T1Bx Mixed forests on acid soils

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Description

Acidophilous zonal forests in the lowlands of the northern, maritime territories of the ecoregion, where summer-droughts are rare and mild, soils remaining moist enough for deciduous broadleaved trees to support the high transpiration rates of their competitive light-capturing apparatus. Usually dominated by pedunculate oak, but with a pretty diverse tree layer including sweet chestnut, birch, ash and wild cherry.

Protection

Managed stands rich in sweet chestnut are protected by the EU Habitat Directive under the code 9260 ("Castanea sativa woods").

Floristic Composition

Frequent species

Quercus robur 98%, Pteridium aquilinum 82%, Hedera helix aggr. 77%, Lonicera periclymenum 61%, Teucrium scorodonia 60%, Castanea sativa 55%, Viola riviniana aggr. 47%, Blechnum spicant 44%, Ruscus aculeatus 41%, Ilex aquifolium 40%, Frangula alnus 40%, Rubus ulmifolius 39%, Corylus avellana 36%, Crataegus monogyna 35%, Dioscorea communis 33%, Holcus mollis 31%, Euphorbia amygdaloides 30%, Stellaria holostea 29%, Potentilla erecta 26%, Erica arborea 25%, Vaccinium myrtillus 24%, Euphorbia dulcis 24%, Brachypodium sylvaticum 24%, Hypericum pulchrum 23%, Daboecia cantabrica 23%, Avenella flexuosa 23%, Brachypodium pinnatum 22%, Melampyrum pratense 20%, Erica vagans 20%, Agrostis capillaris 20%, Helictotrichon thorei 20%, Anthoxanthum odoratum 19%, Asphodelus albus 19%, Stachys officinalis 19%, Arenaria montana 18%, Polystichum setiferum 18%, Laurus nobilis 18%, Hypericum androsaemum 17%, Ranunculus tuberosus aggr. 17%, Digitalis purpurea 17%, Ulex minor aggr. 17%, Dryopteris affinis 17%, Asplenium adiantum-nigrum aggr. 17%, Quercus pyrenaica 16%, Calluna vulgaris 16%, Pulmonaria longifolia 15%, Polypodium vulgare 15%, Rubia peregrina 15%, Fraxinus excelsior 15%, Prunus spinosa 15%, Betula celtiberica 15%, Cornus sanguinea 15%, Cytisus scoparius 14%, Athyrium filix-femina 14%, Geranium robertianum 14%, Oxalis acetosella 14%, Physospermum cornubiense 13%, Omphalodes nitida 13%, Ulex europaeus aggr. 13%, Ajuga reptans 12%, Fagus sylvatica 12%, Pyrus communis 12%, Primula acaulis 12%, Solidago virgaurea 12%, Lathyrus linifolius 12%, Prunus avium 11%, Fragaria vesca 11%, Dactylis glomerata 11%, Crepis lampsanoides 11%, Pyrus cordata 11%, Arbutus unedo 11%, Centaurea nigra 11%, Anemone nemorosa 11%, Rumex acetosa 11%, Arum italicum 10%, Smilax aspera 10%, Glandora prostrata 9%, Erica cinerea 9%, Salix atrocinerea 8%, Potentilla sterilis 8%, Veronica officinalis 8%, Dryopteris borreri 8%, Acer campestre 8%, Rosa arvensis 8%, Luzula sylvatica 8%, Hyacinthoides non-scripta 8%, Danthonia decumbens 8%, Polygonatum odoratum 8%, Vicia sepium 8%, Linaria triornithophora 7%, Hieracium prenanthoides aggr. 7%, Rosa sempervirens 7%, Picris hieracioides 7%, Luzula forsteri 7%, Sanicula europaea 7%, Ligustrum vulgare 7%, Circaea lutetiana 6%, Saxifraga spathularis 6%, Prunella vulgaris 6%, Aquilegia vulgaris aggr. 6%, Rubus lainzii 6%, Acer pseudoplatanus 6%, Cruciata glabra 6%, Festuca rubra 6%, Dryopteris dilatata 6%, Carex sylvatica 6%, Helleborus viridis 6%, Euonymus europaeus 6%, Simethis mattiazzii 6%, Rosa canina aggr. 5%, Cardamine pratensis 5%, Agrostis curtisii 5%, Clinopodium vulgare 5%, Cytisus striatus 5%, Sorbus aucuparia 5%

Phytosociology

  • Blechno spicant-Quercetum roboris
  • Hyperico pulchri-Quercetum roboris
  • Lonicero periclymeni-Quercetum pyrenaicae
  • Rusco aculeati-Quercetum roboris
  • Vaccinio myrtilli-Quercetum roboris
  • Viburno tini-Quercetum roboris

Relations with other habitat types

A new regional level IV unit is created, since the fusion of this acidophilous analogue of T1E1 with the montane forests of T1By is, for deep floristic and ecological reasons, quite unsatisfactory at that level. In the lowest areas, where severe frosts and snowfalls are a rare occurrence, they may transition towards T22x. At somewhat higher elevations or in particularly well-oriented valleys, rainier and cooler summers reduce even further the risk and severity of droughts and lead to the predominance of T182. In southern Galician and northern Portuguese coastal areas, on their part, sunny and dry summers lead to somewhat complex transitions towards T211. A number of higher level units recognised by EUNIS intend to capture all these transitions: T1B621 ("Eastern Cantabrian acidophilous oak forests"); T1B622 ("Western Cantabrian acidophilous oak forests"); T1B631 ("Mesophile Luso-Galician collinar oak forests"); T1B632 ("Humid Luso-Galician collinar oak forests"); T1B64 ("Luso-Galician montane acidophilous oak forests"). Traditional, centuries-old management has often transformed these communities into chestnut-enriched woodlands exploited for timber or fruit.

Regional distribution

These forests were cleared in a great proportion many centuries ago, both as a source of wood and as a way to create more productive, non-ligneous vegetation that humans can consume directly or through livestock intermediation. Most of their ancient domain is currently occupied by grasslands (R1M2, R211), shrublands (especially S332) or, when soil is eroded after burning for pastures, aggravating the intrinsic oligotrophy of these siliceous substrates, by heathlands (S42x); as well as, more recently, by pine or eucalyptus industrial plantations. Most of the remaining stands are quite managed (see above).

Known occurrences and potential area of occupancy of the habitat type in the study region.