelsior, Carpinus betulus) on less warm and less dry sites of Moravia.
  37. Undetermined basiphilous thermophilous woodlands (dom. Quercus petraea, rarely Q. robur, with Pinus sylvestris), with many (sub)xerothermic woodland species, frequently in complex with calcareous pine woodlands on mineral-rich substrates.
  38. Subcontinental thermophilous oak woodlands (Aceri tatarici-Quercion)

    Oak woodlands (Quercus petraea, Q. pubescens, Q. robur) on chernozem (on loess) or cambisols (on sands), mostly on flat sites at planar and colline levels in the Pannonian area of S Moravia, at the NW limit of their distribution:

  39. Quercetum pubescenti-roboris (dom. Quercus petraea, Q. pubescens, Q. robur) on loess, with elements of thermophilous and mesophilous woodlands (Buglossoides purpurocaerulea, Carex michelii, Dictamnus albus, Iris graminea, I. variegata, Galium sylvaticum, Mercurialis perennis) in Pannonian S Moravia.
  40. Carici fritschii-Quercetum roboris (dom. Quercus robur) with frequent Carex fritschii, elements of open thermophilous and mesophilous woods, and species of oligotrophic and alternating moist soils (Geranium sanguineum, Iris variegata, Festuca ovina, Potentilla alba, Serratula tinctoria) on cambisols of sand dunes, covering tertiary clays in S Moravia.
  41. Subacidophilous Central-European thermophilous oak woodlands (Quercion petraeae)

    Oak woodlands (Quercus petraea or Q. robur), on poor soils of siliceous substrates on relatively cold and moist sites at planar and (supra)colline levels:

  42. Potentillo albae-Quercetum (Quercus petraea, Q. robur, rarely Carpinus betulus, Tilia cordata) on illimerized brown earths to pseudogleys at planar to colline levels.
  43. Sorbo torminalis-Quercetum (dom. Quercus petraea, with thermophilous Sorbus- species) on shallow, oligotrophic soils of dry, sunny sites, mostly at colline levels.
  44. Asplenio cuneifolii-Quercetum petraeae (dom. Quercus petraea, with Pinus sylvestris), open woodland with thermophilous species on Mg-rich rendzinas on serpentine substrates of steep, sunny slopes in valleys of the Jihlava- and ¦elivka- rivers.
  45. Acidophilous oak woodlands (Genisto germanicae-Quercion)

    Species-poor broad-leaved (Quercus petraea, Q. robur) or mixed (Abies alba or Pinus sylvestris) oak woodlands, with grasses, Juncaceae or dwarf shrubs on nutrient-poor substrates at planar and colline, locally submontane, levels:

  46. Luzulo albidae-Quercetum petraeae, Abieti-Quercetum (dom. Quercus petraea, Q. robur, with Abies alba and a slight admixture of other woody species) on (meso)oligotrophic brown earths, very frequent in Bohemia.
  47. Molinio arundinaceae-Quercetum (dom. Quercus robur), with Molinia arundinacea and/or Carex brizoides on heavy, pseudogley soils in depressions, mostly at colline levels, frequent in Silesia. Vicariant of (sub)Atlantic birch-oak woods.
  48. Vaccinio vitis-idaeae-Quercetum (dom. Quercus petraea, rarely Q. robur, with Pinus sylvestris), with prevailing dwarf shrubs (Vaccinium myrtillus, V. vitis-idaea) on very-strongly acidic oligotrophic soils at supracolline (to submontane) levels.
  49. Festuco ovinae-Quercetum roboris, open pine-oak woodlands with (sub)thermophilous woodland species and psammophilous elements on arenic cambisols of lowlands.
  50. Basiphilous perialpine pine woodlands (Erico-Pinion)

    Open pine woods (Pinus sylvestris) with peri-alpine species (Biscutella laevigata, Myosotis stenophylla, Thesium alpinum, Thlaspi montanum) and elements of serpentine rocks (Asplenium cuneifolium, Armeria vulgaris subsp. serpentini) on Mg-rich rendzinas on steep slopes at colline levels:

  51. Thlaspio montani-Pinetum sylvestris, in valleys of the Jihlava- and ¦elivka- rivers.
  52. Acidophilous pine woodlands (Dicrano-Pinion)

    Primary relict rocky pine woods (Pinus sylvestris), partly in mosaics with boulder- spruce forests on dystrophic rankers or podsols, and pine woods on oligotrophic soils of sands and sandy terraces:

  53. Betulo carpaticae-Pinetum with Anastrepto-Piceetum (dom. Pinus sylvestris and/or Picea abies, with Betula carpatica, Abies alba or Sorbus aucuparia), (sub)montane stands on shallow dystrophic rankers in sandstone areas of NE Bohemia.
  54. Further Dicrano-Pinion comm. (dom. Pinus sylvestris) on rocky habitats, oligotrophic sands and sand terraces, including: Dicrano-Pinetum, Asplenio cuneifolii-Pinetum sylvestris, Hieracio pallidi-Pinetum, Cardaminopsio petraeae- Pinetum.
  55. Climax and waterlogged spruce forests (Piceion excelsae)

    Natural spruce forests (Picea abies) with a dominance of dwarf shrubs or grasses and with a well developed and species-rich moss layer on podsols and podsol-cambisols of siliceous substrates at supramontane levels, and waterlogged, edaphically determined moss- and Sphagnum-rich spruce forests on stagnogleys, gley podsols and peaty gleys in waterlogged depressions, mostly at (sub)montane levels:

  56. Calamagrostio villosae-Piceetum (dom. Picea abies, with frequent Sorbus aucuparia, rarely, at lower levels, Fagus sylvatica or Abies alba), with predominant Calamagrostis villosa or Vaccinium myrtillus, at (supra)montane levels.
  57. Mastigobryo-Piceetum, partly with Sphagno-Piceetum (dom. Picea abies), waterlogged stands with a dense and species-rich moss layer (principally Sphagnum- species).
  58. Montane to supramontane fern-rich spruce forests (Athyrio alpestris-Piceion)

    Species and fern-rich spruce forests (Picea abies) with many elements of high-montane tall-herb communities on moist oligotrophic soils on steep slopes, permanently saturated by groundwater, at montane and supramontane levels:

  59. Athyrio alpestris-Piceetum (dom. Picea abies), with Athyrium distentifolium and tall herbs (Veratrum lobelianum, Rumex alpestris, Cicerbita alpina), with a weakly developed moss layer, in cold areas with frequent fogs and a high snow cover. Subalpine and alpine vegetation (Pinion mughi, Juncetea trifidi, Mulgedio- Aconitetea, Salicetea herbaceae etc.) Complex of vegetation units of open subalpine areas above the tree line, with a high diversity of species and communities, on the summits of the Sudeten Mts.:
  60. Pinion mughi, Juncetea trifidi, Mulgedio-Aconitetea, Salicetea herbaceae etc., very heterogeneous, species-rich (ca. 600 species) group of communities with many endemic species and associations (belonging to 9 classes), of which summit tundra vegetation, tall-herb and tall-grass stands are the most frequent.
  61. Mires (Scheuchzerio-Caricetea fuscae, Oxycocco-Sphagnetea)

    Complex of mire vegetation from sedge- and sedge-moss-rich types to raised bogs at planar to subalpine levels.

  62. Caricetalia fuscae (dom. Cyperaceae, Poaceae and Juncaceae and/or Bryidae) on shallow minerotrophic peats from lowland to submontane levels.
  63. Scheuchzerietalia palustris (excl. Leuko-Scheuchzerion palustris) (dom. Cyperaceae and Sphagnidae), almost always covering mesotrophic to oligotrophic peat substrates at (sub)montane, rarely subalpine, levels.
  64. Pino rotundatae-Sphagnetum, Eriophoro vaginati-Pinetum sylvestris, Vaccinio uliginosi-Pinetum sylvestris (dom. Pinus rotundata, P. sylvestris, with Picea abies, Betula pubescens), with dwarf shrubs and herbs, and Sphagnum-species.
  65. Sphagnetalia medii excl. syntaxa mentioned sub (49), partly with Pinus mugo and/or Sphagno-Piceetum with dwarf shrubs, Cyperaceae, and prevailing acidophilous Sphagnum-species of oligotrophic to dystrophic habitats at (supra)montane, rarely subalpine levels.

  66. Vegetation on sites strongly influenced by human activity
  67. Complex of successional stages with stabilized Betula pendula-Calamagrostis epigejos comm. in NW Bohemia.
The currently developing open vegetation on raw substrates (tertiary clays) on open- cast coal mines.

Together with the compilation of the map, the explanatory text for the mapping units mentioned above has been prepared.

This text is divided into two parts: the first part includes general information on the physical-geographical characteristics of the country, basic information on vegetation mapping in the Republic, history of the vegetation during the last 15 OOO years and methodology. The second, more detailed, part includes characteristics of the mapping units (data on the most frequent synonyms, structure and species composition, diagnostic species combination, floristic differentiation from the most closely related mapping units, developmental stages, associated natural vegetation in complex with individual mapping units, adjoining potential natural vegetation, habitat and distribution, substitute communities, land use, importance for nature conservation and landscape planning, rare and endangered taxa and syntaxa, most important references, examples of typical relev‚s or synthetic tables, and data on invasive and expansive species in the area of the mapping unit. Beside the Map of Potential Natural Vegetation, the text has been completed by synthesized maps of the distribution of groups of mapping units, figures, and colour photos. It will be printed at the end of 1998.


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