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21 results for “Mediterranean high mountain”
Water column changes under ice during diferent winters in a mid-latitude Mediterranean high mountain lake - Dataset
<p>Dataset of the research article <em>Water column changes under ice during diferent winters in a mid-latitude Mediterranean high mountain lake.</em></p> <p>Granados, I., Toro, M., Giralt, S., Camacho, A., Montes, C., 2020. Water column changes under ice during different winters in a mid-latitude Mediterranean high mountain lake. Aquatic Sciences 82, 30. <a href="https://doi.org/10/ggmkhv">https://doi.org/10/ggmkhv</a></p> <p> </p>
Data from: Testing the efficiency of nested barriers to dispersal in the Mediterranean high mountain plant Edraianthus graminifolius (Campanulaceae)
Due to strong spatial heterogeneity and limited Pleistocene glaciation, the Balkan Peninsula is a major European biodiversity hotspot. Surprisingly little, however, is known about patterns and processes of intraspecific diversification of its biota in general and of high altitude species in particular. A well-suited system to test hypotheses with respect to various isolating factors acting at different geographic scales and to explore full-range phylogeographic patterns on the Balkan Peninsula is Edraianthus graminifolius (Campanulaceae), distributed in the western Balkan mountain systems, the southwestern Carpathians and the Apennine Peninsula. To this end, we used a dense population sampling and employed Amplified Fragment Length Polymorphism (AFLP) markers and plastid DNA sequences supplemented by ecological niche modelling. The strongest splits were inferred to separate southern and northern Balkan populations from the central ones, from where range extension occurred to the Carpathians and, in more recent times, once or twice to the Apennine Peninsula. The three genetic groups in the western Balkan Peninsula were remarkably congruent among molecular markers suggesting that the barriers to gene flow acted over long time periods facilitating allopatric differentiation. Each main group of Balkan populations contained genetically and geographically distinct subgroups, which likely are the result of local refugia during warmer periods. Evidently, the topographically highly complex and during the last glacial maximum only locally glaciated Balkan Peninsula is a hotspot of species richness and endemism as well as a sanctuary of intraspecific genetic diversity, even if the underlying causes remain insufficiently understood.
Data from: Testing the efficiency of nested barriers to dispersal in the Mediterranean high mountain plant Edraianthus graminifolius (Campanulaceae)
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Figure 2 from: Alonso P, Iriondo J (2014) URJC GB dataset: Community-based seed bank of Mediterranean high-mountain and semi-arid plant species at Universidad Rey Juan Carlos (Spain). PhytoKeys 35: 57-72. https://doi.org/10.3897/phytokeys.35.6746
Figure 2 - Distribution map of the two species of URJC GB dataset endemic to Spain: a Helianthemum marifolium ssp. conquense b Lupinus mariae-josephae (Source: http://www.anthos.es).
Figure 3 from: Alonso P, Iriondo J (2014) URJC GB dataset: Community-based seed bank of Mediterranean high-mountain and semi-arid plant species at Universidad Rey Juan Carlos (Spain). PhytoKeys 35: 57-72. https://doi.org/10.3897/phytokeys.35.6746
Figure 3 - Basic elements of the project design. 1 Seed collection in the target plant communities 2 Gathering of passport data on the geographical, physical and biotic features of the locality of seed collection 3 Seed processing to prepare seed accessions 4 Initial germination experiments to obtain seed germinability 5 Seed storage in cold-dry conditions 6 Use in research experiments.
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.
Figure 4 from: Pérez-Luque AJ, Barea-Azcón JM, Álvarez-Ruiz L, Bonet-García FJ, Zamora R (2016) Dataset of Passerine bird communities in a Mediterranean high mountain (Sierra Nevada, Spain). ZooKeys 552: 137-154. https://doi.org/10.3897/zookeys.552.6934
Figure 4 - Temporal coverage of the dataset. For each taxon (y-axis) the temporal coverage is shown including a point. Point size is proportional to monthly records of each taxon.
Figure 2 from: Pérez-Luque AJ, Barea-Azcón JM, Álvarez-Ruiz L, Bonet-García FJ, Zamora R (2016) Dataset of Passerine bird communities in a Mediterranean high mountain (Sierra Nevada, Spain). ZooKeys 552: 137-154. https://doi.org/10.3897/zookeys.552.6934
Figure 2 - Taxonomic families included in the dataset. The bars show the percentage of records belonging to each family.
Figure 1 from: Pérez-Luque AJ, Barea-Azcón JM, Álvarez-Ruiz L, Bonet-García FJ, Zamora R (2016) Dataset of Passerine bird communities in a Mediterranean high mountain (Sierra Nevada, Spain). ZooKeys 552: 137-154. https://doi.org/10.3897/zookeys.552.6934
Figure 1 - a Location of Sierra Nevada (southern Spain) and b distribution of transects in the Protected Natural Area of Sierra Nevada. Transect colour according to habitat type (see Methods section). A Landsat 5 Image (2001) was used as background.
Figure 5 from: Alonso P, Iriondo J (2014) URJC GB dataset: Community-based seed bank of Mediterranean high-mountain and semi-arid plant species at Universidad Rey Juan Carlos (Spain). PhytoKeys 35: 57-72. https://doi.org/10.3897/phytokeys.35.6746
Figure 5 - Taxonomic coverage (percentage per family) of URJC GB.
Figure 8 from: Alonso P, Iriondo J (2014) URJC GB dataset: Community-based seed bank of Mediterranean high-mountain and semi-arid plant species at Universidad Rey Juan Carlos (Spain). PhytoKeys 35: 57-72. https://doi.org/10.3897/phytokeys.35.6746
Figure 8 - Geographical distribution of accessions in Peninsular Spain.
Figure 6 from: Alonso P, Iriondo J (2014) URJC GB dataset: Community-based seed bank of Mediterranean high-mountain and semi-arid plant species at Universidad Rey Juan Carlos (Spain). PhytoKeys 35: 57-72. https://doi.org/10.3897/phytokeys.35.6746
Figure 6 - Geographical distribution of the germplasm subcollections in Peninsular Spain.
Figure 4 from: Alonso P, Iriondo J (2014) URJC GB dataset: Community-based seed bank of Mediterranean high-mountain and semi-arid plant species at Universidad Rey Juan Carlos (Spain). PhytoKeys 35: 57-72. https://doi.org/10.3897/phytokeys.35.6746
Figure 4 - Taxonomic coverage (percentage per order) of URJC GB.
Figure 9 from: Alonso P, Iriondo J (2014) URJC GB dataset: Community-based seed bank of Mediterranean high-mountain and semi-arid plant species at Universidad Rey Juan Carlos (Spain). PhytoKeys 35: 57-72. https://doi.org/10.3897/phytokeys.35.6746
Figure 9 - URJC Germplasm Bank workflow.
Figure 1 from: Alonso P, Iriondo J (2014) URJC GB dataset: Community-based seed bank of Mediterranean high-mountain and semi-arid plant species at Universidad Rey Juan Carlos (Spain). PhytoKeys 35: 57-72. https://doi.org/10.3897/phytokeys.35.6746
Figure 1 - Number of accessions and species in the different subcollections of the URJC GB.
Figure 7 from: Alonso P, Iriondo J (2014) URJC GB dataset: Community-based seed bank of Mediterranean high-mountain and semi-arid plant species at Universidad Rey Juan Carlos (Spain). PhytoKeys 35: 57-72. https://doi.org/10.3897/phytokeys.35.6746
Figure 7 - Temporal coverage in the different subcollections of the URJC GB.
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International Brain Laboratory public data
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OpenNeuro
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