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7,849 results for “Conservancy”
Fig. 2 in Assessing the population of grey peacock-pheasant (Polyplectron bicalcaratum) in a Southeast Asian conservation landscape
Fig. 2. Histograms of perpendicular distances of ungrouped grey peacock-pheasant detections and estimated detection functions derived from DISTANCE software for line transects: (A1) not truncated (A2) truncated by eye at 90 m
Fig. 1 in Assessing the population of grey peacock-pheasant (Polyplectron bicalcaratum) in a Southeast Asian conservation landscape
Fig. 1. Location of line and point transect, listening posts for triangulation, and area searched for display scrapes to spot mapping, Huai Kha Khaeng Wildlife Sanctuary, Uthai Thani,Thailand
Fig. 4 in Assessing the population of grey peacock-pheasant (Polyplectron bicalcaratum) in a Southeast Asian conservation landscape
Fig. 4. The estimated density and standard error of Grey Peacockpheasant by four survey techniques in the 1200 × 1200 m study area at Huai Kha Khaeng Wildlife Sanctuary, Uthai Thani, Thailand
Fig. 6 in Activity budget, travel distance, sleeping time, height of activity and travel order of wild East Bornean Grey gibbons (Hylobates funereus) in Danum Valley Conservation Area
Fig. 6. Average daily travel distance and average sleeping time of the JACUZZI male for May–June (dry season) and December (wet season) from 2011 to 2013. Travel distance was counted for 13 days in August and for 13 days in December. Sleeping time was counted for 14 days in August and for 15 days in December. Solid line: travel distance. Dotted line: sleeping time.
Fig. 3 in Activity budget, travel distance, sleeping time, height of activity and travel order of wild East Bornean Grey gibbons (Hylobates funereus) in Danum Valley Conservation Area
Fig. 3. Activity budget of the SAPA male in both wet season (December) and dry season (August) from 2005 to 2008.
Fig. 2 in Activity budget, travel distance, sleeping time, height of activity and travel order of wild East Bornean Grey gibbons (Hylobates funereus) in Danum Valley Conservation Area
Fig. 2. Location of the BRL, the territory of the SAPA group and the territory of the JACUZZI group. The grey area represents the territory.
Fig. 1 in Activity budget, travel distance, sleeping time, height of activity and travel order of wild East Bornean Grey gibbons (Hylobates funereus) in Danum Valley Conservation Area
Fig. 1. Location of the Borneo Rainforest Lodge (BRL) in the Danum Valley Conservation Area (DVCA; arrow), Sabah, Malaysia.
Fig. 5 in Activity budget, travel distance, sleeping time, height of activity and travel order of wild East Bornean Grey gibbons (Hylobates funereus) in Danum Valley Conservation Area
Fig. 5. Average daily travel distance and average sleeping time of the SAPA male for August (dry season) and December (wet season) from 2003 to 2008. Travel distance was counted for 38 days in August and for 35 days in December. Sleeping time was counted for 39 days in August and for 37 days in December. Solid line: travel distance. Dotted line: sleeping time.
Fig. 4 in Activity budget, travel distance, sleeping time, height of activity and travel order of wild East Bornean Grey gibbons (Hylobates funereus) in Danum Valley Conservation Area
Fig. 4. Activity budget of the JACUZZI male and the JACUZZI female in both wet season (December) and dry season (May–June) from 2011 to 2013.
Fig. 8 in Activity budget, travel distance, sleeping time, height of activity and travel order of wild East Bornean Grey gibbons (Hylobates funereus) in Danum Valley Conservation Area
Fig. 8. Heights of diurnal activity of three gibbons (two males and one female) from 0530–1600 hours.
Fig. 2 in Ecological factors that influence sambar (Rusa unicolor) distribution and abundance in western Thailand: implications for tiger conservation
Fig. 2 The distribution of elevations at which transects were placed (a). The distribution of distances from the Huai Kha Khaeng River (HKK) at which transects were placed (b). The combinations of elevation and distance to HKK River at which pellet groups were found (each dot represents a single transect) (c). The number of pellet groups found in relation to distance from the HKK River at three elevations (where dots represents transects) (d). Dots represent transects and lines represent the predicted number of pellet groups using our top-supported model (Table 2, model 1) solved at mean covariate values and one of three elevations to illustrate the interaction of elevation with distance to the HKK River.
Fig.1 in Ecological factors that influence sambar (Rusa unicolor) distribution and abundance in western Thailand: implications for tiger conservation
Fig.1 Location of Huai Khaeng Wildlife Sanctuary in western Thailand and the 360 sampling units contained within the four areas represent six female tiger home ranges.
Figures 33–41. Polyphylla uteana Tanner. 33–36 in Natural history, ecology, and conservation of the genus Polyphylla Harris, 1841. 1. New species from the southwestern United States and Baja California, Mexico, with notes on distribution and synonymy (Coleoptera: Scarabaeidae: Melolonthinae)
Figures 33–41. Polyphylla uteana Tanner. 33–36) Holotype male. 37) Holotype labels. 38–40) Male variation. 41) Female.
Figures 28–32. Polyphylla avittata 28 in Natural history, ecology, and conservation of the genus Polyphylla Harris, 1841. 1. New species from the southwestern United States and Baja California, Mexico, with notes on distribution and synonymy (Coleoptera: Scarabaeidae: Melolonthinae)
Figures 28–32. Polyphylla avittata 28) Distribution of P. avittata Hardy and Andrews (solid circles) and P. uteana Tanner (black vertical lines). 29–32) Variation of male. 29) Hurricane Sand Dunes, Washington Co., UT (topotype). 30) Goblin Valley State Park, Emory Co., UT. 31) Grand Staircase- Escalante National Monument, Garfield Co., UT. 32) 3 miles N of Moab, Grand Co., UT.
Figures 48–49. Polyphylla. Males. 48 in Natural history, ecology, and conservation of the genus Polyphylla Harris, 1841. 1. New species from the southwestern United States and Baja California, Mexico, with notes on distribution and synonymy (Coleoptera: Scarabaeidae: Melolonthinae)
Figures 48–49. Polyphylla. Males. 48) Polyphylla mescalerensis Young [topotype]. Mescalero Sand Dunes, Chaves County, New Mexico. 49) Polyphylla sp. incertae. Cerro San Luis, Chihuahua, Mexico.
Figures 50–57. Habitats. 50–51 in Natural history, ecology, and conservation of the genus Polyphylla Harris, 1841. 1. New species from the southwestern United States and Baja California, Mexico, with notes on distribution and synonymy (Coleoptera: Scarabaeidae: Melolonthinae)
Figures 50–57. Habitats. 50–51) Polyphylla anivallis. Animas Valley Sand Dunes, Hidalgo Co., NM. 52–53) Polyphylla koso. Coso Mountains, Inyo Co., CA. 52) Coso Bridge. 53) Mill Springs Canyon. 54–55) Polyphylla morroensis. Baywood Fine Sands, San Luis Obispo Co., CA. 56–57) Polyphylla socorriana. El Socorro Sand Dunes, Baja California, MX.
Figures 42–47 in Natural history, ecology, and conservation of the genus Polyphylla Harris, 1841. 1. New species from the southwestern United States and Baja California, Mexico, with notes on distribution and synonymy (Coleoptera: Scarabaeidae: Melolonthinae)
Figures 42–47. Described females and comparative male. Polyphylla monahansensis Hardy and Andrews. 42) Male. 43–44) Female. Polyphylla stellata Young. 45) Male. 46–47) Female.
Fig. 4 in Conservation importance of Nakai-Nam Theun National Protected Area, Laos, for small carnivores based on camera trap data
Fig. 4. Distribution of camera-trap records for Mustelidea and Herpestidea in Nakai-Nam Theun NPA from 2006–2011.
Fig. 3 in Conservation importance of Nakai-Nam Theun National Protected Area, Laos, for small carnivores based on camera trap data
Fig. 3. Distribution of camera-trap records for Viverridae and linsang in Nakai-Nam Theun NPA from 2006–2011.
Fig. 2 in Conservation importance of Nakai-Nam Theun National Protected Area, Laos, for small carnivores based on camera trap data
Fig. 2. Total survey effort (in camera trap days) per month over the 2006–2011 survey period (bars) and relative species encounter rate (i.e., total independent photos of small carnivore spp./total camera trap day for the month). Relative encounter rates were highest during the warmest and well-surveyed months—peaks are observed in March (start of the warm season) and October (still within the warm season). Despite high survey effort in January and December (cold season), encounter rates were low.
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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.