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19,493 results for “Populism”
Figure 1 in First data on population estimates and dispersal of Montenegrina subcristata - a field study at Virpazar, Montenegro
Figure 1. Study area with three study sites (A, B, C). Note that due to the perspective view site B and C appear much smaller.
Figure 4. A cove with shallow water near Ponte Porton with 14 in Populations of Microcondylaea bonellii (Férussac 1827), Unionidae - an european freshwater mussel at rapid decline - and Unio mancus in Istria, Croatia
Figure 4. A cove with shallow water near Ponte Porton with 14 individuals of Microcondylaea bonellii (26.9.2009).
Figure 3 in Populations of Microcondylaea bonellii (Férussac 1827), Unionidae - an european freshwater mussel at rapid decline - and Unio mancus in Istria, Croatia
Figure 3. Numbers of shells of Unio mancus (blue) and Microcondylaea bonelli at the different sites (red).
Fig. 2 and 3 in Populations of Microcondylaea bonellii (Férussac 1827), Unionidae - an european freshwater mussel at rapid decline - and Unio mancus in Istria, Croatia
Fig. 2 and 3 give the results of my surveys in river Mirna in 2009 to 2016. In the upper part of the river from the city of Buzet to the confluence with Butoniga the artificially straightened riverbed is dominated by coarse gravel and shows ± rapid current. Although Microcondylaea was recorded from this part of the river near Istarske Teplice (Fischer 1999) no shells or living specimens were found actually. Populations of Unio mancus were mainly found in tributaries like Bračana and drenches, less frequently in the riverbed of upper Mirna. Between 2009 and 2016 the Mirna-riverbed was reconstructed in several places, eroded banks with coves and fine sand substrate were replaced by blocks of stone and the riverbed straightened again. Thus many suitable habitats and eventually existing mussels-populations were destroyed, so much the worse as heavy machines were driving in the riverbed over many weeks for the construction works and mobilized the substrate, which led to high accumulations of fine sediment in the lower part of the river, especially in parts with low current and coves which were inhabited by Microcondylaea.
Figure 1 in Populations of Microcondylaea bonellii (Férussac 1827), Unionidae - an european freshwater mussel at rapid decline - and Unio mancus in Istria, Croatia
Figure 1. Map of known living populations of Microcondylaea bonelli in Slovenia (grey) and Italy (yellow) from http://art17.eionet.europa.eu/article17/reports2012/species/summary/. Populations in Croatia (red) added by the author.
Figure 5 in The Population Ecology of (Kusn.) Woronow in the Highlands of the Republic of Adygea
Figure 5. Intrapopulation and ecological-geographical variability of G. oschtenica: 1 – the length of the calyx; 2 – the length of the prong cup; 3 – the ratio of calyx length to the length of the prong; 4 – cup wing width; 5 – the length of the corolla limb; 6 – the diameter of the rim at the limb; 7 – the length of the blade of the limb; 8 – length of escape to the base of the cup; 9 – the length of the rosette leaf; 10 – width of rosette leaf; 11 – length of penultimate sheet; 12 – the width of the penultimate leaf; 13 – length of the last sheet; 14 – the width of the last sheet.
Figure 4 in The Population Ecology of (Kusn.) Woronow in the Highlands of the Republic of Adygea
Figure 4. Ontogenetic structure of coenopopulations G. oschtenica: 1-4 – subalpine cenopopulation; 5-8– alpine cenopopulation; 7-8 – rocky-scree cenopopulations.
Figure 2 in Impact of poaching on the population structure and insect associates of the Endangered Encephalartos eugene-maraisii from South Africa
Figure 2. Insects associated with Encephalartos eugene-maraisii in Entabeni: A, B, Amorphocerus cf. setosus; C, D, Apinotropis verdoornae; E, F, Zerenopsis lepida. Photographs: P.D. Janse van Rensburg.
Figure 4 in Impact of poaching on the population structure and insect associates of the Endangered Encephalartos eugene-maraisii from South Africa
Figure 4. Large Encephalartos eugene-maraisii stem that was pushed over by poachers. Photographer: P.D. Janse van Rensburg.
Figure 1 in Impact of poaching on the population structure and insect associates of the Endangered Encephalartos eugene-maraisii from South Africa
Figure 1. Typical architecture of an Encephalartos eugene-maraisii plant. Photographer: P.D. Janse van Rensburg.
Figure 3 in Impact of poaching on the population structure and insect associates of the Endangered Encephalartos eugene-maraisii from South Africa
Figure 3. Distribution of Encephalartos eugene-maraisii in the Entabeni Safari Conservancy between 2021 and 2022, compared to 2008. A, heatmap of E. eugene-maraisii plants re-recorded between 2021 and 2022; B, heatmap of E. eugene-maraisii plants that were not relocated. Lines indicate the fence line. The map is given without a geographical reference because E. eugene-maraisii is vulnerable to poaching.
Figure 6 in Far from urban areas: plastic uptake in fish populations of subtropical headwater streams
Figure 6. Median plastic particle distribution in fishes per sample site (whiskers = min - max values, dots = outliers, stars = extreme outliers, horizontal line = median, box = 50% tile).
Figure 3 in Far from urban areas: plastic uptake in fish populations of subtropical headwater streams
Figure 3. Plastic particles abundances in benthic and water column feeders (whiskers = min - max values, dots outliers, stars extreme outliers, horizontal line median, box 50% tile).
Figure 1. Study area. A. South America and Brazil. B in Far from urban areas: plastic uptake in fish populations of subtropical headwater streams
Figure 1. Study area. A. South America and Brazil. B. Brazil and the state of Rio Grande do Sul. C. Rio Grande do Sul and the Sinos River Basin. D. The numbers from 1 to 7 in the white dots show the sampling sites in the upper section of the Sinos River basin. The colour gradient represents the terrain elevation (light green elevations of 30m altitude and dark brown elevations of 980m). The red polygons are the urban areas.
Figure 5 in Far from urban areas: plastic uptake in fish populations of subtropical headwater streams
Figure 5. Total abundances of food items per category in comparison with ingested plastic particles abundances. (Pla=Pastics, Dip=Diptera, Hem=Hemiptera, Tri=Tricoptera, Lep=Lepidoptera, Eph=Ephemeroptera, Ple=Plecoptera, Col=Coleoptera, Gas=Gastropoda, Odo=Odonata, Veg= Plant).
FIGURE 9 in Morphology and Systematics of Kalophrynus interlineatus-pleurostigma Populations (Anura: Microhylidae: Kalophryninae) and a Taxonomy of the Genus Kalophrynus Tschudi, Asian Sticky Frogs
FIGURE 9. Distribution of Kalophrynus meizon (Borneo). Solid circle denote specimens examined in this study; open circles are literature records and museum records of specimens not examined.
FIGURE 2 in Morphology and Systematics of Kalophrynus interlineatus-pleurostigma Populations (Anura: Microhylidae: Kalophryninae) and a Taxonomy of the Genus Kalophrynus Tschudi, Asian Sticky Frogs
FIGURE 2. Schematic ventral view of the right (A) fore- and (B) hindfoot of Kalophrynus anya sp. nov. (USNM 537420). Scale bar equals ~1 mm.
FIGURE 3 in Morphology and Systematics of Kalophrynus interlineatus-pleurostigma Populations (Anura: Microhylidae: Kalophryninae) and a Taxonomy of the Genus Kalophrynus Tschudi, Asian Sticky Frogs
FIGURE 3. Schematic depiction of the roof of the mouth of a Kalophrynus anya sp. nov., emphasizing the palatal folds. Only the basal portion of the tongue is shown, epiglottis and esophageal opening are not shown, and lower jaw is foreshortened.
Figure 3 in Population attributes of Littoraria angulifera (Gastropoda: Littorinidae) in mangroves in Bahia State, northeastern Brazil
Figure 3. Total specimens of Littoraria angulifera collected monthly throughout 2018 on the grass Spartina alterniflora in a mangrove (M1) in Ilhéus, Bahia State, northeastern Brazil, distributed by size classes (shell height), being: C1 (less than 2.99 mm), C2 (3-5.9 mm), C3 (6-8.99 mm), C4 (9-11.99 mm), C5 (12-14.99 mm), C6 (15-17.99 mm) and C7 (18-20.99 mm); A-L: January to December.
Figure 1 in Population attributes of Littoraria angulifera (Gastropoda: Littorinidae) in mangroves in Bahia State, northeastern Brazil
Figure 1. Map of northeastern Brazil showing the location of the Bahia State and the sampling stations (M1 and M2).
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Allen Brain Atlas
Allen Brain Atlas is an Allen Institute collection of brain map atlases, datasets, APIs, and analysis tools covering mouse, human, and non-human primate brain resources.
Annotated Behaviour and Observability Dataset (ABODe)
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DANDI Archive for NWB datasets
DANDI is a BRAIN Initiative archive for publishing and sharing neurophysiology data, including electrophysiology, optophysiology, and behavioral data packaged as NWB and related standards.
International Brain Laboratory public data
The International Brain Laboratory public data releases expose standardized mouse decision-making experiments, including Neuropixels recordings, widefield calcium imaging, behavior, and session metadata accessed through the ONE API.
OpenNeuro
OpenNeuro is a free, open platform for sharing neuroimaging datasets, with public search, dataset pages, and download paths for web, S3, DataLad, and the OpenNeuro CLI.