Basophilous deciduous species-rich forests in temperate lowlands and midlands whose climate, by any combination of frequent input by rains and modest water loss through scarce direct sunshine, lacks any Mediterranean nuance, enabling the development of deep, humid but aerated, well-developed eutrophic soils.
Protection
In Spain, despite a certain mismatch in its definition, most of these forests have been traditionally considered protected by the EU Habitat Directive through their assimilation to code 9160 ("Sub-Atlantic and medio-European oak or oak-hornbeam forests of the Carpinion betuli"). Variants in steep, rocky and shady slopes (see below) may on their part be taken as protected with priority under 9180* ("Tilio-Acerion forests of slopes, screes and ravines").
Floristic Composition
Floristic Composition
Frequent species show the percentage of occurrence of species in each habitat, with higher values indicating more observations within the total number of samples. Indicator species show the fidelity of species to each habitat, with higher values indicating a stronger association, based on the IndVal metric (Dufrêne & Legendre, 1997). All species values were obtained from numerical classification (Jiménez-Alfaro et al. 2025). The classification of anthropogenic habitats (EUNIS code “V”) was conducted separately (Fernández-Pascual et al. 2025).
References
Dufrêne, M., & Legendre, P. (1997). Species assemblages and indicator species: the need for a flexible asymmetrical approach. Ecological monographs, 67(3), 345-366.
Fernández-Pascual, E., González-García, V., Ivesdal, G., Lázaro-Lobo, A., & Jiménez-Alfaro, B. (2024). Classification and Characterization of Anthropogenic Plant Communities in the Northwestern Iberian Peninsula. Applied Vegetation Science, 28(1), e70010. https://doi.org/10.1111/avsc.70010
Jiménez-Alfaro, B., González Le Barbier J., Carlón L., Álvarez Martínez JM, Espinosa del Alba, C., Fernández-Pascual, E., González-García V., Lázaro-Lobo A, Mendieta-Leiva, Roces Díaz JV (2025) Regionalization of European EUNIS habitat classification for effective ecosystem assessment. In prep.
List of phytosociological associations described in the Ibero-Atlantic region for each habitat. The association concepts mainly follow Rivas-Martinez et al. (2001), with further updates by Fernández-Prieto et al. (2023), and others.
References
Rivas-Martinez, S., Fernández González, F., Loidi Arregui, J., Fernández Lousã, M. & Penas Merino, A. (2001) Sintaxonomical checklist of vascular plant communities of Spain and Portugal to association level. Itinera Geobotanica 14., 5-341.
Fernández Prieto, J.A., Amigo, J., Bueno, A., Herrera, M., Rodríguez-Guitián, M.A. & Loidi, J. (2023) Bosques y orlas forestales de los territorios atlánticos del Noroeste Ibérico. Guineana, 23, 3–240 https://doi.org/10.1387/guineana.25055
Carici pendulae-Fraxinetum excelsioris
Crataego laevigatae-Quercetum roboris
Euphorbio hybernae-Fraxinetum excelsioris
Festuco giganteae-Fraxinetum excelsioris
Fraxino angustifoliae-Ulmetum glabrae
Helictotricho cantabrici-Tilietum platyphylli
Helleboro occidentalis-Tilietum cordatae
Hyperico androsaemi-Coryletum avellanae
Hyperico androsaemi-Quercetum roboris
Hyperico androsaemi-Ulmetum glabrae
Laserpitio eliasii-Coryletum avellanae
Luzulo henriquesii-Aceretum pseudoplatani
Omphalodo nitidae-Coryletum avellanae
Polysticho setiferi-Fraxinetum excelsioris
Pulmonario longifoliae-Quercetum pyrenaicae
Saxifrago hirsutae-Coryletum avellanae
Smilaco asperae-Coryletum avellanae
Valeriano pyrenaicae-Fraxinetum excelsioris
Relations with other habitat types
A mostly basophilous, more eutrophic analogue of T1Bx, functioning as the zonal forest in the north of the ecoregion, either below T172 beechwwods (with Quercus robur as the dominant oak in mature stands) or, when in montane areas, replacing them in sunnier slopes, with Quercus peatraea as the dominant oak. In acidic areas it takes the place of, or intermixes with, said T1Bx in colluvia or valley sides, whose soils are deepened and enriched by materials eroded from upper-lying areas. It may even act as a riverine formation, instead of T111 and T121, in modest watercourses with negligible floodplain and almost dry in summer. In the coast, transitions towards T22x are widespread. It is also successionally and spatially very close to S371, with a vast shared floristic background. In narrow valleys and gorges, including steep foothills where coarse colluvia are deposited, lime trees may gain abundance, suggesting the convenience of admitting EUNIS T1F ("Ravine forest"), whose regional representative would be T1F4 ("Pyreneo-Cantabrian mixed Ulmus-Quercus forests"). However, the distinction between blocks T1E and T1F, at least on floristic grounds, is shaky, as shown by the very name (let alone the respective descriptions) of the level V regional EUNIS within T1E1: T1E19 ("Pyreneo-Cantabrian Quercus-Fraxinus forests"). Therefore, at least for the time being and at level IV, all these eutrophic mixed forests of the ecoregion, regardless of their topographic position, are joined together.
The fertile soils that these forests occupied and contributed to generate (by releasing a nutrient rich, readily humified litter) were massively turned many centuries ago into cultures, orchards and (especially during the XXth century marketisation and increasing cattle-specialisation of Iberoatlantic rural economies) meadows (R211, R221). Most of the remaining stands are immature, particularly rich in wind-dispersed species like ash and maple, or developed in particularly steep places, unsuitable for agriculture (especially if mechanised, having led to a certain recovery in recent decades).
Regional distribution
Occurrence data show the locations of vegetation plots from SIVIM (Font, 2023) classified into habitat types by Jiménez-Alfaro et al. (2025). Distribution errors (outliers) may occur in vegetation plots with few species or transitional ecological conditions. The potential area of occupancy shows the environmental suitability predicted for each habitat (González Le Barbier et al. 2025), with higher values indicating more suitable climate and soil for the habitat.
References
Font, X. (2023). Sistema de Información de la vegetación Ibérica y Macaronésica. Version 1.6. Banc de dades de biodiversitat de Catalunya. http://www.sivim.info/sivi/.
Jiménez-Alfaro, B., González Le Barbier J., Carlón, L., Espinosa del Alba, C., Fernández-Pascual, E., González-García, V., Lázaro-Lobo, A. Adapting EUNIS habitat classification at the regional scale: a case study in the Ibero-Atlantic biogeographic region. In prep.
González Le Barbier, J., Ubaldi, T., Lenoir, J., Roces Díaz, J. & Jiménez-Alfaro, B. (2025) Modelling the area of occupancy of habitat types at different successional stages. In prep.
Known occurrences and potential area of occupancy of the habitat type in the study region.