Data from: How to best threshold and validate stacked species assemblages? Community optimisation might hold the answer

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Primula acaulis;Zygaena filipendulae;Anthriscus sylvestris;Bromus benekenii;Stachys sylvatica;Neottia nidus avis;Aphantopus hyperantus;grasshoppers;Ligusticum mutellina;Phyteuma spicatum;Ranunculus aconitifolius;Geranium sylvaticum;Colias crocea;Glechoma hederacea;Polyommatus Lysandra coridon;Cephalanthera rubra;Polygala chamaebuxus;Calamagrostis varia;Ajuga reptans;insects;Viola hirta;Erynnis tages;Carduus personata;Holocene;Filipendula ulmaria;Lamium purpureum;Euthystira brachyptera;Eupatorium cannabinum;Asplenium trichomanes;Melitaea Mellicta athalia;Dryopteris oreades;Homogyne alpina;Viburnum opulus;Omocestus viridulus;Tettigonia cantans;Cystopteris fragilis;Galium odoratum;Viola reichenbachiana;Sorbus aucuparia;Aconitum napellus aggr;Galeopsis tetrahit;Rhododendron ferrugineum;Sanicula europaea;Carlina simplex;Prunus avium;Ribes alpinum;Thymelicus sylvestris;Vincetoxicum hirundinaria;Pulmonaria officinalis;Sambucus nigra;Cotoneaster tomentosus;Pyrgus serratulae;Populus 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digitata;Allium ursinum;Gryllus campestris;Castanea sativa;Sorbus aria;Hesperia comma;Saxifraga paniculata;Circaea lutetiana;Hypericum maculatum;Ranunculus platanifolius;Myosotis sylvatica;Moehringia muscosa;Acer campestre;Aconitum lycoctonum aggr;Prunella vulgaris;Carex alba;Hippocrepis emerus;Boloria napaea;Valeriana tripteris;Solanum dulcamara;Boloria clossiana titania;Lycaena tityrus;Listera ovata;Trifolium pratense;Hedera helix;Prenanthes purpurea;Crepis paludosa;Campanula cochleariifolia;Actaea spicata;Leptidea reali sinapis;Taraxacum officinale;community models;Carex ferruginea;Juglans regia;Dryopteris carthusiana;Poa nemoralis;Hieracium vogesiacum;Lonicera xylosteum;Larix decidua;Fraxinus excelsior;Cardamine heptaphylla;Potentilla sterilis;Gentiana lutea;Rosa arvensis;Aquilegia vulgaris;Anthriscus nitida;Impatiens noli tangere;Veronica urticifolia;Pinus uncinata;Aster bellidiastrum;Rubus saxatilis;Acer opalus;Achillea macrophylla;Maculinea arion;Zygaena lonicerae;Orchis 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richness modelling;Euonymus europaeus;Listera cordata;Petasites hybridus;Erebia pharte;Luzula luzulina;Euphydryas aurinia;Stauroderus scalaris;Lasiommata maera;Rosa pendulina;Pieris napi;Gentiana purpurea;Laburnum alpinum;Salix appendiculata;Polygonatum multiflorum;Vicia sylvatica;Vanessa atalanta;Daphne laureola;Briza media;Clinopodium vulgare;Lonicera caerulea;Luzula pilosa;Thymelicus lineola;Cornus sanguinea;Nardus stricta;Melanargia galathea;Chorthippus parallelus;Metrioptera saussuriana;Carex humilis;Aquilegia atrata;Pieris brassicae;Dryopteris dilatata;Dryopteris filix mas;Taxus baccata;Thalictrum aquilegiifolium;Corylus avellana;Melica uniflora;Maianthemum bifolium;vegetation plots;Malus sylvestris;Scrophularia nodosa;Adenostyles alliariae;Epipactis helleborine;Gentiana asclepiadea;Blechnum spicant;Miramella alpina;Streptopus amplexifolius

DOI：

doi:10.5061/dryad.nf925ps

摘要：

ing method depends on taxa, prevalence distribution and/or species richness. Based on a comparison of different evaluation approaches, we provide guidelines