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Data from: Type 2 porcine reproductive and respiratory syndrome virus infection increases apoptosis at the maternal-fetal interface in late gestation pregnant gilts
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关键词:
type 2 PRRSV;maternal-fetal interface;PRRS;apoptosis
DOI:
doi:10.5061/dryad.vs27p
摘要:
thymus, and greater odds of meconium staining of the fetus at 21 days post infection (P<0.001 for both). These findings suggest an important role
Data from: Gonadotropin-releasing hormone receptor (Gnrhr) gene knock out: normal growth and development of sensory, motor and spatial orientation behavior but altered metabolism in neonatal and prepubertal mice
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DOI:
doi:10.5061/dryad.00v09
摘要:
, liver and thymus relative to body weight varied significantly in any group. However by day 28, metabolic changes in the GnRH null females compared
Data from: Phenological patterns in Mediterranean south Iberian serpentine flora
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Glandora prostrata subsp. lusitanica;Cistus populifolius subsp. major;Teucrium haenseleri;Fumana thymifolia;Erica scoparia subsp. scoparia;Arenaria montana subsp. intricata;Lavandula stoechas;phenophasic indexes;phenological phases;Halimium atriplicifolium subsp. atriplicifolium;Cistus salviifolius;Centaurea haenseleri;Thymus baeticus;Brachypodium retusum subsp. retusum;Genista hirsuta subsp. lanuginosa;Linum carratracense;Armeria colorata;climatic differences;Carex distachya;Genista triacanthos;Alyssum serpyllifolium subsp. malacitanum;Bupleurum acutifolium;Linum narbonense;Euphorbia flavicoma subsp. flavicoma;Galium boissieranum;Digitalis obscura subsp. laciniata;Sanguisorba verrucosa;serpentinophytes endemic;Ulex borgiae;Phlomis purpurea;Holocene;Staehelina baetica
DOI:
doi:10.5061/dryad.5q22b6g
摘要:
Phenological phases, as adaptive strategies, have been studied in Mediterranean serpentine shrubland vegetation and their endemisms, in the South of the Iberian Peninsula. The aim of this research is to obtain the phenological characterization of the serpentine flora and to make a comparison between endemic serpentine and non?serpentine plants in different years and altitudes. For this purpose, data were taken in the serpentine ecosystem of Sierra Bermeja (Andalusia, Spain) establishing two plots on two altitudinal bioclimatic belts and during two different years. A total of 28 persistent taxa were studied, focusing on serpentinophytes, their allied (magnesicolous) and non?serpentinophytes, trying to detect the possible differences between serpentine endemic taxa and non?endemic plants. Phenological calendars and phenological patterns (phenophasic indexes) were obtained. The species showed phenophasic patterns similar to those of other studied Mediterranean flora: a phenological pause which coincides with summer and most plants behaved as summer semi?deciduous with seasonal dimorphism. There were no statistically significant differences in phenology and in phenological indexes due to the altitude, to the year of sampling and due to the serpentine affinity. The best represented active phenophasic period of the species was 9?11 months of activity although showing the summer phenological pause. Species with low index of reproductive/vegetative activity of the species predominated, employing more time/resources for vegetative functions, and with synchronous phenophases, where flowering and growth coincide (phenophasic pattern type I). The phenophasic period of serpentinophytes and magnesicolous taxa pointed to a certain delay in the period of flowering with respect to the group of non?serpentinophytes, a result which could have reproductive implications.
Data from: Leaf carbon and oxygen isotopes are coordinated with the leaf economics spectrum in Mediterranean rangeland species
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关键词:
stomatal conductance;Carex flacca;Stipa pennata;WUE;plant strategies;Lotus corniculatus;Centaurea pectinata;Sanguisorba minor;Thymus dolomiticus;Bromopsis erecta;Koeleria vallesiana;Prunella laciniata;Leaf traits;Carex humilis;Mediterranean ecosystems;Potentilla neumanniana;leaf economics spectrum;Festuca christiani-bernardii;Helianthemum canum;C and O isotopes;Coronilla minima;Hieracium pilosella
DOI:
doi:10.5061/dryad.n848j
摘要:
The leaf economics spectrum (LES) describes covariation of traits relevant to carbon and nutrient economics across plant species, but much less is known about the relationship between the LES and leaf water economy. We propose an approach combining the measurement of two leaf traits related to water use economy, leaf carbon (?13C) and oxygen (?18O) isotopic composition, and the measurement of leaf morphological and nutrient traits to investigate the link between leaf carbon and nutrient economics and water use. We tested the relationships between leaf traits linked to carbon and nutrient use within the LES and water use traits using leaf ?18O as a proxy of stomatal conductance (gs) and ?13C as a proxy of intrinsic water use efficiency (WUEi) across 15 Mediterranean rangeland species grown in an irrigated common garden and in a natural grassland in Southern France. The target species spanned a wide range of variation in leaf morphological and nutrient trait values and a wide range of leaf ?18O and ?13C values. PCA analysis revealed multiple associations among leaf morphology, nutrients and isotopic composition, with the first axis alone explaining 56.0% of the total variation across species. Leaf ?18O and ?13C covaried with leaf morphology and leaf nutrient concentrations along a single resource use axis. Species with high leaf ?18O and ?13C (low gs and high WUEi) exhibited a resource-conservative strategy (high LDMC, low leaf N, P and K) whereas species with low leaf ?18O and ?13C (high gs and low WUEi) showed a more resource-acquisitive strategy (high SLA and leaf N, P and K). These leaf trait syndromes and resource use strategies were strongly conserved across sites with contrasting environmental conditions, indicating that foliar ?18O and ?13C can be included as an integral part of the LES for this set of rangeland species. Overall, the data suggest a tight coupling and coordination between water, carbon and nutrient use strategies across herbaceous plant species. A dual ?18O and ?13C isotope approach combined with LES trait measurements is a promising tool to more comprehensively assess the diversity of resource use strategies among coexisting plant species.
Data from: Disease where you dine: plant species and floral traits associated with pathogen transmission in bumble bees
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bee decline;Solidago canadensis;Digitalis purpurea;Linaria vulgaris;Thymus vulgaris;foraging behavior;Monarda didyma;Impatiens capensis;Verbascum thapsus;Lythrum salicaria;Bombus impatiens;Crithidia;environmental reservoir;Lobelia siphilitica;Antirrhinum majus;Bombus impatiens;floral traits;transmission hotspots;bee parasites;Helianthus annuus;Crithidia bombi;Penstemon digitalis;Asclepias incarnata;Eupatorium perfoliatum;trait-based
DOI:
doi:10.5061/dryad.0vm264s
摘要:
Hotspots of disease transmission can strongly influence pathogen spread. Bee pathogens may be transmitted via shared floral use, but the role of plant species and floral trait variation in shaping transmission dynamics is almost entirely unexplored. Given the importance of pathogens for the decline of several bee species, understanding whether and how plant species and floral traits affect transmission could give us important tools for predicting which plant species may be hotspots for disease spread. We assessed variation in transmission via susceptibility (probability of infection) and mean intensity (cell count of infected bees) of the trypanosomatid gut pathogen Crithidia bombi to uninfected Bombus impatiens workers foraging on 14 plant species, and assessed the role of floral traits, bee size and foraging behavior on transmission. We also conducted a manipulative experiment to determine how the number of open flowers affected transmission on three plant species, Penstemon digitalis, Monarda didyma, and Lythrum salicaria. Plant species differed fourfold in the overall mean abundance of Crithidia in foraging bumble bees (mean including infected and uninfected bees). Across plant species, bee susceptibility and mean intensity increased with the number of reproductive structures per inflorescence (buds, flowers and fruits); smaller bees and those that foraged longer were also more susceptible. Trait-based models were as good or better than species-based models at predicting susceptibility and mean intensity based on AIC values. Surprisingly, floral size and morphology did not significantly predict transmission across species. In the manipulative experiment, more open flowers increased mean pathogen abundance fourfold in Monarda, but had no effect in the other two plant species. Our results suggest that variation among plant species, through their influence on pathogen transmission, may shape bee disease dynamics. Given widespread investment in pollinator-friendly plantings to support pollinators, understanding how plant species affect disease transmission is important for recommending plant species that optimize pollinator health.
Data from: Climate variability and community stability in Mediterranean shrublands: the role of functional diversity and soil environment
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Cistus crispus;Cytisus grandiflorus;Erica scoparia;Juniperus phoenicea;community resistance;cold stress;Cistus libanotis;Lavandula stoechas;Ulex australis;Staurachantus genistoides;Functional traits;Rosmarinus officinalis;Myrtus communis;Phyllirea angustifolia;Halimium halimifolium;climate change;Plant\u2013climate interactions;Cistus salvifolius;Helycrissum pisardi;dry matter content;plant economics;Calluna vulgaris;Halimium commutatum;Pinus pinea;Ulex minor;conservative strategy;drought stress;Erica umbellata;Thymus mastichina;Corema album
DOI:
doi:10.5061/dryad.qc90d
摘要:
1.Understanding how different factors mediate the resistance of communities to climatic variability is a question of considerable ecological interest that remains mostly unresolved. This is particularly remarkable to improve predictions about the impact of climate change on vegetation. 2.Here we used a trait-based approach to analyse the sensitivity to climatic variability over nine years of 19 Mediterranean shrubland communities located in southwest Spain. We evaluated the role of functional diversity and soil environment as drivers of community stability (assessed as changes in plant cover, species diversity and composition). 3.The studied shrubland communities were strongly sensitive to inter-annual variability in climate. First, colder and drier conditions caused remarkable decreases in total plant cover but increased functional diversity, likely because the reduction of plant cover after harsh climatic conditions promoted the expansion of functionally dissimilar species in the new open microsites; although communities returned to their initial values of plant cover after nine years, changes in functional diversity and structure persisted over time. Second, drier and colder conditions favoured the predominance of shrubs with a conservative resource-use strategy (i.e. with higher dry matter content in leaves, stems and roots), bigger seeds and a more efficient use of water. 4.The most functionally diverse communities were the most stable over time in terms of species diversity, likely because a higher number of functionally dissimilar species allowed compensatory dynamics among them. 5.Communities inhabiting more acidic and resource-limited environments were less variable over time, probably because they were mainly constituted by slow-growth, stress-tolerant species that are potentially better adapted to harsh climatic conditions. 6.Synthesis: This study highlights the utility of a trait-based approach to evaluate how plant communities respond to climatic variability. We could infer that the increased frequency of extreme climatic events predicted by climatic models will alter the functional structure of shrubland communities, with potential repercussions for ecosystem functioning. Our results also provide new insights into the role of functional diversity and soil environment as buffers of the climate impact on woody communities, as well as potentially useful information to be applied in ecologically-based management and restoration strategies.
Data from: The abundance and distribution of guilds of riparian woody plants change in response to land use and flow regulation
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Vaccinium myrtillus;Hypericum humifussum;Rosa canina;Lavandula stoechas;Castanea sativa;Rubus genevieri;Hedera hibernica;Arbutus unedo;Salix atrocinerea;Phyllirea latifolia;Betula pubescens subsp. celtiberica;Cytisus striatus;Erica arborea;Frangula alnus;Salix neotricha;Erica tetralix;Salix alba;Quercus faginea subsp. broteroi;Cistus psilosepalus;Sesamoides sufrruticosa;Rubus brigantinus;Flueggea tinctoria;Robinia pseudoacacia;Populus x canadensis;Platanus hispanica;Cytisus scoparius;Vitis vinifera subsp. vinifera;Thymus mastichina;functional plant traits;Pinus pinaster;land use and land cover;Dittrichia viscosa;fluvial management;Quercus robur;Rubus vagabundus;hydrological alterations;Pyrus cordata;Dams;Lithodora prostrata;Fraxinus angustifolia;Rubus ulmifolius;Erica australis;Crataegus monogyna;Rubus lainzii;Salix salviifolia;Erica ciliaris;Myrtus communis;Corylus avellana;Laurus nobilis;Daphne gnidium;Hypericum androsaemum;Phyllirea angustifolia;Juglans regia;rivers;Ilex aquifolium;Sorbus aucuparia;general linear modelling;Calluna vulgaris;Erica cinerea;Ficus carica;Ulex minor;Genista florida;riparian plant guilds;Rubus radula;Prunus avium;Quercus pyrenaica;Quercus suber;Rosa pouzinii;Sambucus nigra
DOI:
doi:10.5061/dryad.rh4qm
摘要:
1. Many riparian ecosystems in Mediterranean Europe are affected by land use and flow alteration by dams. We focused on understanding how these stressors and their components affect riparian forests in the region. We asked: (i) are there well-defined, responsive riparian guilds?; (ii) do dam-induced stream flows determine abundance and distribution of riparian guilds? and (iii) what are the main drivers governing composition and cover of riparian guilds in regulated rivers? 2. We inventoried the cover of riparian woody species in free-flowing rivers and downstream of dams. We performed a cluster analysis and ordination to derive riparian guilds, using abundance data from 66 riparian woody species and 26 functional plant traits. We used a reduced set of principal components for the environment, land use and hydrology, and general linear modelling to explore the effect of these factors (separately and combined) on riparian guilds. 3. We found that: (i) four dominant guilds are responsive to disturbance in Southwestern European streams, namely the obligate riparian, water-stress tolerant, deciduous competitive, and Mediterranean evergreen guilds ; (ii) a set of land use and hydrological variables differentially affect the diverse co-occurring riparian guilds; (iii) frequency and duration of high flow pulses and the low-flow conditions were major drivers of change in landscapes dominated by intensive agriculture and forestry; (iv) storage reservoirs reduced the cover of obligate riparian and Mediterranean evergreen guilds, and increased the abundance of water-stress tolerant and deciduous competitive guilds, while run-of-river dams, having limited water storage, reduced both obligate and deciduous competitive guilds. 4. Synthesis and applications. Future research, especially in Southwestern Europe, should address the resilience of riparian guilds and the effects of interacting landscape factors and stressors on guild distribution. Stream flow regulations downstream of reservoirs should focus on specific flow components, namely the magnitude of flows, and frequency and duration of extreme flow events. For successful mitigation of the dam-induced effects on riparian vegetation, river management plans must incorporate the environmental and land use site-specific contexts.
Data from: Disentangling the processes driving plant assemblages in mountain grasslands across spatial scales and environmental gradients
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Trifolium medium;habitat filtering;Anthriscus sylvestris;Ranunculus acris s.l.;trait convergence;Luzula alpinopilosa;Vaccinium gaultherioides;Scabiosa lucida;Saxifraga paniculata;Ligusticum mutellina;Phyteuma spicatum;Achillea millefolium;Ranunculus aconitifolius;Galium megalospermum;Geranium sylvaticum;Poa supina;Crepis vesicaria s.str.;Vaccinium vitis-idaea;Pritzelago alpina s.str.;Erigeron uniflorus;Leontodon helveticus;Bromus hordeaceus;Rumex acetosa;Stachys officinalis s.l.;Helictotrichon versicolor;Polygala chamaebuxus;Calamagrostis varia;Luzula multiflora;Ajuga reptans;Trisetum flavescens;Leontodon montanus;Heracleum sphondylium s.l.;Rhinanthus alectorolophus;Arrhenatherum elatius;Poa minor;Prunella vulgaris;Gentiana verna;Trifolium badium;Holocene;Pedicularis foliosa;Filipendula ulmaria;Valeriana tripteris;Cirsium acaule;Daucus carota;Thlaspi rotundifolium aggr.;Thymus praecox subsp. polytrichus;Salix herbacea;Ononis repens;Knautia arvensis;Athamanta cretensis;Campanula cochleariifolia;Carduus defloratus s.l.;Homogyne alpina;Lolium perenne;Carex ferruginea;niche differentiation;Plantago atrata s.str.;Rhinanthus minor;Carex atrata aggr.;Saxifraga aizoides;Molinia caerulea;Galeopsis tetrahit;Chaerophyllum hirsutum aggr.;Rhododendron ferrugineum;Gentiana lutea;Ranunculus bulbosus;Cerastium latifolium;Crepis biennis;Androsace chamaejasme;Tragopogon pratensis s.l.;Aster bellidiastrum;Cerastium arvense sl;Leucanthemum vulgare aggr.;Gentiana acaulis;Saxifraga androsacea;Lolium multiflorum;Polygonum viviparum;Trisetum distichophyllum;Crepis pyrenaica;Gentiana bavarica;Medicago lupulina;Tofieldia calyculata;Epilobium anagallidifolium;Festuca quadriflora;Ranunculus alpestris;Taraxacum alpinum aggr.;Arabis alpina s.l.;Euphrasia minima;Festuca pratensis s.l.;Caltha palustris;Valeriana montana;Hippocrepis comosa;Helictotrichon pubescens;Leontodon autumnalis;Poa alpina;Carex pallescens;Hedysarum hedysaroides;Plantago media;Taraxacum officinale aggr.;Veronica officinalis;Vicia sepium;Anemone narcissiflora;Geum rivale;Hypericum maculatum s.l.;Campanula glomerata s.l.;Carex sempervirens;Valeriana dioica;Soldanella alpina;Carex flacca;Phleum pratense;Lathyrus pratensis;Allium schoenoprasum;Campanula scheuchzeri;Centaurea jacea s.str.;Gypsophila repens;Thesium alpinum;Pimpinella saxifraga;Centaurea montana;Bromus erectus s.str.;Helianthemum nummularium s.l.;Prunella grandiflora;Holcus lanatus;Onobrychis viciifolia;Primula farinosa;Trollius europaeus;Carex sylvatica;Viola biflora;spatial partitioning;Hieracium bifidum aggr.;Deschampsia cespitosa;Vaccinium myrtillus;Pimpinella major;Silene acaulis;Polygonum bistorta;Primula elatior s.str.;Alchemilla glabra aggr.;Arnica montana;Poa cenisia;environmental gradient;Brachypodium pinnatum;Euphrasia salisburgensis;Astrantia major;Hypochaeris radicata;Vicia cracca s.str.;Thymus pulegioides s.str.;Lotus corniculatus;Trifolium montanum;Lysimachia nummularia;Knautia dipsacifolia s.str.;Vicia sativa s.l.;Senecio doronicum;Acinos alpinus;Trifolium repens s.str.;Achillea atrata;Onobrychis montana;Aposeris foetida;Cruciata laevipes;Adenostyles glabra;Alchemilla conjuncta aggr.;Potentilla erecta;Euphorbia cyparissias;Fragaria vesca;Minuartia verna;Bellis perennis;Festuca violacea;Phleum rhaeticum;Plantago major s.l.;Leontodon hispidus s.l.;Rumex obtusifolius;Dryas octopetala;Luzula sieberi;Cerastium fontanum s.l.;Festuca ovina aggr.;Saxifraga moschata s.l.;Salvia pratensis;Saxifraga oppositifolia;Linum catharticum;Silene vulgaris s.l.;Agrostis schraderiana;Carlina acaulis subsp. caulescens;Origanum vulgare;Campanula barbata;Cirsium oleraceum;Centaurea scabiosa s.l.;Glechoma hederacea s.l.;Veronica chamaedrys;Veratrum album s.l.;Anthyllis vulneraria s.l.;Poa pratensis;Agrostis capillaris;Dactylis glomerata;Ranunculus montanus;Tussilago farfara;Phyteuma orbiculare;Carex nigra;limiting similarity;Geum montanum;Rumex alpestris;Globularia nudicaulis;Doronicum grandiflorum;Myosotis alpestris;Phleum hirsutum;Determinants of plant community diversity and structure;Agrostis rupestris;Gnaphalium supinum;Solidago virgaurea s.l.;Hieracium villosum;Poa trivialis s.l.;Ranunculus repens;Hieracium lactucella;Trifolium pratense s.l.;Cirsium spinosissimum;Salix retusa;Gentiana purpurea;trait divergence;Plantago alpina;Sesleria caerulea;Parnassia palustris;Globularia cordifolia;Pulsatilla alpina s.l.;Trifolium thalii;Briza media;Rumex alpinus;Clinopodium vulgare;Carex leporina;Carex panicea;Hieracium pilosella;Saxifraga biflora s.l.;Cynosurus cristatus;Plantago lanceolata;Petasites paradoxus;Veronica alpina;Bartsia alpina;Potentilla crantzii;Festuca rubra aggr.;Chaerophyllum aureum;Nardus stricta;Galium album;Anthoxanthum odoratum aggr.;Oxytropis jacquinii;Laserpitium siler;Salix reticulata;Alchemilla vulgaris aggr.;Anthropocene;Agrostis stolonifera;Linaria alpina s.str.;Sanguisorba minor s.l.;Carum carvi;Galium anisophyllon;Potentilla aurea;Veronica aphylla;Adenostyles alliariae;Primula auricula;Crepis aurea;Trifolium campestre;Euphrasia rostkoviana s.str.;Gentiana campestris s.l.;Laserpitium latifolium;Alchemilla xanthochlora aggr.
DOI:
doi:10.5061/dryad.2dq836f
摘要:
Habitat filtering and limiting similarity are well?documented ecological assembly processes that hierarchically filter species across spatial scales, from a regional pool to local assemblages. However, information on the effects of fine?scale spatial partitioning of species, working as an additional mechanism of coexistence, on community patterns is much scarcer. In this study, we quantified the importance of fine?scale spatial partitioning, relative to habitat filtering and limiting similarity in structuring grassland communities in the western Swiss Alps. To do so, 298 vegetation plots (2 m × 2 m) each with five nested subplots (20 cm × 20 cm) were used for trait?based assembly tests (i.e., comparisons with several alternative null expectations), examining the observed plot and subplot level ??diversity (indicating habitat filtering and limiting similarity) and the among?subplot ??diversity of traits (indicating fine?scale spatial partitioning). We further assessed variations in the detected signatures of these assembly processes along a set of environmental gradients. We found habitat filtering was the dominating assembly process at the plot level with diminished effect at the subplot level, whereas limiting similarity prevailed at the subplot level with weaker average effect at the plot level. Plot?level limiting similarity was positively correlated with fine?scale partitioning, suggesting that the trait divergence resulted from a combination of competitive exclusion between functionally similar species and environmental micro?heterogeneities. Overall, signatures of assembly processes only marginally changed along environmental gradients, but the observed trends were more prominent at the plot than at the subplot scale. Synthesis. Our study emphasises the importance of considering multiple assembly processes and traits simultaneously across spatial scales and environmental gradients to understand the complex drivers of plant community composition.
Data from: Predicting spatial patterns of plant species richness: a comparison of direct macroecological and species stacking modelling approaches
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关键词:
Trifolium medium;Anthriscus sylvestris;Pulsatilla alpina sl;environmental maps;Juncus effusus;Luzula alpinopilosa;Vaccinium gaultherioides;Scabiosa lucida;Saxifraga paniculata;Phyteuma spicatum;Ligusticum mutellina;Ranunculus aconitifolius;Achillea millefolium;Poa supina;Galium megalospermum;Geranium sylvaticum;Vaccinium vitis-idaea;Veronica arvensis;Heracleum sphondylium sl;Erigeron uniflorus;Leontodon helveticus;Bromus hordeaceus;Rumex acetosa;Polygala chamaebuxus;Pimpinella saxifraga aggr;Helictotrichon versicolor;Calamagrostis varia;Luzula multiflora;Pritzelago alpina sstr;Ajuga reptans;Trisetum flavescens;Viola hirta;Anthoxanthum odoratum aggr;Vicia sativa sl;Sedum atratum;Rhinanthus alectorolophus;Arrhenatherum elatius;Poa minor;Prunella vulgaris;Gentiana verna;Trifolium badium;Pedicularis foliosa;Stachys officinalis sl;Cirsium acaule;species distribution;Daucus carota;Salix herbacea;Plantago atrata sstr;Ranunculus acris sl;Knautia arvensis;Primula elatior sstr;Athamanta cretensis;Campanula cochleariifolia;Carduus defloratus sl;Plantago major sl;Homogyne alpina;Rumex crispus;Euphrasia hirtella;Botrychium lunaria;Lolium perenne;Ligusticum mutellinoides;Carex ferruginea;Rhinanthus minor;Saxifraga aizoides;Fraxinus excelsior;Potentilla sterilis;Ranunculus bulbosus;Gentiana lutea;Chaerophyllum hirsutum aggr;Crepis biennis;Cerastium latifolium;Androsace chamaejasme;Sagina saginoides;Selaginella selaginoides;Cerastium arvense sl;Aster bellidiastrum;Tragopogon pratensis sl;Gentiana acaulis;Gentiana nivalis;Thlaspi rotundifolium aggr;Polygonum viviparum;Tofieldia calyculata;Gentiana bavarica;Medicago lupulina;Crepis pyrenaica;Carex caryophyllea;Festuca quadriflora;Ranunculus alpestris;Euphrasia minima;Caltha palustris;Valeriana montana;Campanula rotundifolia;Hippocrepis comosa;Veronica serpyllifolia sl;Campanula rhomboidalis;Ranunculus montanus aggr;Carex ornithopoda;Bromus erectus sstr;Leontodon autumnalis;Helictotrichon pubescens;Poa alpina;Hedysarum hedysaroides;Carex pallescens;Plantago media;Veronica officinalis;Vicia sepium;Anemone narcissiflora;Geum rivale;Galium mollugo;Myosotis arvensis;Picea abies;Carex sempervirens;Thymus pulegioides sstr;Soldanella alpina;Carex flacca;Phleum pratense;Alchemilla xanthochlora aggr;Centaurea jacea sstr;Lathyrus pratensis;Trifolium pratense sl;Sanguisorba minor sl;Hypericum maculatum sl;Campanula scheuchzeri;Gypsophila repens;Thesium alpinum;Centaurea montana;Prunella grandiflora;Holcus lanatus;Trollius europaeus;Carex sylvatica;Primula veris sl;Luzula campestris;Festuca violacea aggr;Viola biflora;Leucanthemum vulgare aggr;Leontodon hispidus sl;Deschampsia cespitosa;Vaccinium myrtillus;Taraxacum officinale aggr;Pimpinella major;Equisetum palustre;Silene acaulis;Veronica persica;Polygonum bistorta;Arnica montana;Knautia dipsacifolia sstr;Poa cenisia;Vicia cracca sstr;Brachypodium pinnatum;Thlaspi repens;Euphrasia salisburgensis;Hypochaeris radicata;Astrantia major;Trifolium montanum;Polygala alpestris;Senecio doronicum;Colchicum autumnale;Acinos alpinus;Alchemilla coriacea aggr;Achillea atrata;Hieracium villosum aggr;Stellaria graminea;Trifolium repens sstr;Cruciata laevipes;Aposeris foetida;Viola calcarata;Adenostyles glabra;Lotus corniculatus aggr;Potentilla erecta;Euphorbia cyparissias;Gentiana clusii;Fragaria vesca;Gentiana campestris sstr;Bellis perennis;Phleum rhaeticum;Festuca rubra aggr;Dryas octopetala;Festuca pratensis sl;Carlina acaulis subsp caulescens;Cardamine pratensis;Saxifraga oppositifolia;Linum catharticum;Carex atrata aggr;Agrostis schraderiana;Campanula barbata;Solidago virgaurea sl;Cirsium oleraceum;Acer pseudoplatanus;Polygala vulgaris sl;Cirsium palustre;Carex montana;Alchemilla vulgaris aggr;Veronica chamaedrys;Gymnadenia conopsea;Silene vulgaris sl;Veratrum album subsp lobelianum;Poa pratensis;Arabis alpina sl;Agrostis capillaris;Holocene\/Anthropocene;Dactylis glomerata;Tussilago farfara;species richness modelling;Centaurea scabiosa sl;Festuca ovina aggr;Phyteuma orbiculare;Carex nigra;Geum montanum;Rumex alpestris;Globularia nudicaulis;Doronicum grandiflorum;Myosotis alpestris;Phleum hirsutum;Agrostis rupestris;Hieracium murorum aggr;Ranunculus repens;Crocus albiflorus;Hieracium bifidum aggr;Hieracium lactucella;Luzula sylvatica;Cirsium spinosissimum;Species distribution modelling;Glechoma hederacea sstr;Salix retusa;Gentiana purpurea;Poa trivialis sl;Agrostis alpina;Plantago alpina;Sesleria caerulea;Dactylorhiza fuchsii;Parnassia palustris;Globularia cordifolia;Linaria alpina sstr;Trifolium thalii;Ranunculus nemorosus aggr;Alchemilla glabra aggr;global change;Pedicularis verticillata;Briza media;Clinopodium vulgare;Carex panicea;Cynosurus cristatus;Plantago lanceolata;Petasites paradoxus;Veronica alpina;Bartsia alpina;Potentilla crantzii;Nardus stricta;Saxifraga moschata sl;Galium album;Anthyllis vulneraria sl;Thymus praecox subsp polytrichus;Salix reticulata;Galium pumilum;vegetation plots;Agrostis stolonifera;Helianthemum nummularium sl;Taraxacum alpinum aggr;Carum carvi;Galium anisophyllon;Veronica aphylla;Potentilla aurea;Primula auricula;Crepis aurea;Cerastium fontanum sl;Alchemilla conjuncta aggr;Laserpitium latifolium
DOI:
doi:10.5061/dryad.28d4k
摘要:
PLEASE NOTE, THESE DATA ARE ALSO REFERRED TO IN TWO OTHER PUBLICATIONS. PLEASE SEE http://dx.doi.org/10.1111/j.1365-2486.2008.01766.x AND http://dx.doi.org/10.1111/2041-210X.12222 FOR MORE INFORMATION. Aim: This study compares the direct, macroecological approach (MEM) for modelling species richness (SR) with the more recent approach of stacking predictions from individual species distributions (S-SDM). We implemented both approaches on the same dataset and discuss their respective theoretical assumptions, strengths and drawbacks. We also tested how both approaches performed in reproducing observed patterns of SR along an elevational gradient. Location: Two study areas in the Alps of Switzerland. Methods: We implemented MEM by relating the species counts to environmental predictors with statistical models, assuming a Poisson distribution. S-SDM was implemented by modelling each species distribution individually and then stacking the obtained prediction maps in three different ways – summing binary predictions, summing random draws of binomial trials and summing predicted probabilities – to obtain a final species count. Results: The direct MEM approach yields nearly unbiased predictions centred around the observed mean values, but with a lower correlation between predictions and observations, than that achieved by the S-SDM approaches. This method also cannot provide any information on species identity and, thus, community composition. It does, however, accurately reproduce the hump-shaped pattern of SR observed along the elevational gradient. The S-SDM approach summing binary maps can predict individual species and thus communities, but tends to overpredict SR. The two other S-SDM approaches – the summed binomial trials based on predicted probabilities and summed predicted probabilities – do not overpredict richness, but they predict many competing end points of assembly or they lose the individual species predictions, respectively. Furthermore, all S-SDM approaches fail to appropriately reproduce the observed hump-shaped patterns of SR along the elevational gradient. Main conclusions: Macroecological approach and S-SDM have complementary strengths. We suggest that both could be used in combination to obtain better SR predictions by following the suggestion of constraining S-SDM by MEM predictions.
Data from: Responses of plant community mycorrhization to anthropogenic influence depend on the habitat and mycorrhizal type
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Abies_alba Abies_grandis Abies_nordmanniana Abies_veitchii Abutilon_theophrasti Acer_campestre Acer_negundo Acer_platanoides Acer_pseudoplatanus Achillea_millefolium Achillea_ptarmica Acorus_calamus Actaea_spicata Adoxa_moschatellina Aegopodium_podagraria Aesculus_hippocastanum Aethusa_cynapium Agrimonia_eupatoria Agrostemma_githago Agrostis_canina Agrostis_capillaris Agrostis_gigantea Agrostis_stolonifera Agrostis_vinealis Ailanthus_altissima Aira_caryophyllea Aira_praecox Ajuga_reptans Alchemilla_glabra Alisma_lanceolatum Alisma_plantago-aquatica Alliaria_petiolata Allium_cepa Allium_oleraceum Allium_schoenoprasum Allium_scorodoprasum Allium_ursinum Allium_vineale Alnus_glutinosa Alnus_incana Alopecurus_aequalis Alopecurus_geniculatus Alopecurus_myosuroides Alopecurus_pratensis Althaea_officinalis Alyssum_alyssoides Amaranthus_blitum Amaranthus_hybridus Amaranthus_retroflexus Ambrosia_artemisiifolia Ammophila_arenaria Amsinckia_menziesii Anacamptis_morio Anacamptis_pyramidalis Anagallis_arvensis Anagallis_tenella Anchusa_officinalis Andromeda_polifolia Anemone_nemorosa Anemone_pulsatilla Anemone_ranunculoides Angelica_archangelica Angelica_sylvestris Antennaria_dioica Anthemis_arvensis Anthemis_cotula Anthoxanthum_aristatum Anthoxanthum_odoratum Anthriscus_cerefolium Anthriscus_sylvestris Anthyllis_vulneraria Apera_spica-venti Aphanes_arvensis Apium_graveolens Apium_nodiflorum Aquilegia_vulgaris Arabidopsis_arenosa Arabidopsis_thaliana Arabis_hirsuta Arctium_lappa Arctium_minus Arctostaphylos_uva-ursi Arenaria_serpyllifolia Armeria_maritima Armoracia_rusticana Arnica_montana Arnoseris_minima Arrhenatherum_elatius Artemisia_absinthium Artemisia_campestris Artemisia_maritima Artemisia_vulgaris Arum_italicum Arum_maculatum Asparagus_officinalis Asperugo_procumbens Asperula_cynanchica Asplenium_ruta-muraria Asplenium_scolopendrium Asplenium_trichomanes Astragalus_glycyphyllos Athyrium_filix-femina Atriplex_glabriuscula Atriplex_hortensis Atriplex_littoralis Atriplex_patula Atriplex_portulacoides Atriplex_prostrata Avena_fatua Avena_sativa Azolla_filiculoides Baldellia_ranunculoides Ballota_nigra Barbarea_stricta Barbarea_vulgaris Bellis_perennis Berberis_aquifolium Berberis_thunbergii Berberis_vulgaris Berteroa_incana Berula_erecta Beta_vulgaris Betula_pendula Betula_pubescens Bidens_cernua Bidens_frondosa Bidens_tripartita Blackstonia_perfoliata Blechnum_spicant Blysmus_rufus Bolboschoenus_maritimus Botrychium_lunaria Brachypodium_pinnatum Brachypodium_sylvaticum Brassica_juncea Brassica_napus Brassica_nigra Brassica_oleracea Brassica_rapa Briza_media Bromus_benekenii Bromus_carinatus Bromus_erectus Bromus_hordeaceus Bromus_inermis Bromus_racemosus Bromus_secalinus Bromus_sterilis Bromus_tectorum Bryonia_cretica Buddleja_davidii Buglossoides_arvensis Bunias_orientalis Butomus_umbellatus Buxus_sempervirens Cakile_maritima Calamagrostis_canescens Calamagrostis_epigejos Calamagrostis_stricta Calamistrum_globuliferum Calendula_officinalis Calla_palustris Callitriche_hamulata Callitriche_palustris Callitriche_stagnalis Calluna_vulgaris Caltha_palustris Calystegia_sepium Calystegia_soldanella Campanula_glomerata Campanula_persicifolia Campanula_rapunculoides Campanula_rotundifolia Campanula_trachelium Capsella_bursa-pastoris Cardamine_amara Cardamine_flexuosa Cardamine_hirsuta Cardamine_impatiens Cardamine_pratensis Carduus_acanthoides Carduus_nutans Carduus_tenuiflorus Carex_acuta Carex_acutiformis Carex_aquatilis Carex_arenaria Carex_buxbaumii Carex_canescens Carex_caryophyllea Carex_colchica Carex_cuprina Carex_diandra Carex_digitata Carex_dioica Carex_distans Carex_disticha Carex_divulsa Carex_echinata Carex_elongata Carex_ericetorum Carex_flacca Carex_flava Carex_hirta Carex_hostiana Carex_lasiocarpa Carex_leporina Carex_limosa Carex_muricata Carex_nigra Carex_pallescens Carex_panicea Carex_paniculata Carex_pendula Carex_pilulifera Carex_praecox Carex_pseudobrizoides Carex_pseudocyperus Carex_pulicaris Carex_remota Carex_riparia Carex_rostrata Carex_spicata Carex_sylvatica Carex_vesicaria Carex_viridula Carex_vulpina Carlina_vulgaris Carpinus_betulus Carum_carvi Castanea_sativa Catabrosa_aquatica Catapodium_rigidum Centaurea_scabiosa Centaurium_erythraea Centaurium_littorale Centaurium_pulchellum Cephalanthera_damasonium Cephalanthera_rubra Cerastium_arvense Cerastium_fontanum Cerastium_glomeratum Cerastium_semidecandrum Ceratophyllum_demersum Chaenorhinum_minus Chaerophyllum_bulbosum Chaerophyllum_temulum Chelidonium_majus Chenopodium_album Chenopodium_bonus-henricus Chenopodium_ficifolium Chenopodium_foliosum Chenopodium_glaucum Chenopodium_hybridum Chenopodium_murale Chrysosplenium_alternifolium Chrysosplenium_oppositifolium Cicendia_filiformis Cichorium_intybus Cicuta_virosa Circaea_alpina Circaea_lutetiana Cirsium_acaule Cirsium_arvense Cirsium_dissectum Cirsium_eriophorum Cirsium_oleraceum Cirsium_palustre Cirsium_vulgare Cladium_mariscus Claytonia_perfoliata Claytonia_sibirica Clematis_vitalba Clinopodium_vulgare Cochlearia_anglica Cochlearia_danica Cochlearia_officinalis Colchicum_autumnale Comarum_palustre Conium_maculatum Consolida_regalis Convallaria_majalis Convolvulus_arvensis Cornus_mas Cornus_sanguinea Cornus_suecica Corydalis_solida Corylus_avellana Corynephorus_canescens Cota_tinctoria Cotoneaster_integerrimus Crataegus_laevigata Crataegus_monogyna Crepis_biennis Crepis_capillaris Crepis_paludosa Crepis_tectorum Crocus_vernus Cruciata_laevipes Cyanus_segetum Cymbalaria_muralis Cynodon_dactylon Cynoglossum_officinale Cynosurus_cristatus Cyperus_fuscus Cystopteris_fragilis Cytisus_scoparius Dactylis_glomerata Dactylorhiza_fuchsii Dactylorhiza_incarnata Dactylorhiza_maculata Dactylorhiza_majalis Dactylorhiza_praetermissa Dactylorhiza_viridis Danthonia_decumbens Daphne_mezereum Datura_stramonium Daucus_carota Deschampsia_cespitosa Deschampsia_flexuosa Descurainia_sophia Dianthus_armeria Dianthus_carthusianorum Dianthus_deltoides Digitalis_purpurea Digitaria_ischaemum Digitaria_sanguinalis Diphasiastrum_complanatum Diplotaxis_muralis Dipsacus_fullonum Drosera_anglica Drosera_intermedia Drosera_rotundifolia Dryopteris_carthusiana Dryopteris_cristata Dryopteris_dilatata Dryopteris_filix-mas Echinochloa_crus-galli Echium_vulgare Egeria_densa Elaeagnus_rhamnoides Elatine_hexandra Eleocharis_acicularis Eleocharis_multicaulis Eleocharis_palustris Eleocharis_quinqueflora Eleocharis_uniglumis Elodea_canadensis Elymus_caninus Elymus_farctus Elymus_repens Empetrum_nigrum Epilobium_angustifolium Epilobium_ciliatum Epilobium_hirsutum Epilobium_lanceolatum Epilobium_montanum Epilobium_obscurum Epilobium_palustre Epilobium_parviflorum Epilobium_roseum Epilobium_tetragonum Epipactis_helleborine Epipactis_palustris Equisetum_arvense Equisetum_fluviatile Equisetum_hyemale Equisetum_palustre Equisetum_ramosissimum Equisetum_sylvaticum Equisetum_variegatum Eragrostis_minor Eragrostis_pilosa Erica_cinerea Erica_tetralix Erigeron_acer Erigeron_annuus Erigeron_canadensis Eriophorum_angustifolium Eriophorum_gracile Eriophorum_latifolium Eriophorum_vaginatum Erodium_cicutarium Erophila_verna Erucastrum_gallicum Eryngium_campestre Eryngium_maritimum Erysimum_cheiranthoides Eschscholzia_californica Euonymus_europaeus Eupatorium_cannabinum Euphorbia_amygdaloides Euphorbia_cyparissias Euphorbia_esula Euphorbia_helioscopia Euphorbia_lathyris Euphorbia_palustris Euphorbia_paralias Euphorbia_peplus Euphorbia_seguieriana Euphorbia_stricta Euphrasia_stricta Fagopyrum_esculentum Fagus_sylvatica Fallopia_convolvulus Fallopia_dumetorum Festuca_arundinacea Festuca_gigantea Festuca_ovina Festuca_pratensis Festuca_rubra Ficaria_verna Filipendula_ulmaria Fragaria_moschata Fragaria_vesca Frangula_alnus Fraxinus_excelsior Fumaria_officinalis Gagea_lutea Galanthus_nivalis Galeopsis_bifida Galeopsis_segetum Galeopsis_speciosa Galeopsis_tetrahit Galinsoga_parviflora Galinsoga_quadriradiata Galium_aparine Galium_boreale Galium_mollugo Galium_odoratum Galium_palustre Galium_saxatile Galium_tricornutum Galium_uliginosum Galium_verum Genista_anglica Genista_germanica Genista_pilosa Genista_tinctoria Gentiana_cruciata Gentiana_pneumonanthe Gentianella_amarella Gentianella_campestris Gentianella_germanica Geranium_dissectum Geranium_lucidum Geranium_molle Geranium_pratense Geranium_pusillum Geranium_pyrenaicum Geranium_robertianum Geranium_rotundifolium Geranium_sanguineum Geum_rivale Geum_urbanum Glaucium_flavum Glebionis_segetum Glechoma_hederacea Glyceria_fluitans Glyceria_maxima Glyceria_notata Glycine_max Gnaphalium_sylvaticum Gnaphalium_uliginosum Goodyera_repens Gratiola_officinalis Gymnadenia_conopsea Gymnocarpium_dryopteris Hammarbya_paludosa Hedera_helix Helianthemum_nummularium Helianthus_annuus Helianthus_tuberosus Helictotrichon_pratense Helictotrichon_pubescens Helminthotheca_echioides Heracleum_mantegazzianum Heracleum_sphondylium Herminium_monorchis Hesperis_matronalis Hieracium_laevigatum Hieracium_umbellatum Hierochloe_odorata Hippocrepis_comosa Hippuris_vulgaris Holcus_lanatus Holcus_mollis Holosteum_umbellatum Honckenya_peploides Hordeum_distichon Hordeum_jubatum Hordeum_murinum Hordeum_vulgare Hottonia_palustris Humulus_lupulus Huperzia_selago Hyacinthoides_non-scripta Hydrocotyle_vulgaris Hyoscyamus_niger Hypericum_hirsutum Hypericum_humifusum Hypericum_maculatum Hypericum_montanum Hypericum_perforatum Hypericum_pulchrum Hypochaeris_glabra Hypochaeris_radicata Iberis_amara Ilex_aquifolium Impatiens_glandulifera Impatiens_noli-tangere Impatiens_parviflora Inula_britannica Inula_conyzae Iris_pseudacorus Isatis_tinctoria Isoetes_echinospora Iva_xanthiifolia Jacobaea_vulgaris Jasione_montana Juglans_regia Juncus_acutiflorus Juncus_alpinoarticulatus Juncus_articulatus Juncus_balticus Juncus_bufonius Juncus_bulbosus Juncus_conglomeratus Juncus_effusus Juncus_filiformis Juncus_gerardii Juncus_inflexus Juncus_maritimus Juncus_pygmaeus Juncus_squarrosus Juncus_tenuis Juniperus_communis Kickxia_spuria Knautia_arvensis Koeleria_macrantha Koeleria_pyramidata Laburnum_anagyroides Lactuca_muralis Lactuca_serriola Lactuca_tatarica Lamium_album Lamium_amplexicaule Lamium_galeobdolon Lamium_purpureum Laphangium_luteoalbum Lappula_myosotis Lapsana_communis Larix_decidua Larix_kaempferi Lathyrus_aphaca Lathyrus_japonicus Lathyrus_linifolius Lathyrus_palustris Lathyrus_pratensis Lathyrus_sylvestris Lathyrus_tuberosus Leersia_oryzoides Lemna_gibba Lemna_minor Lemna_trisulca Leontodon_hispidus Leontodon_saxatilis Leopoldia_comosa Lepidium_campestre Lepidium_didymum Lepidium_draba Lepidium_ruderale Lepidium_virginicum Leucanthemum_vulgare Leucojum_aestivum Leucojum_vernum Leymus_arenarius Ligustrum_vulgare Lilium_martagon Limonium_vulgare Limosella_aquatica Linaria_vulgaris Linnaea_borealis Linum_catharticum Linum_usitatissimum Liparis_loeselii Lithospermum_officinale Littorella_uniflora Lobularia_maritima Lolium_multiflorum Lolium_perenne Lolium_temulentum Lonicera_periclymenum Lonicera_xylosteum Lotus_corniculatus Lotus_pedunculatus Lotus_tenuis Ludwigia_palustris Lunaria_annua Lunaria_rediviva Lupinus_angustifolius Lupinus_luteus Lupinus_polyphyllus Luzula_campestris Luzula_luzuloides Luzula_multiflora Luzula_pilosa Luzula_sylvatica Lycium_barbarum Lycopodiella_inundata Lycopodium_annotinum Lycopodium_clavatum Lycopus_europaeus Lysimachia_europaea Lysimachia_maritima Lysimachia_nemorum Lysimachia_nummularia Lysimachia_punctata Lysimachia_thyrsiflora Lysimachia_vulgaris Lythrum_salicaria Maianthemum_bifolium Malus_domestica Malva_neglecta Malva_sylvestris Marrubium_vulgare Matricaria_chamomilla Matricaria_discoidea Medicago_falcata Medicago_lupulina Medicago_minima Medicago_sativa Melampyrum_arvense Melampyrum_pratense Melica_nutans Melica_uniflora Melilotus_albus Melilotus_officinalis Mentha_aquatica Mentha_arvensis Mentha_longifolia Mentha_pulegium Mentha_spicata Menyanthes_trifoliata Mercurialis_annua Mercurialis_perennis Milium_effusum Milium_vernale Minuartia_hybrida Moehringia_trinervia Molinia_caerulea Monotropa_hypopitys Montia_fontana Muscari_armeniacum Muscari_botryoides Myosotis_arvensis Myosotis_discolor Myosotis_laxa Myosotis_ramosissima Myosotis_scorpioides Myosotis_stricta Myosotis_sylvatica Myosurus_minimus Myrica_gale Myriophyllum_alterniflorum Myriophyllum_spicatum Narcissus_poeticus Narcissus_pseudonarcissus Nardus_stricta Narthecium_ossifragum Nasturtium_microphyllum Nasturtium_officinale Neottia_cordata Neottia_nidus-avis Neottia_ovata Nepeta_cataria Neslia_paniculata Nuphar_lutea Nymphaea_alba Nymphoides_peltata Odontites_vernus Oenanthe_aquatica Oenanthe_crocata Oenanthe_fistulosa Oenanthe_lachenalii Oenothera_glazioviana Onobrychis_viciifolia Ononis_spinosa Onopordum_acanthium Ophioglossum_vulgatum Ophrys_apifera Ophrys_insectifera Orchis_anthropophora Orchis_mascula Orchis_militaris Orchis_purpurea Origanum_vulgare Ornithogalum_nutans Ornithogalum_umbellatum Osmunda_regalis Oxalis_acetosella Oxalis_stricta Panicum_miliaceum Papaver_rhoeas Papaver_somniferum Parentucellia_viscosa Parietaria_judaica Paris_quadrifolia Parnassia_palustris Parthenocissus_inserta Pastinaca_sativa Pedicularis_palustris Pedicularis_sylvatica Persicaria_amphibia Persicaria_bistorta Persicaria_hydropiper Persicaria_lapathifolia Persicaria_maculosa Persicaria_mitis Petasites_hybridus Petroselinum_crispum Peucedanum_palustre Phacelia_tanacetifolia Phalaris_arundinacea Phaseolus_vulgaris Phegopteris_connectilis Philadelphus_coronarius Phleum_arenarium Phleum_pratense Phragmites_australis Physalis_alkekengi Phyteuma_spicatum Picea_abies Picea_sitchensis Picris_hieracioides Pilosella_aurantiaca Pilosella_caespitosa Pilosella_lactucella Pilosella_officinarum Pimpinella_major Pimpinella_saxifraga Pinguicula_vulgaris Pinus_nigra Pinus_pinaster Pinus_strobus Pinus_sylvestris Pisum_sativum Plantago_coronopus Plantago_lanceolata Plantago_major Plantago_maritima Plantago_media Platanthera_bifolia Platanthera_chlorantha Poa_angustifolia Poa_annua Poa_bulbosa Poa_compressa Poa_nemoralis Poa_palustris Poa_pratensis Poa_trivialis Polygala_comosa Polygala_serpyllifolia Polygala_vulgaris Polygonatum_multiflorum Polygonatum_odoratum Polygonatum_verticillatum Polygonum_aviculare Polygonum_maritimum Polypodium_vulgare Polystichum_aculeatum Populus_alba Populus_balsamifera Populus_deltoides Populus_nigra Populus_tremula Potamogeton_crispus Potamogeton_gramineus Potamogeton_lucens Potamogeton_natans Potamogeton_nodosus Potamogeton_perfoliatus Potamogeton_polygonifolius Potentilla_anglica Potentilla_anserina Potentilla_argentea Potentilla_erecta Potentilla_recta Potentilla_reptans Potentilla_sterilis Potentilla_supina Primula_elatior Primula_veris Primula_vulgaris Prunella_vulgaris Prunus_avium Prunus_cerasifera Prunus_domestica Prunus_padus Prunus_serotina Prunus_spinosa Pseudotsuga_menziesii Pteridium_aquilinum Puccinellia_distans Puccinellia_maritima Pulicaria_dysenterica Pulmonaria_officinalis Pyrola_minor Pyrola_rotundifolia Pyrus_communis Quercus_petraea Quercus_robur Quercus_rubra Ranunculus_acris Ranunculus_aquatilis Ranunculus_arvensis Ranunculus_auricomus Ranunculus_bulbosus Ranunculus_circinatus Ranunculus_flammula Ranunculus_fluitans Ranunculus_lingua Ranunculus_polyanthemos Ranunculus_repens Ranunculus_sardous Ranunculus_sceleratus Raphanus_raphanistrum Reseda_alba Reseda_lutea Reseda_luteola Reynoutria_japonica Reynoutria_sachalinensis Rhamnus_cathartica Rhinanthus_minor Rhinanthus_serotinus Rhododendron_ponticum Rhynchospora_alba Ribes_alpinum Ribes_nigrum Ribes_rubrum Ribes_uva-crispa Ricinus_communis Robinia_pseudoacacia Rorippa_amphibia Rorippa_austriaca Rorippa_palustris Rosa_arvensis Rosa_canina Rosa_majalis Rosa_rubiginosa Rosa_rugosa Rosa_xanthina Rubus_caesius Rubus_idaeus Rubus_nessensis Rubus_phoenicolasius Rubus_plicatus Rubus_saxatilis Rubus_spectabilis Rudbeckia_laciniata Rumex_acetosa Rumex_acetosella Rumex_aquaticus Rumex_conglomeratus Rumex_crispus Rumex_hydrolapathum Rumex_obtusifolius Rumex_palustris Rumex_thyrsiflorus Sagina_apetala Sagina_maritima Sagina_nodosa Sagina_procumbens Sagittaria_sagittifolia Salicornia_europaea Salix_alba Salix_aurita Salix_caprea Salix_cinerea Salix_daphnoides Salix_gmelinii Salix_integra Salix_pentandra Salix_purpurea Salix_repens Salix_triandra Salix_viminalis Salsola_kali Salvia_pratensis Salvia_verticillata Sambucus_canadensis Sambucus_nigra Sambucus_racemosa Samolus_valerandi Sanguisorba_minor Sanguisorba_officinalis Sanicula_europaea Saponaria_officinalis Saxifraga_granulata Scabiosa_columbaria Scandix_pecten-veneris Scheuchzeria_palustris Schoenoplectus_americanus Schoenoplectus_lacustris Schoenoplectus_tabernaemontani Schoenus_nigricans Scilla_siberica Scirpus_sylvaticus Scleranthus_annuus Scorzonera_humilis Scorzoneroides_autumnalis Scrophularia_auriculata Scrophularia_nodosa Scrophularia_umbrosa Scrophularia_vernalis Scutellaria_galericulata Secale_cereale Securigera_varia Sedum_acre Sedum_album Sedum_maximum Sedum_rupestre Sedum_spurium Sedum_telephium Sempervivum_tectorum Senecio_inaequidens Senecio_nemorensis Senecio_sylvaticus Senecio_viscosus Senecio_vulgaris Serratula_tinctoria Sesleria_albicans Setaria_pumila Setaria_verticillata Setaria_viridis Sherardia_arvensis Silaum_silaus Silene_baccifera Silene_conica Silene_dioica Silene_flos-cuculi Silene_gallica Silene_latifolia Silene_noctiflora Silene_nutans Silene_otites Silene_vulgaris Sinapis_alba Sinapis_arvensis Sisymbrium_altissimum Sisymbrium_loeselii Sisymbrium_officinale Sisymbrium_orientale Sium_latifolium Solanum_americanum Solanum_dulcamara Solanum_tuberosum Solidago_canadensis Solidago_gigantea Solidago_virgaurea Sonchus_arvensis Sonchus_asper Sonchus_oleraceus Sorbus_aria Sorbus_aucuparia Sparganium_angustifolium Sparganium_emersum Sparganium_erectum Sparganium_natans Spartina_anglica Spergula_arvensis Spergula_morisonii Spergularia_marina Spergularia_media Spergularia_rubra Spinacia_oleracea Spiraea_salicifolia Spiranthes_spiralis Spirodela_polyrrhiza Stachys_officinalis Stachys_palustris Stachys_sylvatica Stellaria_aquatica Stellaria_cuspidata Stellaria_graminea Stellaria_holostea Stellaria_media Stellaria_nemorum Stellaria_pallida Stellaria_palustris Stellaria_uliginosa Stuckenia_pectinata Suaeda_maritima Succisa_pratensis Symphoricarpos_albus Symphyotrichum_lanceolatum Symphytum_officinale Syringa_vulgaris Tanacetum_parthenium Tanacetum_vulgare Taraxacum_campylodes Taxus_baccata Tephroseris_palustris Tetragonia_tetragonioides Teucrium_botrys Teucrium_chamaedrys Teucrium_montanum Teucrium_scorodonia Thalictrum_minus Thelypteris_confluens Thesium_humifusum Thlaspi_arvense Thlaspi_caerulescens Thlaspi_perfoliatum Thuja_occidentalis Thuja_plicata Thymus_praecox Thymus_pulegioides Thymus_serpyllum Thymus_vulgaris Tilia_cordata Tilia_platyphyllos Torilis_arvensis Torilis_japonica Tragopogon_dubius Tragopogon_orientalis Tragopogon_pratensis Trapa_natans Trichophorum_cespitosum Trifolium_arvense Trifolium_campestre Trifolium_dubium Trifolium_fragiferum Trifolium_hybridum Trifolium_incarnatum Trifolium_medium Trifolium_pratense Trifolium_repens Trifolium_resupinatum Trifolium_subterraneum Triglochin_maritima Triglochin_palustris Tripleurospermum_maritimum Tripolium_pannonicum Trisetum_flavescens Triticum_aestivum Tsuga_heterophylla Tuberaria_guttata Turritis_glabra Tussilago_farfara Typha_angustifolia Typha_latifolia Ulex_europaeus Ulmus_glabra Ulmus_laevis Ulmus_minor Urtica_dioica Urtica_urens Vaccinium_corymbosum Vaccinium_macrocarpon Vaccinium_myrtillus Vaccinium_oxycoccos Vaccinium_uliginosum Vaccinium_vitis-idaea Valeriana_dioica Valeriana_officinalis Valerianella_locusta Verbascum_lychnitis Verbascum_nigrum Verbascum_phlomoides Verbascum_thapsus Verbena_officinalis Veronica_agrestis Veronica_anagallis-aquatica Veronica_arvensis Veronica_austriaca Veronica_beccabunga Veronica_catenata Veronica_chamaedrys Veronica_hederifolia Veronica_longifolia Veronica_officinalis Veronica_peregrina Veronica_persica Veronica_praecox Veronica_scutellata Veronica_serpyllifolia Veronica_verna Viburnum_lantana Viburnum_opulus Vicia_cracca Vicia_faba Vicia_hirsuta Vicia_sativa Vicia_sepium Vicia_tetrasperma Vicia_villosa Vinca_minor Vincetoxicum_hirundinaria Viola_arvensis Viola_canina Viola_hirta Viola_lutea Viola_odorata Viola_palustris Viola_persicifolia Viola_reichenbachiana Viola_riviniana Viola_rupestris Viola_tricolor Vulpia_bromoides Vulpia_myuros Zannichellia_palustris Zea_mays Zostera_marina;alien plant species;Mycorrhizal symbiosis;naturalness;urbanity;anthropogenic impact;arbuscular mycorrhiza
DOI:
doi:10.5061/dryad.v87q30f
摘要:
Anthropogenic impact represents a major pressure on ecosystems, yet little is known about how it affects symbiotic relationships, such as mycorrhizal symbiosis, which plays a crucial role in ecosystem functioning. We analyzed the effects of three human impact types – increasing urbanity, introduction of alien plant species (alienness) and modifications in plant species distribution ranges (as a proxy for naturalness) – on plant community mycorrhization and arbuscular mycorrhization (indicating the degree of forming mycorrhizal symbiosis at plant community level using the relative abundance of mycorrhizal and arbuscular mycorrhizal plants, respectively). The study was carried out in three habitat types, each dominated by a distinct mycorrhizal type – ectomycorrhizal woodlands, ericoid mycorrhizal heathlands and arbuscular mycorrhizal grasslands - at the regional scale in the Netherlands. The response of community mycorrhization and arbuscular mycorrhization to anthropogenic influence showed contrasting patterns, depending on the specific aspect of human impact. Community mycorrhization responded negatively to urbanity and positively to increasing alienness, while arbuscular mycorrhization showed the reverse trend. More natural heathlands were found to be more mycorrhizal and less arbuscular mycorrhizal. The strongest responses were detected in woodlands and heathlands, while mycorrhization in grasslands was relatively insensitive to human impact. Our study highlights the importance of considering mycorrhizal symbiosis in understanding and quantifying the effects of anthropogenic influence on plant communities, especially in woodlands and heathlands.

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