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Figure 2 in Abrupt boundaries between mountain meadows and forests separate ground-dwelling invertebrate communities: a case study from South Tyrol, Italy
Figure 2. Unconstrained Detrended Canonical Analyses (DCA) of log-transformed abundances of ground-dwelling macroinvertebrates from montane meadows and mixed forests in South Tyrol, Italy. Data for the highest available taxonomic resolution was used (i.e. Araneae and Formicidae at species level, all other on family level, where possible). Each data point represents a pitfall trap along a linear transect starting from extensively managed hay meadows ('MM' and 'M', squares) across an abrupt ecotone ('E', diamonds) towards mixed forest stands ('F' and 'FF', circles). The size of the data points represents the number of taxa from min. 15 to max. 41.
Figure 1 in Abrupt boundaries between mountain meadows and forests separate ground-dwelling invertebrate communities: a case study from South Tyrol, Italy
Figure 1. Overview map of the study area of Barbian/Barbiano, South Tyrol (Italy), showing the three extensively managed meadows and the linear transects towards the forests. (A) Overview of the three meadows that are embedded in montane mixed forests. (B) Detailed view of a site showing the sampling design ('MM' – meadow, 'E' – ecotone, 'FF' – forest). (C) Photo of the plot EH3 (Photo credit: Michael Steinwandter). (D) Position of the study site of Barbian/Barbiano within the European Alps (red border). Aerial photographs by Google Earth.
Posidonia oceanica meadows (1120) Atokos island
<p>This layer has derived from a habitat classification using satellite imagery and ground truthing<br>data, in the context of "Protecting the Inner Ionian Archipelago and Formicula island" project.<br>The project was implemented by iSea and funded by Blue Marine Foundation the mapping was<br>produced in collaboration with terraSolutions mer. More detailed info on the product and appropriate citation can be found here:<br>https://zenodo.org/doi/10.5281/zenodo.12672634</p>
FIGURE 22 in Faunal study of velvet ants (Hymenoptera: Mutillidae) and their activity patterns and habitat preference at Ash Meadows National Wildlife Refuge, Nye County, Nevada, USA
FIGURE 22. Number of velvet ant species found per month for the 2008 and 2009 field seasons.
Figure 4 from: Pérez-Luque AJ, Sánchez-Rojas CP, Zamora R, Pérez-Pérez R, Bonet FJ (2015) Dataset of Phenology of Mediterranean high-mountain meadows flora (Sierra Nevada, Spain). PhytoKeys 46: 89-107. https://doi.org/10.3897/phytokeys.46.9116
Figure 4 - (a) Panoramic view of the borreguil of San Juan valley. The particular zonation of this ecosystem depending on soil moisture is reflected in the different colours of the borreguil. (b) Schematic representation of the vegetal communities forming the borreguiles, including dry borreguil (4 Armerio-Agrostietum nevadensis), dense grassland (1 Nardo-Festucetum ibericae), incipient peat formations (2 Ranunculo-Caricetum intrincatae) and variants of borreguil in promontory areas (3 Ranunculo-Vaccinietum uliginosi). Modified from Losa-Quintana et al. (1986). Picture: JM Martín-Martín.
Figure 5 from: Pérez-Luque AJ, Sánchez-Rojas CP, Zamora R, Pérez-Pérez R, Bonet FJ (2015) Dataset of Phenology of Mediterranean high-mountain meadows flora (Sierra Nevada, Spain). PhytoKeys 46: 89-107. https://doi.org/10.3897/phytokeys.46.9116
Figure 5 - Schema of the sampling design. a Different sampling plots were distributed along an altitudinal gradient. For the middle-altitude locality the plots were sampled in two periods: 1988–1990 and 2009–2013. View of a sampling plot of 1 × 1 m (b) that was divided into quadrats of 25 × 25 cm to facilitate counting (c) and to record the cover-abundance and the number of individuals in flowering (d) or in fruit phenophase.
Figure 2 from: Pérez-Luque AJ, Sánchez-Rojas CP, Zamora R, Pérez-Pérez R, Bonet FJ (2015) Dataset of Phenology of Mediterranean high-mountain meadows flora (Sierra Nevada, Spain). PhytoKeys 46: 89-107. https://doi.org/10.3897/phytokeys.46.9116
Figure 2 - Taxonomic coverage. The upper bar shows the percentage of records of the dataset belonging to each phylum. The bottom bars show the percentage of total records in the dataset by order. The number of records is included above the bars. The order bars is aggregated by class.
Figure 3 from: Pérez-Luque AJ, Sánchez-Rojas CP, Zamora R, Pérez-Pérez R, Bonet FJ (2015) Dataset of Phenology of Mediterranean high-mountain meadows flora (Sierra Nevada, Spain). PhytoKeys 46: 89-107. https://doi.org/10.3897/phytokeys.46.9116
Figure 3 - Taxonomic coverage (families). Percentage of dataset records by families. The numbers indicate the records of each family.
Figure 1 from: Pérez-Luque AJ, Sánchez-Rojas CP, Zamora R, Pérez-Pérez R, Bonet FJ (2015) Dataset of Phenology of Mediterranean high-mountain meadows flora (Sierra Nevada, Spain). PhytoKeys 46: 89-107. https://doi.org/10.3897/phytokeys.46.9116
Figure 1 - Location of Sierra Nevada (southern Spain) and boundaries of the National and Natural Parks (top panels). The bottom panel shows the location of the borreguiles in the San Juan river basin with the sampling plots along an altitudinal gradient.
Fig 1 from: Jung Y, Baek M, Lee S-i, Jablonski PG (2018) Microhabitat segregation among three co-existing species of grasshoppers on a rural meadow near Seoul, South Korea. Journal of Orthoptera Research 27(2): 173-175. https://doi.org/10.3897/jor.27.28402
Fig 1 The use of different types of substrates by the three grasshopper species. A. Substrates divided according to taxonomy; B. Substrates divided according to vegetation structure.
Microhabitat selection of meadow and steppe vipers enlightened by digital photography and image processing to describe grassland vegetation structure
<p>Dataset</p> <ol> <li> <p>Understanding animals’ selection of microhabitats is important in both ecology and biodiversity conservation. However, there is no generally accepted methodology for the characterisation of microhabitats, especially for vegetation structure.</p> </li> <li> <p>We studied microhabitat selection of <em>Vipera</em> snakes by comparing grassland vegetation structure between viper occurrence points and random points in three grassland ecosystems: <em>V. graeca</em> in mountain meadows of Albania, <em>V. renardi</em> in loess steppes of Ukraine, and <em>V. ursinii</em> in sand grasslands in Hungary. We quantified vegetation structure in an objective manner by automated processing of images taken of the vegetation against a vegetation profile board under standardised conditions. We developed an R script for automatic calculation of four vegetation structure variables derived from raster data obtained in the images: leaf area (LA), height of closed vegetation (HCV), maximum height of vegetation (MHC), and foliage height diversity (FHD).</p> </li> <li> <p>Generalized linear mixed models revealed that snake occurrence was positively related to HCV in <em>V. graeca</em>, to LA in <em>V. renardi</em> and to LA and MHC in <em>V. ursinii</em>, and negatively to to HCV in <em>V. ursinii</em>.</p> </li> <li> <p>Our results demonstrate that vegetation structure variables derived from automated image processing significantly influence viper microhabitat selection. Our method minimises the risk of subjectivity in measuring vegetation structure, allows upscaling if neighbouring pixels are combined, and is suitable for comparison of or extrapolation across different grasslands, vegetation types or ecosystems.</p> </li> </ol>
FIG. 4 in Multi-aged forest fragments in Atlantic France that are surrounded by meadows retain a richer epiphyte lichen flora
FIG. 4. — The significant effect of canopy density on lichen abundance according to the summary of the GLMMs. The GLMM results are presented for the exterior forest at the tree level within the FFs surrounded by meadows, taking into account the larger tree category (details as in Fig. 2).
Community species diversity mediates the trade-off between aboveground and belowground biomass for grasses and forbs in degraded alpine meadow, Tibetan Plateau
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Data from: Resident species with larger size metrics do not recruit more offspring from the seed bank in old-field meadow vegetation
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Data from: Differential responses of ecosystem carbon flux components to experimental precipitation gradient in an alpine meadow
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Data from: Nitrogen addition reduces soil respiration but increases the relative contribution of heterotrophic component in an alpine meadow
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Distribution and pollination services of wild bees and hoverflies along an altitudinal gradient in mountain hay meadows
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Long-term shifts in the functional diversity of abandoned wet meadows – Impacts of historical disturbance and successional pathways
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Male meadow vole scent marking 1 rival odor context
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Data from: Disentangling the interplay of generative and vegetative propagation among different functional groups during gap colonization in meadows
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