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7,081 results for “Habitats”
Fig. 3 in Four new species of the subfamily Candoninae (Crustacea, Ostracoda) from freshwater habitats in Japan
Fig. 3. Pseudocandona becca sp. nov. A. Internal view of male left valve. B. Internal view of female left valve (LBM 1430006266). C. Male antennule (LBM 1430006264). D. Male antenna (LBM 1430006264). E. Detail of male antenna (LBM 1430006264). F. Detail of female antenna (LBM 1430006266). G. Female mandibular coxa (LBM 1430006267). Scale bar: A–B = 500 µm; C–D, G = 127 µm; E–F = 66 µm.
Fig. 4 in Four new species of the subfamily Candoninae (Crustacea, Ostracoda) from freshwater habitats in Japan
Fig. 4. Pseudocandona becca sp. nov. A. Female mandibular palp (LBM 1430006267). B. Alpha and beta setae of the mandibular palp (LBM 1430006267). C. Female maxillula (setae on endites not drawn) (LBM 1430006265). D–E. Left and right male fifth limb palps (LBM 1430006264). F. Female fifth limb (LBM 1430006265). G. Male sixth limb (LBM 1430006264). H. Male seventh limb (LBM 1430006264). Scale bar: A–C = 66 µm; D–H = 127 µm.
Fig. 16 in Four new species of the subfamily Candoninae (Crustacea, Ostracoda) from freshwater habitats in Japan
Fig. 16. Undulacandona colymba sp. nov. A. Female mandibular palp (LBM 1430006282). B. Alpha, beta and gamma setae of mandibular palp (LBM 1430006282). C. Female mandibular coxa (LBM 1430006282). D. Female maxillula (setae on endites not drawn) (LBM 1430006280). E–F. Left and right male fifth limb palps (LBM 1430006279). G. Female fifth limb (LBM 1430006282). H. Male sixth limb (LBM 1430006281). I. Female seventh limb (LBM 1430006280). Scale bar: A–B, D = 61 µm; C, E–I = 117 µm.
Fig. 8 in Four new species of the subfamily Candoninae (Crustacea, Ostracoda) from freshwater habitats in Japan
Fig. 8. Pseudocandona atmeta sp. nov. A. Internal view of male left valve (LBM 1430006270). B. Internal view of female left valve (LBM 1430006271). C. Male antennule (LBM 1430006270). D. Male antenna (LBM 1430006270). E. Detail of male antenna (LBM 1430006270). F. Detail of female antenna (LBM 1430006271). G. Male mandible (LBM 1430006270). Scale bar: A–B = 710 µm; C–D, G = 200 µm; E–F = 122 µm.
Fig. 2. A–E in Four new species of the subfamily Candoninae (Crustacea, Ostracoda) from freshwater habitats in Japan
Fig. 2. A–E. Pseudocandona becca sp. nov. A. Right view of male carapace (LBM 1430006268). B. Right view of female carapace (LBM 1430006269). C. Dorsal view of female carapace, anterior to left (LBM 1430006269). D. Internal view of female left valve (LBM 1430006269). E. Internal view of female right valve (LBM 1430006269). F–I. Pseudocandona atmeta sp. nov. F. Right view of male carapace (LBM 1430006272). G. Right view of female carapace (LBM 1430006273). H. Internal view of female left valve (LBM 1430006274). I. Internal view of female right valve (LBM 1430006274).
Figs 3–8. Live specimens and habitats. 3. Artema atlanta Walckenaer, 1837 from Thailand, Ratchaburi. 4–5. A in Daddy-long-leg giants: revision of the spider genus Artema Walckenaer, 1837 (Araneae, Pholcidae)
Figs 3–8. Live specimens and habitats. 3. Artema atlanta Walckenaer, 1837 from Thailand, Ratchaburi. 4–5. A. nephilit sp. nov. from Israel. 6. Typical Artema web mass, in a cave in Petra, Jordan. 7–8. Caves populated by Artema nephilit sp. nov.: Oren Cave, Mount Karmel (7) and caves in the Eilat Mountains (8), Israel. Photos: BAH (3–4, 6–8), SA (5).
Data from : Classifying wetland‐related land cover types and habitats using fine‐scale lidar metrics derived from country‐wide Airborne Laser Scanning
<p>This data repository contains the processed lidar metrics for characterizing the habitat structure for classifying main land cover and habitat types in the Lauwersmeer area in the northern part of the Netherlands in the province of Groningen (5754 ha). The lidar metrics were derived from Airborne Laser Scanning (ALS) data using the Actueel Hoogtebestand Nederland 2 (AHN2) openly available dataset from https://www.pdok.nl/. </p> <p>The derived lidar metrics saved in *.grd file format and contain 32 bands. Each band represents a lidar metric and the water surface was masked out in the dataset. The *l1* in the file name indicates that the file was used for level 1 (wetland) classification and *l23* used for level 2 (land cover types within wetland) and level 3 (reedbed habitats) classification. The lidar metrics were calculated using lidR (<a href="https://github.com/Jean-Romain/lidR">https://github.com/Jean-Romain/lidR</a>) software package. Further details related to the lidar metrics extraction can be found at <a href="https://github.com/eEcoLiDAR/PhDPaper1_Classifying_wetland_habitats">https://github.com/eEcoLiDAR/PhDPaper1_Classifying_wetland_habitats</a> Github repository.</p> <p> </p>
Least-cost habitat linkages for American black bear, Rafinesque's big-eared bat, and timber rattlesnake.
<p>This data set contains 3 shapefiles and associated files that map linkages, which are least-cost paths between adjacent habitat cores for three wildlife species in the Southeastern U.S. The species are: the American black bear (Ursus americanus), Rafinesque's big-eared bat (Corynorhinus rafinesquii), and Timber rattlesnake (Crotalus horridus). We mapped habitat cores based on c. 2006 land cover, then used LinkageMapper software to identify least-cost paths between them, and buffered the least-cost paths by 2.5 km using ArcGIS, for a total width of 5 km. The buffered least-cost paths are the linkages provided here. The attribute tables for these shapefiles contain fields that describe the importance of each linkage to the overall habitat connectivity network, contemporary and future average modeled habitat suitability within the linkage, change in average proportion suitable, percent of urban land within the linkage, percent of linkage that is protected for conservation, and categorical values for climate threat, whether the linkage was designated as highly important, protection status, and future urbanization threat.</p>
Figure 9 in Behaviour and habitat of Neohela monstrosa (Boeck, 1861) (Amphipoda: Corophiida) in Norwegian Sea deep water
Figure 9. Glacial eelpout (Lycodes frigidus) is often observed in the same habitat as dense populations of Neohela monstrosa and may represent an important predator from which the latter has to hide in its burrow.
Data from: Foraging behaviour and habitat-use drives niche segregation in sibling seabird species
<p>To mediate competition, similar sympatric species are assumed to utilise different resources, or the same but geographically separated resources. The two giant petrels (<em>Macronectes</em> spp.) are intriguing in that they are morphologically similar seabirds with overlapping diets and distributions. To better understand the mechanisms allowing their co-existence, we investigated intra- and interspecific niche segregation at Marion Island (Southern Indian Ocean), one of the few localities where they breed in sympatry. We used GPS tracks from 94 individuals and remote-sensed environmental data to quantify habitat-use, combined with blood carbon and nitrogen stable isotope ratios from 90 individuals to characterise their foraging habitat and trophic ecology. Females of both species made distant at sea foraging trips and fed at a similar trophic level. However, they used distinct pelagic habitats. In contrast, males of both species mainly foraged on or near land, resulting in significant sexual segregation, but high interspecific habitat and diet overlap. However, some males showed flexible behavioural strategies, also making distant, pelagic foraging trips. Using contemporaneous tracking, environmental and stable isotope data we provide a clear example of how sympatric sibling species can be segregated along different foraging behaviour dimensions.</p>
Figure 2 in Improved local inventory and regional contextualization for anuran (Amphibia) diversity assessment at an endangered habitat in southeastern Brazil
Figure 2. Rarefaction curves based on Jackknife I species-richness estimator for records of adults, tadpoles and all life stages pooled for four canga lakes at the Quadrilátero Ferrífero region, southeastern Brazil.
Figure 1 in Habitat and diet of Bhutan takin Budorcas taxicolor whitei during summer in Jigme Dorji National Park, Bhutan
Figure 1. Location of study area, Tsharijathang valley (black box), within Jigme Dorji National Park (shaded grey), north-western Bhutan.
Figure 3 in Investigating the influence of habitat type and weather conditions on the population dynamics of land snails Vertigo angustior Jeffreys, 1830 and Vertigo moulinsiana (Dupuy, 1849). A case study from western Poland
Figure 3. Diagram of one-way analysis of covariance test comparing a logarithmized number of individuals of Vertigo angustior (F = 92.16; p <0.01) and Vertigo moulinsiana (F = 8.165; p <0.01) in the Ilanka and Pliszka sites in 2009. Middle line: mean; box range: standard error; whiskers: standard deviation.
Figure 2 in Investigating the influence of habitat type and weather conditions on the population dynamics of land snails Vertigo angustior Jeffreys, 1830 and Vertigo moulinsiana (Dupuy, 1849). A case study from western Poland
Figure 2. Precipitation in the studied sites in consecutive months of 2009; dashed bars – sampling months. (B) and (C) Abundance of individuals: juveniles (white bars) and adults (black bars) of Vertigo angustior (B) and Vertigo moulinsiana (C) in each sampling event in the Ilanka and Pliszka sites in 2009.
Figure 1 in Conservation in a changing landscape: habitat occupancy of the critically endangered Tennent's leaf-nosed lizard (Ceratophora tennentii) in Sri Lanka
Figure 1. Location of Knuckles forest reserve within Kandy and Matale Districts (left) and the four study sites [two at Riverston (1 and 2), Hunasgiriya (3) and Deanston (4)] within the reserve (right).
Figure 3 in Conservation in a changing landscape: habitat occupancy of the critically endangered Tennent's leaf-nosed lizard (Ceratophora tennentii) in Sri Lanka
Figure 3. Comparison of climatic and structural parameters among the four habitat types during the dry (dashed line) and wet (solid line) seasons. Data from both locations with lizards and random locations are considered in combination. (C = Cardamom plantations, M = Mixed cardamom forests, N = Natural forests, P = Pine plantations.)
Figure 2 in Conservation in a changing landscape: habitat occupancy of the critically endangered Tennent's leaf-nosed lizard (Ceratophora tennentii) in Sri Lanka
Figure 2. Mean number of sightings of Ceratophora tennentii within three habitat types at Knuckles Range, Sri Lanka.
Figure 1 in Winter-active wolf spiders (Araneae: Lycosidae) in thermal habitats from western Romania
Figure 1. Map of the surveyed localities with thermal habitats in western Romania (1, Moneasa; 2, Ciocaia; 3, Roşiori; 4, Roşiori/Tămăşeu; 5, Săcuieni I; 6, Săcuieni II; 7, Curtici; 8, Socodor; 9, Chiribiş; 10, Chişlaz; 11, Livada de Bihor; 12, Mădăras; 13, Răbăgani; 14, Sânnicolau de Munte; 15, Tărian; 16, Acâş; 17, Beltiug; 18, Mihăieni; 19, Chiraleu; 20, Oradea; 21, Săcuieni III; 22, Tămăşeu; AR = Arad county, BH = Bihor county, SM = Satu Mare county).
Figure 1 in Home range and foraging habitat selection by breeding lesser kestrels (Falco naumanni) in Greece
Figure 1. Minimum convex polygon home ranges (outer: 100%, interior: 95% of locations) of male (A) and female (B) lesser kestrels during the breeding season in central Greece, 2008.
Figure 2. Summer core area delineation. The straight line with a in Demographic characteristics, seasonal range and habitat topography of Balkan chamois population in its southernmost limit of its distribution (Giona mountain, Greece)
Figure 2. Summer core area delineation. The straight line with a slope of –1 represents the random use of space within the population seasonal range. The curve that sags below the line of random use represents the clumped use of space. The summer core area can be defined at the point whose tangent has slope –1, e.g. 85%, that is, whose tangent is parallel to the line of random use. This is also the point of the curve that is furthest from the line of random use.
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These curated guides explain access requirements, typical timelines, costs, and reuse considerations for widely used research datasets.
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.