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8,729 results for “Ranges”
Fig. 15 in Revision of the Andrena (Micrandrena) tiaretta group: redescription of A. tiaretta WARNCKE, 1974 and description of two new species (A. cyrenaica nov.sp. and A. orientalis nov.sp.) demarcating the central and eastern part of the range (Libya, Israel, Syria)
Fig. 15: Andrena tiaretta s.str. (male) from Algeria, OLML 112. Fig. 16: A. orientalis nov.sp. (male) from Israel, OLML 125. (a) dorsal view; (b) labels. Fig. 17: A. cyrenaica nov.sp. (male) from Lybia, OLML 128. (a) dorsal view; (b) labels. All specimens deposited in the 'Biology Centre of the Upper Austrian Provincial Museum Linz' (Austria). Photos L. Haitzinger.
Fig. 7 in Revision of the Andrena (Micrandrena) tiaretta group: redescription of A. tiaretta WARNCKE, 1974 and description of two new species (A. cyrenaica nov.sp. and A. orientalis nov.sp.) demarcating the central and eastern part of the range (Libya, Israel, Syria)
Fig. 7: Andrena tiaretta s.str. (female) from Morocco, OLML 110; Fig. 8: A. orientalis nov.sp. (female) from Israel, OLML 116; Fig. 9: A. cyrenaica nov.sp. (female) from Lybia, OLML 120; (a) tibia, metatarsus, tarsi 2, 3, tibial scopa; (b) dorsal view mesoscutum. Photos L. Haitzinger.
Fig. 4 in Revision of the Andrena (Micrandrena) tiaretta group: redescription of A. tiaretta WARNCKE, 1974 and description of two new species (A. cyrenaica nov.sp. and A. orientalis nov.sp.) demarcating the central and eastern part of the range (Libya, Israel, Syria)
Fig. 4: Andrena tiaretta s.str. (female) from Morocco, OLML 110; Fig. 5: A. orientalis nov.sp. (female) from Israel, OLML 116; Fig. 6: A. cyrenaica nov.sp. (female) from Lybia, OLML 120; (a) head frontal view; (b) dorsal view mesoscutum, scutellum, postscutellum, propodeum. Photos L. Haitzinger.
Fig. 1 in Revision of the Andrena (Micrandrena) tiaretta group: redescription of A. tiaretta WARNCKE, 1974 and description of two new species (A. cyrenaica nov.sp. and A. orientalis nov.sp.) demarcating the central and eastern part of the range (Libya, Israel, Syria)
Fig. 1: Andrena tiaretta s.str. (female) from Morocco, OLML 110. Fig. 2: A. orientalis nov.sp. (female) from Israel, OLML 116. (a) dorsal view; (b) labels. Fig. 3: A. cyrenaica nov.sp. (female) from Lybia, OLML 120. (a) dorsal view; (b) labels. All specimens deposited in the 'Biology Centre of the Upper Austrian Provincial Museum Linz' (Austria). Photos L. Haitzinger.
Fig. 1 in Home range size and microhabitat selection by a tropical partridge species in moist evergreen forest
Fig. 1. Analysis of green-legged partridges' group range based on radio locations using the characteristic hull polygon (CHP) and minimum convex polygon (MCP; 100%, 95% and 50%) methods. F refers to females, and M refers to males.
Fig. 2 in Home range, habitat use and roost-site selection by lowland female Siamese fireback Lophura diardi in northeastern Thailand
Fig. 2. The variation in home ranges and core areas of the eight female Siamese fireback in 2011 during different reproductive periods, estimated using 95% MCP and CHP Hot Spot methods. Locations shown were the food supplement sites (1 and 2) and nesting sites during the breeding season.
Fig. 3 in Home range, habitat use and roost-site selection by lowland female Siamese fireback Lophura diardi in northeastern Thailand
Fig. 3. The occurrence probability of Siamese fireback in relation to habitat variables. Shown are predicted values and 95% confidence limits for breeding (black solid lines) and non-breeding (gray dashed lines) periods.
Fig. 1 in Home range, habitat use and roost-site selection by lowland female Siamese fireback Lophura diardi in northeastern Thailand
Fig. 1. Location of Sakaerat Environmental Research Station (SERS), northeastern Thailand, including the locations of 60 available sites, two food supplementary sites, 14 nesting sites, and 52 roosting sites. Polygons shown are the home range boundaries of the eight radiotagged Siamese firebacks (group A–H).
Fig. 2 in Exploring potential range connectivity of sun bear (Carnivora: Ursidae: Ursinae)
Fig. 2. Frequency plots of land type values from the Terrestrial Ecosystem Environment Observation by Satellites (TREES; Stigbig et al., 2003). TREES land type values were calculated to 20,000 random points generated equally between non-habitat, marginal, sub-optimal, and core habitat. Land type was reclassified into 12 categories; 1–8 are categories in which bear use has been previously detected (1–3 = evergreen; 4 = deciduous, woodland; 5 = mangrove; 6 = swamp, woodland; 7–8 = mosaic of woodland, secondary, evergreen and cropland), and 9–12 are considered non-habitat (9 = cropland, shrub; 10 = cropland, bare land; 11 = rock, limestone; 12 = water). To correct for errors on the TREES map due to deforestation since 2000, % tree cover in 2014 was extracted for each random point, and points with no tree cover in 2014 reclassified as falling in non-viable habitat. TREES land classification values within non-habitat were more often classified as areas considered as non-viable bear habitat (i.e., cropland, shrub, bare land, rock). Second to non-habitat, marginal habitat had the highest proportion of points within non-viable bear habitat categories. In sub-optimal and core habitat, land classification tended to be areas of potential bear habitat (i.e., evergreen, deciduous forest, and other forms of mosaic forest).
Fig. 1 in Exploring potential range connectivity of sun bear (Carnivora: Ursidae: Ursinae)
Fig. 1. Density plots of Human Influence Index values within areas classified as habitat and non-habitat within sun bear range. Human Influence Index values (Sanderson et al., 2002) were calculated to 30,000 random points generated equally within areas of non-habitat and habitat. Human Influence Index values were on average 13.8 points higher in areas classified as non-habitat (t = –95.2, df = 29658, p <0.001, x – within non-habitat = 36.7, SD = 13.1, x – within habitat = 23, SD = 11.8) supporting our assumption that habitat is different from non-habitat.
Fig. 3 in Exploring potential range connectivity of sun bear (Carnivora: Ursidae: Ursinae)
Fig. 3. Sun bear landscape fragmentation and connectivity in Southeast Asia, India and Bangladesh. A) Core and sub-optimal contiguous range is assumed to positively impact bear movement (i.e., connectivity), although dependent on associated levels of human influence and roads. Visual analysis identified seven potential subpopulations of sun bears; i) northern Mainland, ii) Central Myanmar, iii) Central SE Asia, iv) South-central SE Asia, v) Thai-Malay peninsula, vi) Sumatra, vii) Borneo (divided by dashed lines). Within these potential subpopulations there were many 'At Risk' areas where sun bears may be vulnerable to becoming isolated due to potential barriers to movement including habitat fragmentation, high human influence and roads (identified by red ovals and numbers 1–16 correspond with the IDs listed in Table 2). B) High Human Influence and road network are assumed to be significant barriers to bear movement across the sun bear landscape.
Fig. 1 in Preliminary estimation of home range size for Meristogenys orphnocnemis, a common Bornean Ranid, in an altered forest ecosystem using radiotelemetry
Fig. 1. Section of stream in SAFE Project experimental site, known as logged forest edge (LFE) stream, where all radiotracking occurred.
Fig. 6 in A new landhopper genus and species (Crustacea: Amphipoda: Talitridae) from Annamite Range, Vietnam
Fig. 6. Solitroides motokawai, new genus & species, holotype (VNMN 2017.01). A, uropod 1, lateral view; B, uropod 2, ventral view; C, uropod 3, dorsal view; D, telson, dorsal view. Scale bars = 0.5 mm [A, B]; 0.1 mm [C, D].
Fig. 5 in A new landhopper genus and species (Crustacea: Amphipoda: Talitridae) from Annamite Range, Vietnam
Fig. 5. Solitroides motokawai, new genus & species, holotype (VNMN 2017.01). A, coxal gill of gnathopod 2, lateral view; B, coxal gill of pereopod 3, lateral view; C, coxal gill of pereopod 4, lateral view; D, coxal gill of pereopod 5, lateral view; E, coxal gill of pereopod 6, lateral view; F, oostegite of gnathopod 2, lateral view; G, oostegite of pereopod 3, lateral view; H, oostegite of pereopod 4, lateral view; I, oostegite of pereopod 5, lateral view; J, epimeral plate 1, lateral view; K, epimeral plate 2, lateral view; L, epimeral plate 3, lateral view; M, pleopod 1, posterior view; N, pleopod 2, posterior view; O, pleopod 3, posterior view. Scale bars = 0.5 mm [A–L]; 0.1 mm [M–O].
Fig. 1 in A new landhopper genus and species (Crustacea: Amphipoda: Talitridae) from Annamite Range, Vietnam
Fig. 1. Solitroides motokawai, new genus & species, holotype (VNMN 2017.01), lateral view. Scale bar = 1 mm.
Fig. 7 in A new landhopper genus and species (Crustacea: Amphipoda: Talitridae) from Annamite Range, Vietnam
Fig. 7. Scanning electron micrographs of Solitroides motokawai, new genus & species, paratype (KUZ Z1865). A, maxilliped, ventral view; B, distal part of maxilliped palp, arrowhead indicates boundary between articles 3 and 4, ventral view. Scale bars = 100 µm [A]; 50µm [B].
Fig. 3 in A new landhopper genus and species (Crustacea: Amphipoda: Talitridae) from Annamite Range, Vietnam
Fig. 3. Solitroides motokawai, new genus & species, holotype (VNMN 2017.01). A, maxilliped, dorsal view; B, gnathopod 1, lateral view; C, gnathopod 2, lateral view; D, pereopod 3, lateral view; E, dactylus of pereopod 3. Scale bars = 0.1 mm [A, E]; 0.5 mm [B–D].
Fig. 4 in A new landhopper genus and species (Crustacea: Amphipoda: Talitridae) from Annamite Range, Vietnam
Fig. 4. Solitroides motokawai, new genus & species, holotype (VNMN 2017.01). A, pereopod 4, medial view; B, dactylus of pereopod 4, medial view; C, pereopod 5, medial view; D, dactylus of pereopod 5, medial view; E, pereopod 6, medial view; F, dactylus of pereopod 6, medial view; G, pereopod 7, lateral view; H, dactylus of pereopod 7, lateral view. Scale bars = 1.0 mm [A, C, E, G]; 0.1 mm [B, D, F, H].
Fig. 2 in A new landhopper genus and species (Crustacea: Amphipoda: Talitridae) from Annamite Range, Vietnam
Fig. 2. Solitroides motokawai, new genus & species, holotype (VNMN 2017.01). A, head, lateral view; B, antenna 1, lateral view; C, antenna 2, lateral view; D, upper lip, anterior view; E, left mandible, medial view; F, right mandible, lateral view; G, lower lip, ventral view; H, maxilla 1, dorsal view; I, maxilla 2, dorsal view. Scale bars = 0.5 mm [A–C, G]; 0.1 mm [D–F, H, I].
Fig. 2 in Distribution range and extinction risk of tree snail subgenus Amphidromus (Pulmonata: Camaenidae) in Thailand
Fig. 2. Locations of Amphidromus (Amphidromus) records from literature. Open circles show reported locations of Amphidromus.
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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)
ABODe is a University of Edinburgh DataShare dataset for behavior classification in group-housed mice using home-cage video, identities, bounding boxes, ground-plate positions, and annotator labels.
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.