Find research datasets worth reusing
Search datasets from major research repositories and use ShareScore to quickly assess how well each record supports discovery, access, and reuse.
549
datasets available to search
ShareScore release 0.9.0
Dataset results
549 results for “habitat‐use”
Fig. 7 in Habitat use and site fidelity of Irrawaddy dolphins (Orcaella brevirostris) in the coastal waters of Bago-Pulupandan, Negros Occidental, Philippines
Fig. 7. Activity Index showing proportion of each behavioural activity (foraging; socialising; traveling; resting) per sector.
Fig. 8 in Habitat use and site fidelity of Irrawaddy dolphins (Orcaella brevirostris) in the coastal waters of Bago-Pulupandan, Negros Occidental, Philippines
Fig. 8. Monthly (N=25) and yearly (N=8) sighting rate (please see Material and Methods) for 19 identified Irrawaddy dolphins from Bago-Pulupandan (includes entire period of the sightings of these identified dolphins).
Fig. 3 in Habitat use and site fidelity of Irrawaddy dolphins (Orcaella brevirostris) in the coastal waters of Bago-Pulupandan, Negros Occidental, Philippines
Fig. 3. Discovery curve of marked individual dolphins in the study area over 25 survey months from 2010 to 2016.
Fig. 1 in Habitat use and site fidelity of Irrawaddy dolphins (Orcaella brevirostris) in the coastal waters of Bago-Pulupandan, Negros Occidental, Philippines
Fig. 1. Coastal waters of Bago City and the Municipality of Pulupandan in Guimaras Strait; Left inset: location of Western Visayas Region in the Philippines; Right inset: Guimaras Strait located between Negros Island and Guimaras Island.
Fig. 4. A in Habitat use and site fidelity of Irrawaddy dolphins (Orcaella brevirostris) in the coastal waters of Bago-Pulupandan, Negros Occidental, Philippines
Fig. 4. A, sightings of Irrawaddy dolphins (in yellow dots) relative to sectors; B, minimum convex polygon (MCP) of all sightings in Bago-Pulupandan coastal waters.
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).
Figure 1 in Variables Affecting Habitat Use Of Hume'S Pheasant In Two Disturbed Sites In Northern Thailand
Figure 1. Map showing the locations of Doi Chiang Dao and Mae- Lao Mae-Sae Wildlife Sanctuaries and Doi Khun Mae Daet located in northern Thailand.
Fig. 3. Land use and land cover data for 2014 in Population trends and conservation status of proboscis monkeys (Nasalis larvatus) in the face of habitat change in the Klias Peninsula, Sabah, Borneo, Malaysia
Fig. 3. Land use and land cover data for 2014/2015 within the 1-km buffer distance from surveyed rivers, overlaid with proboscis monkey sightings from the 2004/2005 and 2014 surveys, Protected Areas, and Production Forest Reserve boundaries.
Fig. 2 in Comparative feeding ecology and habitats use of Crenicichla species (Perciformes: Cichlidae) in a Venezuelan floodplain river
Fig. 2. Map showing location of the Cinaruco River, a tributary of the Orinoco River in Venezuela's Apure State; the study reach is outlined with a rectangle.
Fig. 4 in Comparative feeding ecology and habitats use of Crenicichla species (Perciformes: Cichlidae) in a Venezuelan floodplain river
Fig. 4. Number of immature and mature gonads encountered in C. lugubris (a) and C. aff. wallacii (b) of different size classes during the dry season. (black barra) Mature (gonad state> 3); (white barra) immature (gonad state 1-2). C. lugubris (n = 102), C. aff. wallacii (n = 108).
Fig. 8 in Habitat use and behaviour of the Irrawaddy dolphin, Orcaella brevirostris and the Indo-Pacific finless porpoise, Neophocaena phocaenoides off the west coast of Penang Island, Malaysia
Fig. 8. Mean activity index (AI) of Irrawaddy dolphins and finless porpoises for each quadrat in the west Penang Island study.
Fig. 6 in Habitat use and behaviour of the Irrawaddy dolphin, Orcaella brevirostris and the Indo-Pacific finless porpoise, Neophocaena phocaenoides off the west coast of Penang Island, Malaysia
Fig. 6. Coefficient of Area Use (AU) for both species in west Penang Island. A, AU for the Irrawaddy dolphin, B, AU for the finless porpoise and C, combination and overlap of area use for both Irrawaddy dolphin and finless porpoise
Fig. 2 in Habitat use and behaviour of the Irrawaddy dolphin, Orcaella brevirostris and the Indo-Pacific finless porpoise, Neophocaena phocaenoides off the west coast of Penang Island, Malaysia
Fig. 2. Two survey routes where the research boat travelled, consisting of a parallel line route and a zig–zag route in west Penang
Fig. 3 in Habitat use and behaviour of the Irrawaddy dolphin, Orcaella brevirostris and the Indo-Pacific finless porpoise, Neophocaena phocaenoides off the west coast of Penang Island, Malaysia
Fig. 3. Cetacean encounters in the western coastal waters of Penang Island (February 2019–April 2021) during on-effort surveys. A, Irrawaddy dolphin group size; and B, finless porpoise group size.
Fig. 4 in Habitat use and behaviour of the Irrawaddy dolphin, Orcaella brevirostris and the Indo-Pacific finless porpoise, Neophocaena phocaenoides off the west coast of Penang Island, Malaysia
Fig. 4. Comparison of Irrawaddy dolphin and finless porpoise sightings across distance from the shore (km) and depth of water (m) in west Penang Island, Malaysia.
Species detection histories used in Killion et al. (2023): Integrating Spaceborne Estimates of Structural Diversity of Habitat into Wildlife Occupancy Models
<p>Camera trap species detection histories used for occupancy models in "Integrating Spaceborne Estimates of Structural Diversity of Habitat into Wildlife Occupancy Models". </p>
Data for: Drivers affecting habitat use in Afrotropical hipposiderid and pteropodid bats
<p>Assessing how bats respond to habitat attributes requires an integrative approach to reliably predict direct community-level effects. We focused on hipposiderid and pteropodid bats because of their diverse resource use patterns, body size ranges, and dispersal abilities. We combined an array of bat species-level characteristics with key rainforest stand characteristics that may covary with habitat use. Twelve stations were sampled in the Lomami and Yangambi landscapes in the Democratic Republic of the Congo. We investigated whether the species-level flight ability of bats and rainforest stand characteristics can affect bat commuting flights and community-level estimates of both species detection and habitat occupancy. We captured bats for 108 trap-nights. Three sampling events (early evening, middle of the night, and early morning) were replicated for each survey night. Hipposiderids showed an early evening flight peak, while flight activity of pteropodids was constant throughout the night, but increased around the middle of the night. Species capture probability decreased with higher wing loading in hipposiderids and was negatively correlated with higher wing aspect ratio in pteropodids. Forest occupancy of hipposiderids increased along the gradient towards waterways, while pteropodid occurrence was not directly linked to measured forest stand variables. This suggests a consequence of habitat patterns at larger spatial scales, which would need clarifying through additional data collection. We discuss these findings in terms of resource-use strategies of clutter-tolerant and clutter-intolerant species. We argue that the occurrence of specific bat species and their habitat use patterns can serve as surrogate measures of ecosystem health.</p>
Fig. 10. A in Small carnivores (Mammalia: Carnivora) in the Wonorejo Mangroves, Jawa Timur, Indonesia: habitat use and activity patterns
Fig. 10. A Sunda palm civet in Surabaya's Bratang wildlife market on 20 July 2018. Photograph: Angie Appel.
ScienceDex guides
Understand access before you commit
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.