Research Article |
Corresponding author: Danièle Lagnaz ( daniele.lagnaz@zhaw.ch ) Academic editor: Daniele Viciani
© 2023 Danièle Lagnaz, Giacomo Trotta, Patrice Prunier, Bertil Krüsi, Francesco Boscutti.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Lagnaz D, Trotta G, Prunier P, Krüsi B, Boscutti F (2023) Acidophilous grasslands in the Locarnese region (Southern Switzerland): description and classification of main plant communities. Plant Sociology 60(2): 71-91. https://doi.org/10.3897/pls2023602/05
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This paper presents a phytosociological study of dry and mesophilous meadows and pastures in the Locarnese region (Insubria - Southern Switzerland). Seventy-one vegetation relevés were analysed using both hierarchical classification and nonmetric multidimensional scaling (NMDS) ordination. Seven main clusters were identified and described as follows: (i) xerophytic grasslands on sandy soil dominated by Koeleria macrantha; (ii) mesophilous meadows with Arrhenatherum elatius and Centaurea transalpina; (iii) semi-dry meadows with Chrysopogon gryllus; (iv) semi-dry grasslands with Carex fritschii and Thalictrum minus; (v) nutrient-poor Phyteuma betonicifolium-Festuca nigrescens montane zone grasslands; Nardus stricta grasslands dominated by (vi) Festuca paniculata or (vii) Carex pilulifera. From a phytosociological point of view, a new association named Phyteumo betonicifolii-Festucetum nigrescentis, classified into the Nardo strictae-Agrostion tenuis alliance was proposed. In addition, we confirmed the presence of the Holco-Chrysopogonetum grylli association, within the Bromion erecti, which up to now was provisional only.
dry meadows, Festuco-Brometea, Insubria, Molinio-Arrhenatheretea, Nardetea strictae, phytosociology, pastures
The Semi-natural temperate grasslands are plant communities that arose from the non-intensive use of pastures and meadows (
The first study on Swiss grassland vegetation was published in 1887 by Stebler & Schröter. Since then, studies have been performed in various regions of Switzerland (
In Switzerland, so far, only few studies have dealt with the flora and vegetation of the Insubrian region South of the Alps (
For the Canton of Ticino, early comprehensive studies were performed by
This paper proposes a phytosociological overview of the siliceous meadows and pastures in the foothills and montane zone of the Locarnese region (200–1,500 m a.s.l.). The aims of the study were to describe and classify grassland communities occurring in the area. The study is expected to shed new light on the phytosociological classification of these grasslands and to test the occurrence of new plant associations specific to the Insubrian region.
The study area covered approximately 230 km2 in the Canton of Ticino (Fig.
From a biogeographical point of view, the Locarnese region is particularly interesting due to its geological and climatic features. These characteristics result in a unique floristic diversity that was early recognized (
From a geological point of view, the Locarnese has a special position. The Insubric Line, a fault line between the European and African plates, passes across the Centovalli. It marks the boundary between the Central Alps and the Southern Alps and is the southern limit of Alpine metamorphism. A mylonite belt surrounds this line, with ultramafic, mafic and paragneisses to the South, and gneiss, metagranitoide and mica-slate to the North (
The Insubrian climate (Fig.
In the foothill zone, forests are composed by deciduous tree species. Forests dominated by Castanea sativa are the most abundant and account for 20% of the total forested area in Ticino (Dipartimento del territorio 2008). On siliceous soil, Quercus sp.-Betula pendula forests, belonging to the Quercion-robori petraeae alliance, is the potential natural vegetation. Above an altitude of 800 m a.s.l., the main forest types are characterised by Fagus sylvatica and Abies alba (
Study area in the Locarnese region, Ticino - Switzerland. Copyright: data swisstopo, https://map.geo.admin.ch/.
Seventy-one vegetation relevés were analyzed. This includes 70 surveys conducted during spring and summer of 2016 and 2017, as well as one survey from the national inventory of dry meadows and pastures (
All relevés were performed using the Braun-Blanquet approach (
The species cover values were transformed into ordinal scale values according to
Indicators for the four main clusters and eight sub-clusters were determined using Indicator Species Analysis (ISA) as proposed by
Ecological characterization of the clusters was performed using weighted mean indicator values according to
Phytosociological attributions of species and floristic nomenclature were performed according to Flora Indicativa (
Calculation of mean Landolt’s indicator values (
The results of the cluster analysis are shown in Figure
The ordination diagram obtained using nonmetric multidimensional scaling (NMDS) calculated along the first two axes (Fig.
Dendrogramme of 71 phytosociological relevés (Bray-Curtis Index, WPGMA). A: Grasslands with Koeleria macrantha; B: Grasslands with Festuca nigrescens; A1: Stipo-Poion xerophilae; B1: Arrhenatherion; B2: Bromion erecti; B3: Nardo-Agrostion; a: Poo bulbosae-Festucetum trachyphyllae; b: Poo bulbosae-Festucetum trachyphyllae, mesophilic variant c: Centaureo transalpinae-Arrhenatheretum; d: outlier; e: Holco-Chrysopogonetum grylli; f: Phyteumo-Mesobrometum; g: Phyteumo betonicifolii-Festucetum nigrescentis; h: Carici piluliferae-Nardetum strictae.
Ordination diagram of the total 71 relevés (NMDS). a: Poo bulbosae-Festucetum trachyphyllae; b: Poo bulbosae-Festucetum trachyphyllae, mesophilic variant c: Centaureo transalpinae-Arrhenatheretum; d: outlier; e: Holco-Chrysopogonetum grylli; f: Phyteumo-Mesobrometum; g: Phyteumo betonicifolii-Festucetum nigrescentis; h: Carici piluliferae-Nardetum strictae (for species abbreviations see Appendix IV).
Poo bulbosae-Festucetum trachyphyllae
Relevé number | 72 | 42 | 8 | 7 | 66 | Presence |
Altitude (m a.s.l.) | 286 | 310 | 230 | 220 | 229 | |
Aspect | - | - | - | - | - | |
Slope (degree) | 0 | 0 | 0 | 0 | 0 | |
Relevé area (m2) | 25 | 25 | 25 | 25 | 25 | |
Species number | 21 | 17 | 26 | 25 | 20 | |
Total coverage (%) | . | 90 | 90 | 90 | 90 | |
Characteristic and differential species of Poo bulbosae-Festucetum trachyphyllae | ||||||
Koeleria macrantha (Lam.) P. Beauv. | + | 3 | 1 | 1 | 2 | 5 |
Rumex acetosella L. s.l. | . | 1 | 1 | 2 | 1 | 4 |
Characteristic species of Stipo-Poion xerophilae and Festucetalia valesiaceae | ||||||
Achillea collina | + | 1 | 1 | . | . | 3 |
Festuca ovina aggr. (Festuca trachyphylla R. Tracey pro maxima parte) | 2 | 1 | . | . | . | 2 |
Carex liparocarpos Gaudin | . | 1 | . | . | . | 1 |
Pseudolysimachion spicatum (L.) Opiz | . | . | . | + | . | 1 |
Characteristic species of Festuco-Brometea and subordinate units | . | . | . | . | . | |
Artemisia campestris L. s.l. | + | 2 | . | r | + | 4 |
Carex caryophyllea Latourr. | 1 | . | 1 | 2 | 1 | 4 |
Euphorbia cyparissias L. | . | 1 | 1 | 1 | 1 | 4 |
Lotus corniculatus L. s.l. | . | 1 | + | + | + | 4 |
Ranunculus bulbosus L. | + | . | r | r | + | 4 |
Thymus pulegioides L. | . | + | + | + | 1 | 4 |
Bromus erectus Huds. | . | . | 1 | 2 | 2 | 3 |
Dianthus carthusianorum L. s.l. | 1 | r | . | . | + | 3 |
Helianthemum nummularium (L.) Mill. | + | . | + | 1 | . | 3 |
Potentilla neumanniana Rchb. | 1 | + | . | 1 | . | 3 |
Anthericum liliago L. | . | . | . | 1 | + | 2 |
Centaurea splendens L. | . | . | . | + | + | 2 |
Trifolium montanum L. | . | . | 2 | + | . | 2 |
Centaurea scabiosa L. | . | . | + | . | . | 1 |
Euphrasia stricta J. F. Lehm. | . | . | . | . | 1 | 1 |
Galium verum L. s.l. | . | . | + | . | . | 1 |
Luzula campestris (L.) DC. | . | . | 2 | . | . | 1 |
Orchis morio L. | . | . | . | 1 | . | 1 |
Orchis ustulata L. | . | . | . | r | . | 1 |
Salvia pratensis L. | . | . | + | . | . | 1 |
Thesium linophyllon L. | . | . | . | 1 | . | 1 |
Hypochaeris maculata L. | . | . | . | + | . | 1 |
Plantago media L. | + | . | . | . | . | 1 |
Poa angustifolia L. | . | . | . | 1 | . | 1 |
Companion species | ||||||
Koelerio-Corynephoretea and subordinate units | ||||||
Jasione montana L. | + | + | . | . | + | 3 |
Aira caryophyllea L. | 2 | + | . | . | . | 2 |
Hypochaeris radicata L. | 1 | . | . | . | . | 1 |
Sedum sexangulare L. | + | . | . | . | . | 1 |
Trifolium arvense L. | . | . | . | . | + | 1 |
Molinio-Arrhenatheretea and subordinate units | ||||||
Plantago lanceolata L. | 1 | . | 1 | + | 1 | 4 |
Agrostis capillaris L. | 2 | . | . | . | 1 | 2 |
Anthoxanthum odoratum L. | + | . | 1 | . | . | 2 |
Cerastium fontanum subsp. vulgare (Hartm.) Greuter & Burdet | . | . | 1 | r | . | 2 |
Dactylis glomerata L. | . | . | 1 | . | . | 1 |
Erigeron annuus (L.) Desf. s.l. | . | . | . | . | 1 | 1 |
Festuca nigrescens Lam. | . | . | + | . | . | 1 |
Knautia arvensis (L.) Coult. | + | . | . | . | . | 1 |
Other species | ||||||
Peucedanum oreoselinum (L.) Moench | 1 | + | 2 | 2 | 3 | 5 |
Chrysopogon gryllus (L.) Trin. | . | . | 1 | 2 | . | 2 |
Hypericum perforatum L. | . | . | r | . | + | 2 |
Calluna vulgaris (L.) Hull | . | . | . | r | . | 1 |
Cytisus scoparius (L.) Link /S | + | . | . | . | . | 1 |
Danthonia decumbens (L.) DC. | 1 | . | . | . | . | 1 |
Echium vulgare L. | . | + | . | . | . | 1 |
Festuca filiformis Pourr. | . | 1 | . | . | . | 1 |
Hieracium pilosella aggr. | . | . | 1 | . | . | 1 |
Hieracium piloselloides Vill. | . | + | . | . | . | 1 |
Phyteuma betonicifolium Vill. | . | . | + | . | . | 1 |
Thalictrum minus L. | . | . | + | . | . | 1 |
Characteristic and differential species : Koeleria macrantha, Rumex acetosella.
High frequency Taxa : Artemisia campestris, Carex caryophyllea, Euphorbia cyparissias, Koeleria macrantha, Lotus corniculatus, Peucedanum oreoselinum, Plantago lanceolata, Ranunculus bulbosus, Rumex acetosella, Thymus pulegioides.
Species composition : This community was dominated by Koeleria macrantha (Φ 0.88; p-value<0.001) and Peucedanum oreoselinum (Φ 0.45; p-value=0.07), accompanied by less demanding xerothermophytes, e.g. Hieracium pilosella, Galium verum, Thymus pulegioides, Carex caryophyllea, Potentilla neumanniana and Helianthemum nummularium. Among the other species, Rumex acetosella (Φ 0.40; p-value=0.02) and Euphorbia cyparissias (Φ 0.90; p-value<0.001) showed significant values for the ISA. Pioneer grassland on sand species, like Jasione montana, Trifolium arvense or Aira caryophyllea, and mesic meadows species, like Achillea millefolium aggr, Plantago lanceolata were present. The clustering split the community into two groups. One relevé (number 71) had a higher cover of Festuca trachyphylla, Aira caryophyllea, Hypochaeris radicata and typical dry grassland on sandy soil species. The others (42, 8, 7, 66) were in different secondary transitional stages dominated by semi-dry grassland species, like Bromus erectus, Lotus corniculatus, Trifolium montanum and the presence of the protected species Orchis ustulata and Orchis morio. The number of species per relevé ranged between 21 and 25, with an average of 21.8.
Geographic distribution
: These grasslands were found along the Maggia and the Melezza river. This community can be found in the entire Insubria region from Torino to Brescia (
Synecology
: The pH ranged between 4.5 and 5.0. The mean weighted Landolt indicator values were as follows: temperature (T) 3.58, continentality (K) 3.13, light (L) 3.85, moisture (F) 1.68, soil reaction (R) 2.90 and nutrients (N) 2.13, Humus (H) 2.89 (Fig.
Boxplots showing the variability of altitude and other environmental indicators (i.e. Landolt's moisture, light, temperature, continentality, soil reaction, nutrients, humus) for each plant community. The abbreviations used are referred to the following plant association: Phy-Fes for Phyteumo-Festucetum, Car-Nar for Carici-Nardetum, Cen-Arr for Centaureo-Arrhenatheretum, Hol-Chr for Holco-Chrysopogonetum, Poo-Fes for Poo-Festucetum and Phy-Mes for Phyteumo-Mesobrometum.
Syntaxonomical discussion
: This plant community is included to the Stipo-Poion xerophilae alliance by the occurrence of Achillea collina, Festuca trachyphylla and Carex liparocarpos. This plant community was initially described in Insubria by
The species in Plot 71 of the inventory of dry grasslands are very similar to Poo-bulbosae-Festucetum trachyphyllae. However, the data does not specify which species of Festuca ovina aggr. is present. Festuca trachyphylla could only be confirmed in our own relevé 42. Relevés 8, 7, and 66 have a much higher proportion of mesophilic species, which could potentially represent a degradational stage due to pasture and are considered as a mesophilic variant without Festuca trachyphylla.
Holco-Chrysopogonetum grylli Lagnaz, Trotta, Prunier, Krüsi et Boscutti 2023 ex
Holco-Chrysopogonetum grylli Lagnaz, Trotta, Prunier, Krüsi et Boscutti ex
Relevé number | 54 | 65 | 13 | 6 | 14 | Presence |
Altitude (m a.s.l) | 820 | 445 | 373 | 478 | 507 | |
Aspect | S | S | S | SO | S | |
Slope (degree) | 40 | 25 | 30 | 30 | 20 | |
Relevé area (m2) | 25 | 25 | 25 | 25 | 25 | |
Species number | 28 | 28 | 35 | 30 | 30 | |
Total coverage (%) | 90 | 90 | 100 | 100 | 100 | |
Characteristic and differential species of Holco-Chrysopogonetum grylli | ||||||
Danthonia decumbens (L.) DC. | 1 | 2 | 1 | 2 | 1 | 5 |
Brachypodium rupestre (Host) Roem. & Schult. | + | 1 | 1 | 2 | 1 | 5 |
Chrysopogon gryllus (L.) Trin. | . | 2 | 1 | 2 | 3 | 4 |
Bromion erecti and Brachypodietalia pinnati | ||||||
Thymus pulegioides L. | + | 1 | 1 | 2 | 2 | 5 |
Carex caryophyllea Latourr. | 1 | 1 | . | 1 | 1 | 4 |
Silene nutans L. | r | + | r | . | + | 4 |
Lotus corniculatus L. | . | + | 1 | 1 | 1 | 4 |
Bromus erectus Huds. | . | 1 | 1 | . | 3 | 3 |
Helianthemum nummularium (L.) Mill. | + | . | + | . | 1 | 3 |
Polygala vulgaris L. s.l. | . | + | + | . | 1 | 3 |
Luzula campestris (L.) DC. | . | . | . | 1 | 1 | 2 |
Ranunculus bulbosus L. | . | + | . | + | . | 2 |
Characteristic species of Festuco-Brometea | ||||||
Anthericum liliago L. | + | r | + | . | + | 4 |
Briza media L. | + | + | . | + | . | 3 |
Characteristic species Molinio-Arrhenatheretea and subordinate units | ||||||
Anthoxanthum odoratum L. | 1 | + | 3 | 3 | 1 | 5 |
Agrostis capillaris L. | . | 1 | 1 | . | + | 3 |
Festuca nigrescens Lam. | . | . | + | 1 | + | 3 |
Holcus lanatus L. | . | . | 2 | 1 | + | 3 |
Ajuga reptans L. | . | . | + | 1 | . | 2 |
Prunella vulgaris L. | . | . | + | + | . | 2 |
Centaurea transalpina DC. | . | + | + | . | . | 2 |
Plantago lanceolata L. | . | . | . | + | 1 | 2 |
Rumex acetosa L. | . | . | . | + | 1 | 2 |
Trifolium pratense L. | . | . | . | + | r | 2 |
Characteristic species of Nardetea strictae and subordinate units | ||||||
Stachys officinalis (L.) Trevis. | . | + | + | 1 | + | 4 |
Carex pilulifera L. | . | 1 | 2 | 1 | . | 3 |
Carex pallescens L. | . | 1 | + | . | . | 2 |
Other species | ||||||
Festuca filiformis Pourr. | 2 | 1 | 2 | 2 | 2 | 5 |
Potentilla erecta (L.) Raeusch. | 1 | 1 | 1 | 1 | . | 4 |
Cruciata glabra (L.) Ehrend. | . | . | + | 1 | + | 3 |
Hypochaeris radicata L. | + | + | . | + | . | 3 |
Molinia arundinacea Schrank | 3 | 1 | . | . | . | 2 |
Carex fritschii Waisb. | 2 | . | 1 | . | . | 2 |
Thalictrum minus L. | + | + | . | . | . | 2 |
Clinopodium vulgare L. | . | . | + | . | + | 2 |
Peucedanum oreoselinum (L.) Moench | + | + | . | . | . | 2 |
Veronica officinalis L. | . | . | 1 | . | + | 2 |
Pteridium aquilinum (L.) Kuhn | . | . | r | . | + | 2 |
Solidago virgaurea L. | + | . | . | + | . | 2 |
Vincetoxicum hirundinaria Medik. | r | . | . | . | + | 2 |
Lathyrus linifolius (Reichard) Bässler | + | . | + | . | . | 2 |
Lectotypus
: Tab.
According to the International Code of Phytosociology (
Characteristic and differential species : Brachypodium rupestre, Chrysopogon gryllus, Danthonia decumbens
High frequency Taxa : Achillea millefolium aggr., Anthericum liliago, Anthoxantum odoratum, Brachypodium rupestre, Carex caryophyllea, Carex pilulifera, Festuca filiformis, Lotus corniculatus, Silene nutans, Thymus pulegoides.
Species composition : This community was characterised by the dominance of Chrysopogon gryllus (Φ 0.3; p-value<0.05) and Anthoxantum odoratum. One relevé showed dominance of Chrysopogon gryllus combined with Bromus erectus. Other species with a significant fidelity according to ISA analysis were Danthonia decumbens (Φ 0.74; p-value<0.001) and Brachypodium rupestre (Φ 0.37; p-value<0.05). The protected species, Serapias vomeracea, was found in one relevé. Mesophilous meadow species, like Plantago lanceolata, Centaurea transalpina and Rumex acetosa were combined with typical semi-dry meadow species, such Bromus erectus, Carex caryophyllea, and Silene nutans. The latter had a higher frequency. The number of species per relevé ranged between 28 and 35, with an average of 30.2. One relevé (54) was an outlier with a dominance of Molinia arundinacea and other fringe vegetation species.
Geographic distribution : These grasslands are present in the Terre di Pedemonte and the outer part of Centovalli.
Synecology
: They are present on exposed southern slopes (max. 30 degrees) in the hill belt of the Terre di Pedemonte and the outer area of Centovalli. In the Terre die Pedemonte, the altitude for this plant community ranged between 373 m a.s.l. and 507 m a.s.l. One relevé was located in Centovalli at 820 m a.s.l. and the pH was near 4.5. The Landolt indicator values were as follows: temperature (T) 3.41, continentality (K) 2.82, light (L) 3.55, moisture (F) 2.37, soil reaction (R) 2.66 and nutrients (N) 2.34 (Fig.
Syntaxonomical discussion
: The association belongs to the alliance Bromion erecti by the occurrence of the characteristics species Thymus pulegoides, Silene nutans, Luzula campestris, Ranunculus bulbosus. In Switzerland, plant communities with Chrysopogon gryllus are limited to the Canton of Ticino. Chrysopogon gryllus has a wide amplitude and can be found also in different xerophytic communities in the central Alps extending to the Balkans, where its sociologic optimum occurs in the associations of the East continental order Festucetalia valesiacae (Ilijanić & Topić, 1989; Redzic, 1999). Chrysopogon gryllus grasslands in Ticino were first described by
Phyteumo-Mesobrometum
Relevé number | 22 | 50 | 49 | 52 | 11 | 53 | 16 | 17 | 33 | 37 | 57 | 19 | 59 | Presence |
Altitude m a.s.l. | 811 | 1013 | 1069 | 911 | 403 | 849 | 555 | 560 | 334 | 603 | 782 | 840 | 1274 | |
Aspect | SE | S | S | SE | S | E | SE | SE | SE | E | SE | SO | SE | |
Slope (degree) | 30 | 10 | 50 | 30 | 30 | 30 | 20 | 30 | 20 | 20 | 45 | 45 | 30 | |
Relevé area (m2) | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | |
Species number | 38 | 41 | 29 | 38 | 20 | 31 | 35 | 17 | 24 | 39 | 35 | 33 | 31 | |
Total coverage (%) | 100 | 90 | 95 | 95 | 100 | 100 | 100 | 90 | 100 | 100 | 100 | 100 | 100 | |
Characteristic and differential species of Phyteumo-Mesobrometum | ||||||||||||||
Thymus pulegioides L. | 2 | 2 | 1 | 1 | + | 1 | 2 | 2 | 1 | 1 | 3 | 2 | 1 | 13 |
Thalictrum minus L. | 1 | + | 1 | + | . | + | 1 | 1 | 1 | + | 1 | r | 1 | 12 |
Carex fritschii Waisb. | . | . | 2 | 2 | 3 | 3 | 3 | 2 | 3 | 3 | 2 | 3 | 3 | 11 |
Characteristic species of Bromion erecti and Brachypodietalia pinnati | ||||||||||||||
Luzula campestris (L.) DC. | 1 | 2 | + | 1 | 1 | . | 2 | 2 | 2 | 2 | . | 1 | 1 | 11 |
Silene nutans L. | . | + | . | + | . | + | r | + | + | 1 | 1 | + | 1 | 10 |
Ranunculus bulbosus L. | 2 | + | . | + | 2 | + | + | . | . | 1 | 1 | + | . | 9 |
Carex caryophyllea Latourr. | 2 | + | 1 | 1 | . | 1 | 2 | 1 | . | . | . | . | . | 7 |
Lotus corniculatus L. | . | + | . | + | . | . | + | . | . | + | + | 1 | + | 7 |
Helianthemum nummularium (L.) Mill. | 2 | 2 | . | 1 | . | . | . | . | . | 1 | 2 | 2 | 2 | 7 |
Bromus erectus Huds. | . | . | . | 1 | . | . | + | + | . | 2 | 2 | . | . | 5 |
Helictotrichon pubescens (Huds.) Pilg. | . | . | + | . | . | + | . | . | . | . | + | . | . | 3 |
Poa angustifolia L. | . | . | 1 | . | 2 | . | + | . | . | . | . | . | . | 3 |
Characteristic species of Festuco-Brometea and subordinate units | ||||||||||||||
Achillea collina (Becker ex Wirtg.) Heimerl | 1 | + | r | + | 1 | + | 1 | . | . | + | 1 | 1 | + | 11 |
Brachypodium rupestre (Host) Roem. & Schult. | + | 2 | 3 | 2 | . | . | + | . | 1 | 1 | 1 | + | 1 | 10 |
Briza media L. | + | + | . | + | . | . | . | + | . | + | . | 1 | 2 | 7 |
Salvia pratensis L. | . | 1 | . | . | r | . | 1 | + | r | + | + | . | . | 7 |
Dianthus carthusianorum L. s.l. | 2 | . | . | 1 | . | . | . | 1 | . | . | + | r | + | 6 |
Festuca ovina aggr. | . | + | 1 | 1 | . | + | . | . | . | . | . | . | + | 5 |
Anthericum liliago L. | . | . | r | + | . | . | . | . | . | . | 1 | . | . | 3 |
Hieracium piloselloides Vill. | r | . | . | + | . | . | . | . | . | + | . | . | . | 3 |
Characteristic species of Molinio-Arrhenatheretea and subordinate units | ||||||||||||||
Anthoxanthum odoratum L. | + | 1 | . | . | . | 1 | 2 | 1 | 2 | 3 | 1 | 2 | 2 | 10 |
Festuca nigrescens Lam. | 2 | 2 | 1 | 3 | 1 | . | 1 | . | 2 | 2 | + | . | 1 | 10 |
Leontodon hispidus L. | + | + | . | . | . | 1 | + | . | 1 | + | 1 | r | 1 | 9 |
Viola tricolor L. | 1 | . | . | + | + | 2 | + | 1 | . | + | + | . | + | 9 |
Arrhenatherum elatius (L.) J. & C. Presl | r | 1 | + | . | 2 | + | . | . | + | 1 | . | 1 | . | 8 |
Plantago lanceolata L. | 1 | + | . | . | . | . | + | r | . | + | + | + | 1 | 8 |
Cerastium fontanum subsp. vulgare (Hartm.) Greuter & Burdet | 1 | . | . | . | r | + | . | . | + | . | + | + | + | 7 |
Rumex acetosa L. | 1 | . | . | . | . | 1 | 1 | + | . | + | + | 1 | . | 7 |
Agrostis capillaris L. | . | + | . | . | + | 1 | . | . | . | + | 1 | . | 1 | 6 |
Holcus lanatus L. | . | 1 | . | . | . | . | + | . | 1 | + | + | 1 | . | 6 |
Dactylis glomerata L. | . | + | + | . | . | . | . | . | . | r | + | . | + | 5 |
Trifolium pratense L. | + | . | . | . | r | . | . | . | . | r | + | 1 | . | 5 |
Trisetum flavescens (L.) P. Beauv. | + | + | . | . | . | + | . | . | . | . | . | 2 | + | 5 |
Lathyrus pratensis L. | . | + | r | . | . | . | . | . | . | . | + | + | . | 4 |
Silene vulgaris (Moench) Garcke | . | + | . | . | . | . | . | r | . | + | . | . | + | 4 |
Veronica chamaedrys L. | + | + | . | . | . | . | . | . | + | + | . | . | . | 4 |
Trifolium repens L. | + | 1 | + | . | . | . | . | . | . | . | . | . | . | 3 |
Leucanthemum vulgare aggr. | . | . | . | . | . | + | . | . | 1 | + | . | . | . | 3 |
Other species | ||||||||||||||
Phyteuma betonicifolium Vill. | . | 1 | + | + | . | + | + | . | . | 1 | + | + | . | 8 |
Clinopodium vulgare L. | . | . | + | + | r | . | 1 | . | . | . | . | + | 1 | 6 |
Festuca filiformis Pourr. | 2 | . | . | . | . | 2 | 1 | 2 | . | . | 1 | 1 | . | 6 |
Galium rubrum L. | . | 1 | + | . | . | . | + | . | . | . | + | 1 | + | 6 |
Peucedanum oreoselinum (L.) Moench | r | . | . | + | . | . | . | . | 1 | 1 | . | r | . | 5 |
Rumex acetosella L. s.l. | . | + | r | . | + | + | . | . | 1 | . | . | . | . | 5 |
Cruciata glabra (L.) Ehrend. | 1 | . | . | . | . | . | 1 | . | 2 | 1 | . | . | . | 4 |
Vincetoxicum hirundinaria Medik. | . | . | 2 | + | . | . | . | . | . | . | . | r | 1 | 4 |
Avenella flexuosa (L.) Drejer | r | + | . | . | . | 1 | . | . | . | . | . | . | . | 3 |
Carex pairae F. W. Schultz | + | + | 1 | . | . | . | . | . | . | . | . | . | . | 3 |
Chrysopogon gryllus (L.) Trin. | . | . | . | 1 | . | . | 1 | 2 | . | . | . | . | . | 3 |
Hypericum perforatum L. | . | + | . | + | . | + | . | . | . | . | . | . | . | 3 |
Nardus stricta L. | . | + | . | + | . | + | . | . | . | . | . | . | . | 3 |
Poa variegata Lam. | . | + | . | + | . | 1 | . | . | . | . | . | . | . | 3 |
Potentilla erecta (L.) Raeusch. | . | . | . | + | . | + | . | . | . | . | + | . | . | 3 |
Scabiosa lucida Vill. | . | + | . | . | . | + | . | . | . | . | . | . | + | 3 |
Silene viscaria (L.) Borkh. | 1 | . | . | . | . | r | . | . | . | r | . | . | . | 3 |
Vicia sativa subsp. nigra (L.) Ehrh. | + | . | . | . | . | . | + | . | . | . | . | + | . | 3 |
Characteristic and differential species : Carex fritschii (Φ 0.50; p-value<0.001), Thymus pulegoides (Φ 0.22; p-value<0.1), Thalictrum minus (Φ 0.30; p-value<0.05)
High frequency Taxa : Luzula campestris, Achillea millefolium aggr., Brachypodium rupestre, Silene nutans, Anthoxantum odoratum, Festuca nigrescens, Ranunculus bulbosus.
Species composition : All the diagnostic species showed a significant fidelity to this association (Carex fritschii, Φ 0.50, p-value<0.001; Thymus pulegoides, Φ 0.22, p-value<0.1; Thalictrum minus, Φ 0.30, p-value<0.05). Two variants could be distinguished: one variant (plots 22, 49, 50, 52) was drier than the second one (plots 11, 16, 17, 19, 33, 37, 53, 57, 59). The first one comprised three meadows of national importance. They contained Festuca ovina aggr. and a more abundant cover of species typical of dry grasslands, like Helianthemum nummularium, Dianthus carthusianorum and Carex caryophyllea and a presence of very dry indicators, like Sedum annuum and Sedum telephium. These plots were also characterized by the presence or dominance of species indicating short-term abandonment, like Carex pairae, Vincetoxicum hirundinaria or dominance of Brachypodium rupestre. The second variant was characterized by the presence of Carex fritschii with a cover abundance between 2 and 3 in all surveys. Anthoxantum odoratum was dominant and species typical of semi-dry meadows were also present, like Centaurea scabiosa, Arabis hirsuta, Galium verum and Pimpinella saxifraga. Species typically from Arrhenatheretelia like Centaurea transalpina, Galium album, Poa pratensis were present in the second variant and absent in the first one. Bromus erectus was present but never dominant. The protected species, Lilium bulbiferum and Orchis ustulata, were also found. The number of species per relevé ranged between 17 and 41, with an average of 31.6.
Geographic distribution : These grasslands had a wide amplitude and were spread throughout the study area.
Synecology
: These grasslands were found on exposed southern and eastern slopes (from 10 to 45 degrees in gradient). The altitudes ranged from 334 m a.s.l. to 1274 m a.s.l. The pH ranged between 4.0 and 4.5. The Landolt indicator values were as followed: temperature (T) 3.35, continentality (K) 2.98, light (L) 3.56, moisture (F) 2.31, soil reaction (R) 2.85 and nutrients (N) 2.42, Humus (H) 3.18 (Fig.
Syntaxonomical discussion
: The association belongs to the alliance Bromion erecti by the occurrence of the characteristics species Ranunculus bulbosus, Luzula campestris, Silene nutans. Semi-dry grasslands on silicious soils in Ticino were described by
Centaureo transalpinae-Arrhenatheretum Oberd. 1964 nom. mut. prop.
Centaureo transalpinae-Arrhenatheretum Oberd. 1964 nom. mut. prop.
Relevé number | 29 | 30 | 24 | 35 | 34 | 36 | 15 | 21 | 25 | 48 | 10 | 20 | 9 | 23 | 12 | 51 | 2 | 3 | 47 | 58 | Presence |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Altitude m a.s.l. | 711 | 701 | 700 | 308 | 339 | 360 | 550 | 676 | 666 | 780 | 222 | 823 | 335 | 701 | 367 | 855 | 1160 | 1174 | 1057 | 1180 | |
Aspect | N | N | SE | SE | SE | E | O | S | N | SO | E | SO | NE | SE | NO | SE | E | E | SE | SE | |
Slope (degree) | 10 | 20 | 10 | 0 | 0 | 10 | 20 | 30 | 10 | 20 | 0 | 30 | 0 | 40 | 10 | 0 | 35 | 30 | 45 | 30 | |
Relevé area (m2) | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | |
Species number | 26 | 25 | 19 | 24 | 11 | 25 | 19 | 27 | 25 | 25 | 23 | 21 | 20 | 25 | 22 | 25 | 25 | 23 | 30 | 35 | |
Total coverage (%) | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 90 | 100 | 100 | 100 | 100 | 95 | 100 | 100 | 100 | 100 | 100 | |
Characteristic and differential species of Centaureo-Arrhenatheretum | |||||||||||||||||||||
Centaurea transalpina (Schleich. ex DC.) Nyman | 2 | . | 1 | 2 | + | 1 | 1 | + | 2 | + | + | . | . | + | r | . | . | + | . | + | 14 |
Characteristic species of Arrhenatherion elatioris and Arrhenatheretalia elatioris | |||||||||||||||||||||
Arrhenatherum elatius (L.) J. & C. Presl | + | 2 | . | + | + | 1 | . | 3 | + | 3 | 2 | 2 | 3 | 3 | 1 | 1 | 2 | 2 | 1 | 1 | 18 |
Silene vulgaris (Moench) Garcke | . | + | + | 1 | 1 | 1 | . | . | 1 | + | 2 | . | 1 | r | 1 | + | 1 | + | 1 | 1 | 16 |
Rumex acetosa L. | + | + | . | 1 | . | 1 | 1 | 1 | 2 | + | . | . | . | 1 | + | + | 1 | . | + | + | 14 |
Trisetum flavescens (L.) P. Beauv. | 1 | + | 1 | . | . | . | . | 2 | 2 | 1 | 1 | 2 | . | 1 | . | + | + | 2 | 1 | + | 14 |
Cerastium fontanum subsp. vulgare (Hartm.) Greuter & Burdet | . | . | + | 1 | . | + | 1 | . | 1 | . | 2 | 1 | . | . | . | + | 1 | 1 | + | + | 12 |
Holcus lanatus L. | . | . | 2 | 2 | . | . | 1 | 2 | . | + | . | 1 | . | 1 | . | . | . | + | 1 | + | 10 |
Galium album Mill. | 1 | 1 | 1 | . | . | . | . | 1 | + | . | . | . | + | + | . | + | . | . | + | . | 9 |
Leucanthemum vulgare aggr. | r | . | . | 2 | . | . | . | 1 | 1 | 1 | . | . | . | . | . | . | 1 | + | . | + | 8 |
Viola tricolor L. | . | . | . | 1 | . | + | . | . | . | . | + | . | 1 | . | . | + | 2 | . | 1 | 1 | 8 |
Poa pratensis L. | . | . | . | 1 | 2 | 2 | . | . | . | . | . | . | . | . | + | + | . | . | . | + | 6 |
Lolium perenne L. | . | . | . | 1 | 1 | + | + | . | . | . | . | . | . | . | . | . | + | . | . | + | 6 |
Erigeron annuus (L.) Desf. s.l. | . | . | . | . | . | . | . | r | . | r | . | . | r | + | . | . | . | . | . | . | 4 |
Characteristic species of Molinio-Arrhenatheretea and subordinate units | |||||||||||||||||||||
Achillea millefolium aggr. | 1 | 1 | 1 | 2 | 2 | 2 | 2 | 2 | 1 | + | 1 | 1 | + | 1 | + | + | + | 1 | + | 1 | 20 |
Dactylis glomerata L. | + | r | 2 | + | + | 1 | + | 1 | r | + | 2 | + | 2 | 2 | + | . | 1 | 2 | 1 | + | 19 |
Plantago lanceolata L. | 1 | + | 2 | 2 | 2 | + | 1 | 1 | + | + | 1 | + | 2 | 1 | 1 | 2 | 2 | . | + | 1 | 19 |
Festuca nigrescens Lam. | + | 1 | 2 | . | . | 1 | 2 | 2 | 2 | 1 | 2 | 2 | 1 | 2 | 2 | 2 | 1 | 2 | 1 | 2 | 18 |
Anthoxanthum odoratum L. | 1 | 1 | . | 2 | 4 | 2 | 3 | 2 | 2 | 1 | 2 | . | 2 | 1 | 2 | 2 | 1 | 2 | 2 | 2 | 18 |
Trifolium pratense L. | 1 | 1 | 2 | 1 | . | + | 2 | 2 | 2 | 1 | . | 1 | 1 | 2 | r | + | + | 1 | 1 | + | 18 |
Leontodon hispidus L. | 2 | 2 | + | 2 | 2 | 1 | + | 1 | 2 | + | . | r | 1 | . | . | + | . | . | + | 1 | 15 |
Ranunculus acris L. | + | . | . | + | 1 | 1 | . | 1 | . | . | . | . | . | . | + | + | + | 1 | + | + | 11 |
Trifolium repens L. | . | 1 | 1 | 1 | . | + | + | 2 | 1 | + | . | . | . | . | . | + | . | 1 | . | + | 11 |
Agrostis capillaris L. | 1 | 2 | . | 1 | . | . | . | 1 | 3 | . | + | . | . | . | + | . | . | . | 1 | 1 | 9 |
Chaerophyllum villarsii W. D. J. Koch | 3 | . | . | . | . | . | . | . | . | + | . | . | . | . | . | . | 2 | 2 | + | 1 | 6 |
Lathyrus pratensis L. | . | . | . | . | . | . | . | 1 | . | + | . | + | . | 1 | + | + | . | . | . | . | 6 |
Prunella vulgaris L. | . | . | . | . | . | . | . | + | 1 | . | . | . | . | + | . | . | + | + | . | . | 5 |
Ranunculus friesianus Jord. | . | 1 | 2 | . | . | . | + | . | 1 | . | . | + | . | . | . | . | . | . | . | . | 5 |
Pimpinella major (L.) Huds. | . | r | . | . | . | . | r | . | . | + | . | . | . | . | r | . | . | . | . | . | 4 |
Characteristic species of Festuco-Brometea and subordinate units | |||||||||||||||||||||
Luzula campestris (L.) DC. | . | 1 | . | 1 | . | . | + | . | 1 | . | . | 1 | 1 | 1 | 2 | 1 | 1 | 1 | 1 | 1 | 13 |
Thymus pulegioides L. | + | 1 | . | . | . | . | . | . | + | + | . | 1 | + | 2 | 1 | 2 | 2 | + | 2 | 1 | 13 |
Veronica chamaedrys L. | . | . | . | . | . | + | 2 | 1 | 1 | . | . | + | + | + | 1 | + | + | . | + | . | 11 |
Lotus corniculatus L. s.l. | 2 | . | + | . | . | . | . | + | . | + | + | . | . | . | . | . | . | 1 | + | 1 | 8 |
Ranunculus bulbosus L. | . | 1 | . | . | . | . | . | . | . | 1 | + | 1 | . | . | 1 | 1 | . | . | r | 1 | 8 |
Poa angustifolia L. | . | . | 1 | 1 | . | + | . | . | . | . | + | . | + | . | . | . | . | . | . | . | 5 |
Briza media L. | 2 | . | . | . | . | . | . | . | . | . | . | . | . | . | . | . | 1 | . | 1 | 2 | 4 |
Carex caryophyllea Latourr. | . | . | . | . | . | . | . | . | . | . | . | . | + | . | . | 2 | . | . | 1 | + | 4 |
Helictotrichon pubescens (Huds.) Pilg. | . | . | . | . | . | . | . | . | . | . | . | . | . | . | . | 2 | 2 | 1 | . | + | 4 |
Salvia pratensis L. | . | . | . | . | . | r | . | . | . | + | 1 | . | . | r | . | . | . | . | . | . | 4 |
Other species | |||||||||||||||||||||
Phyteuma betonicifolium Vill. | + | 1 | . | . | . | . | . | + | . | . | . | + | . | 1 | + | + | 2 | 2 | 2 | + | 11 |
Thalictrum minus L. | 3 | 1 | . | 1 | . | 1 | 1 | 2 | . | . | + | 1 | . | 1 | . | . | 1 | . | 2 | . | 11 |
Carex pairae F. W. Schultz | . | . | + | + | . | r | . | + | . | . | + | + | 1 | 1 | . | . | . | . | . | + | 9 |
Potentilla erecta (L.) Raeusch. | . | 1 | + | . | . | . | + | . | 1 | . | . | . | . | r | + | . | 2 | 1 | . | . | 8 |
Carex fritschii Waisb. | 1 | . | 1 | . | . | + | . | 1 | . | . | + | 3 | . | . | + | . | . | . | . | . | 7 |
Rumex acetosella L. s.l. | . | . | . | + | . | . | . | . | . | . | 1 | 1 | 1 | 1 | . | 1 | . | . | . | + | 7 |
Peucedanum oreoselinum (L.) Moench | 2 | 2 | . | . | . | r | . | + | . | + | 1 | . | . | . | . | . | . | . | . | . | 6 |
Carex pallescens L. | 1 | 1 | . | . | . | . | . | . | . | . | . | . | . | . | . | . | . | + | + | + | 5 |
Clinopodium vulgare L. | + | . | . | . | . | . | . | . | . | + | 1 | . | . | . | . | . | . | . | + | 2 | 5 |
Myosotis arvensis Hill | . | . | . | . | . | + | . | . | 1 | . | + | . | + | . | . | . | . | . | . | + | 5 |
Stellaria graminea L. | r | 2 | . | . | . | . | . | . | + | . | . | . | . | . | . | . | . | . | + | . | 4 |
Original name
: Centaurea dubiae-Arrhenatheretum elatioris
Synonyms
: Centaureo carniolicae-Arrhenatheretum elatioris
Lectotypus
: Tab. 9, relevé 4 in
Characteristic and differential species : Centaurea transalpina.
High frequency Taxa : Achillea millefolium aggr., Arrhenatherum elatius, Silene vulgaris, Festuca nigrescens, Dactylis glomerata, Plantago lanceolata, Anthoxantum odoratum, Trifolium pratense, Leontodon hispidus.
Species composition : These grass-rich meadows were generally dominated by Arrhenatherum elatius (Φ 0.45; p-value=0.06) and Anthoxanthum odoratum. Centaurea transalpina was the only other species whit a significant ISA value (Φ 0.58; p-value<0.01). Trisetum flavescens was present in all plots above 650 m a.s.l. but was never dominant. One meadow (relevé 29) showed signs of extensive management, with a dominance of Chaerophyllum villarsii and Thalictrum minus. All plots were characterized by nutrient rich grassland species, like Dactylis glomerata, Trifolium repens, Ranunculus friesianus. Agrostis capillaris and Viola tricolor indicated soil acidity. The presence of species from the Southern part of the Alps was typical for this association, particularly Centaurea transalpina and Achillea roseo-alba (which was aggregated into Achillea millefolium in the present work). Two variants could be distinguished: the first one contained meadows (relevés 15, 21, 24, 25, 34, 35, 36) that were more intensively managed on flat areas or gentle slopes (10-20 degrees) and was found below 700 m. The number of species was lower (average 24.7) than the second variant (relevés 2, 3, 9, 10, 12, 20, 23, 47, 48, 51, 58). The second variant had an average of 31.9 species. These were present on slopes up to 45 degrees. Some of them were found on formerly cultivated terraces. In one meadow, we found the locally protected species, Lilium bulbiferum subsp. croceum. These grasslands were generally found above 700 m. They had a high frequency and cover of montane species like Chaerophyllum villarsii and Phyteuma orbiculare. They could be considered as a transitional stage to Centaureo transalpinae-Trisetetum flavescentis. The number of species per relevé ranged between 11 for the most intensively managed meadow to 35, with an average of 23.8.
Geographic distribution
: This association is found South of the Alps in Ticino and Northern East Italy, from Comasco to Friuli (Poldini & Oriolo 1994;
Synecology
: The pH ranged between 4.5 and 5.0. This association had a wide amplitude. It was found across the whole study area in the hill and the lower montane zones at altitudes between 222 m a.s.l. and 1180 m a.s.l. The Landolt indicator values were as follows: temperature (T) 3.20, continentality (K) 3.02, light (L) 3.45, moisture (F) 2.66, soil reaction (R) 2.88 and nutrients (N) 2.92, Humus (H) 3.20 (Fig.
Syntaxonomical discussion
: The association belongs to the alliance Arrhenatherion elatioris by the occurrence of the characteristic species Arrhenatherum elatius, Silene vulgaris, Rumex acetosa, Galium album, Viola tricolor, and Poa pratensis.
Phyteumo betonicifolii-Festucetum nigrescentis ass. nova (Tab.
Relevé number | 27 | 28 | 39 | 41 | 5 | 18 | 68 | 64 | 46 | 43 | 44 | 60 | 61 | Presence |
Altitude m a.s.l. | 1050 | 899 | 978 | 927 | 924 | 747 | 1465 | 1342 | 1115 | 1261 | 1100 | 1406 | 1384 | |
Aspect | NE | N | E | NO | E | NO | S | S | S | S | S | E | S | |
Slope (degree) | 45 | 20 | 20 | 20 | 15 | 30 | 25 | 40 | 10 | 20 | 45 | 30 | 40 | |
Relevé area (m2) | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | |
Species number | 22 | 22 | 25 | 29 | 44 | 36 | 19 | 37 | 24 | 33 | 34 | 31 | 40 | |
Total coverage (%) | 100 | 100 | 100 | 100 | 100 | 100 | 90 | 100 | 100 | 100 | 100 | 100 | 100 | |
Characteristic and differential Phyteumo betonicifolii-Festucetum nigrescentis | ||||||||||||||
Phyteuma betonicifolium Vill. | . | 1 | 2 | 1 | 2 | 1 | + | + | 1 | 1 | 1 | + | 1 | 12 |
Festuca nigrescens Lam. | 2 | 3 | 4 | 3 | 2 | 1 | . | . | 4 | 2 | 1 | 1 | 2 | 11 |
Poa chaixii Vill. | + | + | + | + | . | . | + | 1 | 2 | + | 1 | + | + | 11 |
Chaerophyllum villarsii W. D. J. Koch | . | . | . | 1 | . | + | . | 1 | . | 2 | 2 | 1 | 1 | 7 |
Ranunculus montanus aggr. | . | . | 1 | + | . | . | + | + | . | + | + | . | + | 7 |
Crocus albiflorus Kit. | . | . | . | 1 | + | + | . | + | + | . | . | . | + | 6 |
Phleum rhaeticum (Humphries) Rauschert | + | 1 | . | 1 | . | + | + | . | . | . | . | + | . | 6 |
Characteristic species of Nardo strictae-Agrostion and Nardetalia | ||||||||||||||
Carex pallescens L. | . | . | + | . | 2 | 1 | + | 1 | + | 1 | 1 | . | + | 9 |
Avenella flexuosa (L.) Drejer | 2 | 4 | . | . | . | 2 | 1 | . | . | . | . | . | 1 | 5 |
Paradisea liliastrum (L.) Bertol. | . | r | . | + | . | r | . | + | . | . | . | . | r | 5 |
Stellaria graminea L. | + | + | 1 | 1 | . | . | . | . | . | . | . | . | . | 4 |
Carex pilulifera L. | 2 | 2 | . | . | . | . | . | . | . | . | . | 2 | 1 | 4 |
Galium pumilum Murray | r | . | . | . | + | . | 1 | + | . | . | . | . | . | 4 |
Poa variegata Lam. | . | . | . | . | + | . | 2 | . | . | . | . | 2 | 1 | 4 |
Stachys officinalis (L.) Trevis. | r | . | . | . | 1 | . | . | + | . | . | . | . | . | 3 |
Viola canina s.l. | 1 | . | . | . | + | . | . | . | . | . | 1 | . | . | 3 |
Characteristic species of Nardetea strictae and subordinate units | ||||||||||||||
Nardus stricta L. | . | + | 1 | + | . | . | 2 | 1 | 1 | 1 | . | 1 | 1 | 9 |
Alchemilla hybrida aggr. sensu K. Lauber | r | . | . | . | . | . | . | . | . | + | 1 | 1 | 1 | 5 |
Characteristic species of Molinio-Arrhenatheretea and subordinate units | ||||||||||||||
Achillea millefolium aggr. | 1 | . | + | 1 | 2 | 1 | + | 1 | 1 | 1 | 1 | 1 | 1 | 12 |
Agrostis capillaris L. | 1 | + | 1 | + | 1 | 1 | 1 | 2 | + | . | + | 1 | 1 | 12 |
Veronica chamaedrys L. | 1 | . | + | + | + | . | . | + | + | + | 1 | . | + | 9 |
Silene vulgaris (Moench) Garcke | . | . | + | + | 1 | . | + | . | + | 1 | + | + | 1 | 9 |
Anthoxanthum odoratum L. | 1 | . | 1 | 3 | 2 | 2 | + | . | . | . | 1 | 1 | . | 8 |
Dactylis glomerata L. | . | . | r | . | + | . | . | r | + | 2 | 2 | + | + | 8 |
Trifolium pratense L. | . | . | . | r | 1 | 1 | . | + | . | + | + | + | + | 8 |
Viola tricolor L. | . | . | + | . | + | . | . | . | 1 | + | + | 1 | . | 6 |
Cerastium fontanum subsp. vulgare (Hartm.) Greuter & Burdet | . | . | . | . | + | . | . | . | + | + | + | . | + | 5 |
Rumex acetosa L. | . | . | + | . | 2 | . | . | . | + | . | + | . | + | 5 |
Trisetum flavescens (L.) P. Beauv. | . | + | + | . | . | . | + | . | . | . | + | . | 2 | 5 |
Leontodon hispidus L. | . | . | . | . | 1 | . | . | . | . | + | + | 2 | . | 4 |
Plantago lanceolata L. | . | . | . | . | . | . | . | . | . | + | + | + | . | 3 |
Trifolium repens L. | . | . | . | . | 1 | + | . | + | . | . | . | . | . | 3 |
Narcissus verbanensis (Herb.) M. Roem. | . | . | 2 | 1 | . | . | . | . | . | . | . | . | . | 2 |
Characteristic species of Festuco-Brometea and subordinate units | ||||||||||||||
Thymus pulegioides L. | 2 | 1 | + | + | 3 | + | + | 1 | + | . | 2 | 1 | 1 | 12 |
Luzula campestris (L.) DC. | + | 1 | + | 1 | 2 | 2 | . | 1 | . | . | . | + | 1 | 9 |
Briza media L. | . | . | . | . | + | . | . | + | 1 | + | 2 | 2 | 1 | 7 |
Carex caryophyllea Latourr. | . | . | . | . | 1 | . | . | 1 | 2 | 2 | 1 | 1 | 1 | 7 |
Brachypodium rupestre (Host) Roem. & Schult. | 3 | + | . | . | + | + | . | 2 | . | . | . | + | . | 6 |
Silene nutans L. | r | . | r | . | 2 | 1 | . | . | . | r | . | 1 | . | 6 |
Festuca ovina aggr. | . | r | . | . | . | . | 1 | 1 | . | + | + | r | . | 6 |
Lotus corniculatus L. s.l. | . | . | . | . | + | 1 | . | + | . | + | + | . | . | 5 |
Polygala vulgaris L. s.l. | r | . | . | . | 2 | . | + | + | . | . | . | . | . | 4 |
Ranunculus bulbosus L. | . | . | . | . | 1 | . | . | . | . | . | . | + | 1 | 3 |
Other species | ||||||||||||||
Rumex acetosella L. s.l. | . | r | + | + | + | + | . | + | + | 1 | + | + | + | 11 |
Potentilla erecta (L.) Raeusch. | 2 | 1 | 1 | 2 | 2 | + | + | 1 | . | . | . | . | . | 8 |
Festuca filiformis Pourr. | . | . | + | + | 1 | 1 | . | + | . | . | . | 1 | . | 6 |
Galium rubrum L. | . | . | . | . | . | . | . | + | 1 | + | + | + | 1 | 6 |
Vincetoxicum hirundinaria Medik. | . | . | . | r | . | . | + | + | r | r | 2 | . | . | 6 |
Thalictrum minus L. | . | . | . | + | . | 1 | . | + | + | . | + | . | 1 | 6 |
Veronica officinalis L. | + | + | . | . | 1 | 1 | . | . | . | + | . | . | . | 5 |
Hypericum perforatum L. | . | . | . | + | . | . | . | . | 1 | 1 | + | . | . | 4 |
Carex fritschii Waisb. | . | . | . | 2 | 1 | 1 | . | . | . | . | . | . | . | 3 |
Solidago virgaurea L. | . | . | . | . | 2 | + | . | + | . | . | . | . | . | 3 |
Arabis ciliata Clairv. | . | . | . | . | . | . | . | . | . | . | + | + | + | 3 |
Rosa spec. | . | . | . | . | . | . | . | r | . | . | . | + | r | 3 |
Characteristic and differential species : Festuca nigrescens, Phyteuma betonicifolium, Crocus albiflorus, Phleum rhaeticum, Poa chaixii, Ranunculus montanus, Chaerophyllum villarsii.
High frequency Taxa : Achillea millefolium aggr., Agrostis capillaris, Rumex acetosella, Thymus pulegoides.
Species composition : All diagnostic species showed a high fidelity to the association (Festuca nigrescens Φ 0.32, p-value<0.05; Phyteuma betonicifolium Φ 0.32, p-value<0.05; Crocus albiflorus, Φ 0.29, p-value<0.05; Phleum rhaeticum, Φ 0.40, p-value<0.05; Poa chaixii, Φ 0.4; p-value<0.05; Ranunculus montanus, Φ 0.49, p-value<0.05). These meadows were characterized by a mix of montane belt mesic meadow species (e.g. Chaerophyllum villarsii, Phleum rhaeticum), montane and subalpine belt mat-grass dry pasture species (Nardus stricta, Avenella flexuosa, Stellaria graminea), and meso-xerophytic grassland species (e.g. Thymus pulegoides, Silene nutans, Lotus corniculatus, Ranunculus bulbosus). In many relevés Festuca nigrescens was dominant. Two variants were distinguished. In the first one (5, 18, 27, 28, 39, 41) Festuca nigrescens was always present and was dominant in half of the relevés. Two protected species were found in the first variant: Lilium bulbiferum and Narcissus verbanensis. In the second variant (43, 44, 46, 60, 61, 64, 68) there was a higher frequency of species typical of Nardus stricta grasslands, like Nardus stricta, Carex pallescens, Alchemilla hybrida aggr., Galium rubrum, Poa chaixii. The number of species per relevé ranged between 19 and 44, with an average of 30.5.
Geographic distribution : The first variant included four relevés from the Centovalli, one from the lakeside and one from the Onsernone Valley. The second variant included four relevés from the Onsernone valley and three from the Vergeletto valley.
Synecology
: Grasslands belonging to the first variant were North facing and at altitudes ranging from 747 m a.s.l. to 1050 m a.s.l. The ones in the second variant were found in the upper mountain belt and were mostly South facing. The altitude ranged from 1100 to 1,465 m a.s.l. The pH ranged between 4.0 and 4.5. The Landolt indicator values were as follows: temperature (T) 2.92, continentality (K) 2.95, light (L) 3.36, moisture (F) 2.63, soil reaction (R) 2.59 and nutrients (N) 2.55, Humus (H) 3.31 (Fig.
Syntaxonomical discussion
: The association is included in the alliance Nardo strictae-Agrostion tenuis by the occurrence of the characteristic species Avenella flexuosa, Phyteuma betonicifolium, Carex pallescens, Poa variegata. In Ticino, Festuca rubra-Agrostis capillaris meadows have been described by different authors (
We could consider placing these grasslands in the Violion alliance (acidophilous nutrient poor grasslands), as our relevés have a lot of species in common with the Polygalo-Nardetum described in Friuli (Poldini & Oriolo, 1997). The fact that Nardus stricta should be dominant in this association (Poldini & Oriolo 1997;
Carici piluliferae-Nardetum strictae Marschall and Dietl 1974 (Tab.
Relevé number | 31 | 55 | 4 | 62 | 63 | 1 | 38 | 26 | 40 | 32 | 67 | 70 | 71 | Presence |
Altitude m a.s.l. | 1496 | 1013 | - | 1273 | 1243 | 1044 | 1012 | 1060 | 989 | 1498 | 1425 | 1101 | 1037 | |
Aspect | S | SO | - | S | SO | SE | SE | SE | NE | y | SO | N | S | |
Slope | 30 | 30 | - | 25 | 0 | 45 | 40 | 10 | 45 | 10 | 10 | 20 | 0 | |
Relevé area (m2) | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | |
Species number | 21 | 19 | 22 | 34 | 25 | 16 | 9 | 14 | 12 | 7 | 9 | 15 | 19 | |
Total coverage (%) | 100 | 95 | 100 | 95 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | |
Characteristic and differential species of Carici piluliferae-Nardetum | ||||||||||||||
Carex pilulifera L. | 1 | 1 | 3 | 1 | 1 | 5 | 5 | 1 | 2 | 2 | 1 | 2 | 1 | 13 |
Nardus stricta L. | . | 2 | 3 | 1 | 2 | 1 | 1 | 4 | 3 | 4 | 4 | 1 | 2 | 12 |
Characteristic species of Nardo strictae-Agrostion and Nardetalia | ||||||||||||||
Avenella flexuosa (L.) Drejer | 1 | . | . | . | . | . | + | + | 2 | 3 | 2 | 2 | 1 | 8 |
Phyteuma betonicifolium Vill. | + | 1 | + | + | + | + | . | . | . | . | . | + | + | 8 |
Festuca nigrescens Lam. | . | . | . | . | + | . | . | 1 | 2 | . | + | 1 | + | 6 |
Carex pallescens L. | . | + | . | . | + | . | . | + | . | . | + | . | . | 4 |
Poa variegata Lam. | 2 | 2 | . | . | . | . | . | . | . | . | . | . | . | 2 |
Danthonia decumbens (L.) DC. | r | . | . | . | . | . | . | . | . | . | . | . | . | 1 |
Cytisus scoparius (L.) Link /S | 2 | . | . | . | . | . | . | . | . | . | . | . | . | 1 |
Characteristic species of Nardetea strictae and subordinate units | ||||||||||||||
Luzula campestris (L.) DC. | . | . | . | . | . | . | . | r | + | . | . | 1 | . | 3 |
Characteristic species of Juncetea trifidii and subordinate units | ||||||||||||||
Festuca paniculata (L.) Schinz & Thell. | 4 | 3 | . | . | . | . | . | . | . | . | . | . | . | 2 |
Hieracium lactucella Wallr. | + | . | . | . | . | . | . | . | . | . | . | . | . | 1 |
Characteristic species of Festuco-Brometea and subordinate units | ||||||||||||||
Anthericum liliago L. | . | . | + | . | . | + | + | . | . | . | . | + | + | 5 |
Thymus pulegioides L. | . | 1 | 1 | 2 | 2 | . | . | . | . | . | . | . | + | 5 |
Carex caryophyllea Latourr. | 2 | . | . | 1 | 2 | . | . | . | . | . | . | 1 | . | 4 |
Festuca ovina aggr. | 1 | . | 2 | 2 | 2 | . | . | . | . | . | . | . | . | 4 |
Helianthemum nummularium (L.) Mill. | . | . | 1 | 2 | + | + | . | . | . | . | . | . | . | 4 |
Silene nutans L. | . | 1 | 1 | + | + | . | . | . | . | . | . | . | . | 4 |
Brachypodium rupestre (Host) Roem. & Schult. | . | . | . | 1 | 1 | 1 | . | . | . | . | . | . | . | 3 |
Briza media L. | . | . | 1 | + | . | + | . | . | . | . | . | . | . | 3 |
Lotus corniculatus L. s.l. | . | . | . | + | + | . | . | . | . | . | + | . | . | 3 |
Ranunculus bulbosus L. | . | . | . | 1 | . | + | . | . | . | . | . | 1 | . | 3 |
Veronica chamaedrys L. | . | + | . | . | . | . | . | . | . | . | . | . | . | 1 |
Characteristic species of Molinio-Arrhenatheretea and subordinate units | ||||||||||||||
Anthoxanthum odoratum L. | . | 1 | 1 | . | . | . | . | . | 1 | 1 | + | . | . | 5 |
Leontodon hispidus L. | + | . | + | + | + | . | . | . | . | . | . | . | 1 | 5 |
Rumex acetosa L. | . | + | . | . | . | 1 | . | + | + | . | . | . | + | 5 |
Poa chaixii Vill. | . | . | . | . | + | + | . | . | + | . | . | . | + | 4 |
Plantago lanceolata L. | . | . | + | + | + | . | . | . | . | . | . | . | . | 3 |
Silene vulgaris (Moench) Garcke | . | + | . | . | . | . | . | . | . | . | . | . | . | 1 |
Viola tricolor L. | . | 1 | . | . | . | . | . | . | . | . | . | . | . | 1 |
Holcus lanatus L. | . | + | . | . | . | . | . | . | . | . | . | . | . | 1 |
Rorippa stylosa (Pers.) Mansf. & Rothm. | + | . | . | . | . | . | . | . | . | . | . | . | . | 1 |
Other species | ||||||||||||||
Festuca filiformis Pourr. | 1 | 3 | 1 | 1 | 1 | + | 1 | 1 | . | . | . | 2 | 3 | 10 |
Potentilla erecta (L.) Raeusch. | + | + | . | . | . | . | + | + | 1 | r | . | + | + | 8 |
Veronica officinalis L. | . | + | . | + | . | + | . | + | . | . | . | . | + | 5 |
Calluna vulgaris (L.) Hull | 1 | . | . | . | . | . | . | . | . | . | . | . | . | 1 |
Galium rubrum L. | 1 | . | . | . | . | . | . | . | . | . | . | . | . | 1 |
Pteridium aquilinum (L.) Kuhn | 1 | . | . | . | . | . | . | . | . | . | . | . | . | 1 |
Vaccinium myrtillus L. | 1 | . | . | . | . | . | . | . | . | . | . | . | . | 1 |
Vaccinium vitis-idaea L. | r | . | . | . | . | . | . | . | . | . | . | . | . | 1 |
Rubus fruticosus aggr. sensu Landolt /S | + | . | . | . | . | . | . | . | . | . | . | . | . | 1 |
Synonyms
: Nardetum alpigenum ss-ass. à Carex pilulifera et Polygala serpyllifolia Berset 1969, Omalotheco sylvaticae-Nardetum strictae Gillet in
Characteristic and differential species : Carex pilulifera, Nardus stricta.
High frequency Taxa : Carex pilulifera, Nardus stricta.
Species composition : Avenella flexuosa, Carex pilulifera (Φ 0.55; p-value<0.1), Festuca filiformis, Nardus stricta (Φ 0.61; p-value<0.01) were the dominant species. Three variants could be distinguished: the first one (relevés 4, 62, 63) presented several semi-dry meadow species like Festuca ovina aggr., Helianthemum nummularium, Thymus pulegoides and Silene nutans. The second variant (relevés 1, 26, 32, 38, 40, 67, 70, 71) was very poor in species (mean 16), mostly dominated by Carex pilulifera or Nardus stricta (cover-abundance 4 or 5), the third characherized by dominance of Festuca paniculata (cover-abundance 3, resp. 4) and Festuca filiformis. The number of species per relevé ranged between 7 and 34, with an average of 17.1.
Geographic distribution : Carici piluliferae-Nardetum strictae was present throughout the whole studied area, except from the Vergeletto Valley. One relevé was from Pizzo Leone, five from the Onsernone Valley and five from Centovalli and two on the lakeside of Lago Maggiore.
Synecology
: These grasslands were mostly on exposed southern slopes at altitudes between 989 to 1,498 m a.s.l. The slopes varied from flat to 40 degrees. With a mean of 26 species, the first variant had significantly more species than the second variant and third variant. Two of them belong to the federal inventory of dry meadows and pastures of national importance. The Landolt indicator values were as follows: temperature (T) 2.95, continentality (K) 2.78, light (L) 3.37, moisture (F) 2.57, soil reaction (R) 2.26, nutrients (N) 2.38 and Humus (H) 3.33 (Fig.
Syntaxonomical discussion
: The association is included in the alliance Nardo strictae-Agrostion by the high frequency and abundance of Phyteuma betonicifolium, Festuca nigrescens, and Carex pallescens. The Nardus-rich grasslands in Ticino are well known.
This study has contributed to providing new phytosociological knowledge for a region that has been poorly studied. We found six associations distributed in four alliances and three classes (Tab.
A further consideration about dry grassland composition and conservation concerns the frequency and abundance of Brachypodium rupestre. This species resulted dominant in some stands across different investigated plant communities suggesting for its plausible encroachment behaviour, especially where a regular mowing or grazing is missing.
Since the number of surveys is low for some plant communities, future studies should also shed light on the attribution of grasslands with Festuca paniculata and confirm the presence of the Thymo-Festucetum association within the Nardo-Agrostion alliance.
Class (FB: Festuco-Brometea, MA: Molino-Arrhenatheretea, NS: Nardetea strictae) | FB | FB | FB | MA | NS | NS |
---|---|---|---|---|---|---|
Association | PoFe | HoCh | ThCa | CeAr | PhFe | CaNa |
Relevés numbers | 5 | 5 | 13 | 20 | 13 | 13 |
Characteristic and differential species of Poo bulbosae-Festucetum trachyphyllae (PoFe) | ||||||
Koeleria pyramidata (Lam.) P. Beauv. | 100 | 0 | 8 | 0 | 8 | 0 |
Rumex acetosella L. s.l. | 80 | 40 | 54 | 35 | 38 | 38 |
Characteristic and differential species of Holco-Chrysopogonetum grylli (HoCh) | ||||||
Brachypodium rupestre (Host) Roem. & Schult. | 0 | 100 | 77 | 15 | 46 | 23 |
Danthonia decumbens (L.) DC. | 20 | 100 | 8 | 0 | 8 | 23 |
Chrysopogon gryllus (L.) Trin. | 40 | 80 | 23 | 0 | 0 | 0 |
Characteristic and differential species of Phyteumo-Mesobrometum (PhMe) | ||||||
Thymus pulegioides L. | 80 | 100 | 100 | 65 | 92 | 38 |
Thalictrum minus L. | 20 | 40 | 92 | 55 | 46 | 15 |
Carex fritschii Waisb. | 0 | 40 | 85 | 35 | 23 | 0 |
Characteristic and differential species of Centaureo transalpinae-Arrhenatheretum (CeAr) | ||||||
Centaurea transalpina (Schleich. ex DC.) Nyman | 0 | 40 | 15 | 70 | 0 | 0 |
Characteristic and differential species of Phyteumo betonicifolii-Festucetum nigrescentis ass. nova (PhFe) | ||||||
Phyteuma betonicifolium Vill. | 20 | 20 | 62 | 55 | 92 | 62 |
Festuca nigrescens Lam. | 20 | 60 | 77 | 90 | 85 | 62 |
Poa chaixii Vill. | 0 | 0 | 15 | 10 | 85 | 31 |
Ranunculus montanus aggr. | 0 | 0 | 0 | 5 | 54 | 0 |
Chaerophyllum villarsii W. D. J. Koch | 0 | 0 | 0 | 30 | 54 | 8 |
Crocus albiflorus Kit. | 0 | 0 | 8 | 10 | 46 | 8 |
Phleum rhaeticum (Humphries) Rauschert | 0 | 0 | 0 | 0 | 46 | 8 |
Characteristic and differential species of Carici piluliferae-Nardetum (CaNa) | 0 | |||||
Carex pilulifera L. | 0 | 60 | 8 | 5 | 31 | 100 |
Nardus stricta L. | 0 | 0 | 23 | 0 | 69 | 92 |
Festuco-Brometea and affiliates | ||||||
Carex caryophyllea Latourr. | 80 | 80 | 54 | 20 | 54 | 31 |
Lotus corniculatus L. s.l. | 80 | 80 | 54 | 40 | 38 | 23 |
Ranunculus bulbosus L. | 80 | 40 | 77 | 40 | 23 | 23 |
Helianthemum nummularium (L.) Mill. | 60 | 60 | 54 | 5 | 8 | 31 |
Bromus erectus Huds. | 60 | 60 | 38 | 5 | 0 | 0 |
Silene nutans L. | 0 | 80 | 77 | 15 | 46 | 31 |
Luzula campestris (L.) DC. | 20 | 40 | 85 | 65 | 69 | 23 |
Anthericum liliago L. | 40 | 80 | 23 | 0 | 8 | 38 |
Dianthus carthusianorum L. s.l. | 60 | 20 | 46 | 5 | 8 | 15 |
Briza media L. | 0 | 60 | 54 | 20 | 54 | 23 |
Festuca ovina aggr. | 40 | 20 | 38 | 0 | 46 | 31 |
Salvia pratensis L. | 20 | 0 | 54 | 20 | 0 | 0 |
Potentilla neumanniana Rchb. | 60 | 0 | 0 | 0 | 0 | 0 |
Poa angustifolia L. | 20 | 0 | 23 | 25 | 0 | 0 |
Trifolium montanum L. | 40 | 0 | 0 | 5 | 0 | 0 |
Veronica chamaedrys L. | 0 | 0 | 31 | 55 | 69 | 15 |
Viola canina s.l. | 0 | 20 | 8 | 5 | 23 | 0 |
Helictotrichon pubescens (Huds.) Pilg. | 0 | 0 | 23 | 20 | 0 | 0 |
Silene viscaria (L.) Borkh. | 0 | 0 | 23 | 0 | 0 | 0 |
Molinio-Arrhenatheretea and affiliates | ||||||
Achillea millefolium aggr. | 60 | 80 | 85 | 100 | 92 | 8 |
Dactylis glomerata L. | 20 | 0 | 38 | 95 | 62 | 0 |
Plantago lanceolata L. | 80 | 40 | 62 | 95 | 23 | 23 |
Anthoxanthum odoratum L. | 40 | 100 | 77 | 90 | 62 | 38 |
Silene vulgaris (Moench) Garcke | 0 | 20 | 31 | 80 | 69 | 23 |
Leontodon hispidus L. | 0 | 0 | 69 | 75 | 31 | 38 |
Rumex acetosa L. | 0 | 20 | 38 | 70 | 85 | 0 |
Trisetum flavescens (L.) P. Beauv. | 0 | 0 | 38 | 70 | 38 | 8 |
Cerastium fontanum subsp. vulgare (Hartm.) Greuter & Burdet | 40 | 0 | 54 | 60 | 38 | 8 |
Trifolium repens L. | 0 | 0 | 23 | 55 | 23 | 8 |
Ranunculus acris L. | 0 | 0 | 0 | 55 | 0 | 0 |
Holcus lanatus L. | 0 | 60 | 46 | 50 | 8 | 8 |
Agrostis capillaris L. | 40 | 60 | 46 | 45 | 92 | 15 |
Viola tricolor L. | 0 | 0 | 69 | 40 | 46 | 15 |
Leucanthemum vulgare aggr. | 0 | 20 | 23 | 40 | 8 | 0 |
Lathyrus pratensis L. | 0 | 0 | 31 | 30 | 8 | 0 |
Poa pratensis L. | 0 | 0 | 15 | 30 | 8 | 0 |
Lolium perenne L. | 0 | 0 | 0 | 30 | 0 | 0 |
Ranunculus friesianus Jord. | 0 | 0 | 0 | 25 | 8 | 0 |
Prunella vulgaris L. | 0 | 40 | 0 | 25 | 0 | 0 |
Hypochaeris radicata L. | 20 | 60 | 15 | 15 | 8 | 15 |
Ajuga reptans L. | 0 | 40 | 8 | 5 | 0 | 0 |
Rorippa stylosa (Pers.) Mansf. & Rothm. | 0 | 0 | 0 | 5 | 0 | 8 |
Nardetea strictae and affiliates | ||||||
Avenella flexuosa (L.) Drejer | 0 | 20 | 23 | 5 | 38 | 62 |
Carex pallescens L. | 0 | 40 | 8 | 25 | 69 | 31 |
Alchemilla hybrida aggr. sensu K. Lauber | 0 | 0 | 8 | 0 | 38 | 15 |
Polygala vulgaris L. s.l. | 0 | 60 | 8 | 10 | 31 | 15 |
Stachys officinalis (L.) Trevis. | 0 | 80 | 15 | 5 | 23 | 15 |
Stellaria graminea L. | 0 | 0 | 0 | 20 | 31 | 9 |
Galium pumilum Murray | 0 | 0 | 15 | 10 | 31 | 0 |
Scabiosa lucida Vill. | 0 | 20 | 23 | 15 | 15 | 8 |
Other species | ||||||
Peucedanum oreoselinum (L.) Moench | 100 | 40 | 38 | 30 | 8 | 0 |
Festuca filiformis Pourr. | 20 | 100 | 46 | 0 | 46 | 77 |
Potentilla erecta (L.) Raeusch. | 0 | 80 | 23 | 40 | 62 | 62 |
Galium rubrum L. | 0 | 20 | 46 | 5 | 46 | 23 |
Veronica officinalis L. | 0 | 40 | 8 | 10 | 38 | 38 |
Vincetoxicum hirundinaria Medik. | 0 | 40 | 31 | 0 | 46 | 15 |
Clinopodium vulgare L. | 0 | 40 | 46 | 25 | 15 | 0 |
Pteridium aquilinum (L.) Kuhn | 0 | 40 | 0 | 5 | 8 | 15 |
Cruciata glabra (L.) Ehrend. | 0 | 60 | 31 | 10 | 8 | 0 |
Hypericum perforatum L. | 40 | 0 | 23 | 5 | 31 | 8 |
Calluna vulgaris (L.) Hull | 20 | 0 | 0 | 0 | 0 | 23 |
Hieracium pilosella aggr. | 20 | 20 | 23 | 0 | 0 | 15 |
Rubus fruticosus aggr. sensu Landolt /S | 0 | 20 | 0 | 0 | 0 | 15 |
Festuca paniculata (L.) Schinz & Thell. | 0 | 20 | 0 | 0 | 0 | 23 |
Hieracium lactucella Wallr. | 0 | 0 | 8 | 0 | 8 | 8 |
Vaccinium myrtillus L. | 0 | 0 | 0 | 0 | 8 | 23 |
Cytisus scoparius (L.) Link | 20 | 0 | 0 | 0 | 0 | 8 |
Molinia arundinacea Schrank | 0 | 40 | 8 | 5 | 8 | 8 |
Carex pairae F. W. Schultz | 0 | 0 | 23 | 45 | 0 | 0 |
Solidago virgaurea L. | 0 | 40 | 0 | 5 | 23 | 0 |
Rosa spec. | 0 | 20 | 15 | 0 | 23 | 0 |
Lathyrus linifolius (Reichard) Bässler | 0 | 40 | 0 | 10 | 8 | 0 |
Vaccinium vitis-idaea L. | 0 | 0 | 0 | 0 | 0 | 8 |
Arabis ciliata Clairv. | 0 | 0 | 8 | 5 | 23 | 9 |
Aira caryophyllea L. | 40 | 0 | 0 | 0 | 0 | 0 |
Myosotis arvensis Hill | 0 | 0 | 8 | 25 | 0 | 0 |
FESTUCO VALESIACAE-BROMETEA ERECTI Br.-Bl. & Tüxen ex Br.-Bl. 1949
BRACHYPODIETALIA PINNATI
Bromion erecti
Holco-Chrysopogonetum grylli Lagnaz, Trotta, Prunier, Krüsi et Boscutti 2023 ex
Phyteumo-Mesobrometum Studer-Ehrensberger, 1993
FESTUCETALIA VALESIACEAE Br.-Bl. et Tüxen ex Br.-Bl. 1949
Stipo-Poion xerophilae Br.-Bl. & Richard 1949
Poo bulbosae-Festucetum trachyphyllae Lonati & Lonati, 2007
MOLINIO-ARRHENATHERETEA Tüxen 1937
ARRHENATHERETALIA ELATIORIS Tüxen 1931
Arrhenatherion elatioris
Centaureo transalpinae-Arrhenatheretum Oberd. 1964 nom. mut. prop.
NARDETEA STRICTAE Rivas Goday in Rivas Goday & Rivas-Martínez 1963
NARDETALIA Preising 1950
Nardo strictae-Agrostion tenuis Sillinger 1933
Phyteumo betonicifolii-Festucetum nigrescentis ass. nova Carici piluliferae-Nardetum strictae Marschall and Dietl 1974
We thank Jean-Bernard Bächtiger for the field work support.
We greatly thank the Editor, the anonimous reviewer, and the reviewer Bruno Foggi for the insightful comments that greatly improved the quality of the manuscript.