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Fig. 2 in The herpetofauna of Bicuar National Park and surroundings, southwestern Angola: a preliminary checklist
Fig. 2. Left: Bicuar National Park (BNP) and surveyed sites from historical and recent records. Right: Angola with provincial boundaries and location of BNP. Source of satellite image: Maxar (https://www.digitalglobe.com/).
Fig. 1 in The herpetofauna of Bicuar National Park and surroundings, southwestern Angola: a preliminary checklist
Fig. 1. Habitat types in the study area. (A) Angolan Miombo woodland on Kalahari sands, BNP; (B) Burkea/Baikiaea woodlands, Carmira Farm; (C) dry grassy wetland ("mulola") flanked by miombo woodlands ("tunda"), BNP; (D) temporary pan in a "mulola," BNP.
Fig. 5 in Abundance and microhabitat use of the Endangered toad Rhinella yanachaga (Anura: Bufonidae) in the cloud forest of Yanachaga Chemillén National Park, Peru
Fig. 5. Comparisons of the sizes of Rhinella yanachaga individuals. (A) Differences in size of females in dry and wet seasons. (B) Differences in size of males in dry and wet seasons. (C) Differences in size between males and females. (D) Differences in the size of individuals with respect to microhabitats. The different letters indicate significant differences at p ≤ 0.05 according to the Tukey test after GLMM. Error bars represent standard errors.
Fig. 4 in Abundance and microhabitat use of the Endangered toad Rhinella yanachaga (Anura: Bufonidae) in the cloud forest of Yanachaga Chemillén National Park, Peru
Fig. 4. Correlations between the elevation and size of Rhinella yanachaga according to sex. The model presents correlation factors of r2 = 0.34; p = 0.01 for females and r2 = 0.003; p = 0.41 for males. The colors indicate sex (blue for males and red for females) and the shaded areas indicate the 95% confidence limits.
Fig. 2 in Abundance and microhabitat use of the Endangered toad Rhinella yanachaga (Anura: Bufonidae) in the cloud forest of Yanachaga Chemillén National Park, Peru
Fig. 2. Number of Rhinella yanachaga individuals per transect, T1 = 2,800–2,700 m, T2 = 2,700–2,600 m, T3 = 2,600–2,500 m, and T4 = 2,500–2,400 m, according to the elevation gradient for both sexes, in (A) dry season and (B) wet season. (C) Correlation between the abundance of Rhinella yanachaga and elevation for both sexes and seasons. The grey band indicates the 95% confidence limits.
Fig. 3 in Abundance and microhabitat use of the Endangered toad Rhinella yanachaga (Anura: Bufonidae) in the cloud forest of Yanachaga Chemillén National Park, Peru
Fig. 3. Numbers of individuals according to sex and length (SVL) ranges of Rhinella yanachaga in four transects, T1 = 2,800–2,700 m, T2 = 2,700–2,600 m, T3 = 2,600–2,500 m, and T4 = 2,500–2,400 m, according to the elevation gradient in the wet and dry seasons.
Fig. 1 in Abundance and microhabitat use of the Endangered toad Rhinella yanachaga (Anura: Bufonidae) in the cloud forest of Yanachaga Chemillén National Park, Peru
Fig. 1. (A) Map of the study area. The white circle indicates the location of the study site (San Alberto) within Yanachaga-Chemillén National Park, Oxapampa, Pasco; (B) lateral view, (C) ventral view, and (D) dorsal view of Rhinella yanachaga in life. Map by Vladimir Camel (A), photos by Shirley Huamán-Trucios (B–D).
Fig. 6 in Herpetofauna diversity in Zamrud National Park, Indonesia: baseline checklist for a Sumatra peat swamp forest ecosystem
Fig. 6. Photos of specimen of Lygosoma samajaya Karin, Freitas, Shonleben, Grismer, Bauer, and Das, 2018 encountered in Zamrud National Park, Riau, Indonesia.
Fig. 4 in Herpetofauna diversity in Zamrud National Park, Indonesia: baseline checklist for a Sumatra peat swamp forest ecosystem
Fig. 4. Species accumulation curve illustrates the accumulation of the encountered species during the 15 days of field sampling.
Fig. 3 in Herpetofauna diversity in Zamrud National Park, Indonesia: baseline checklist for a Sumatra peat swamp forest ecosystem
Fig. 3. Eight of the 33 species found in this survey. (A) Limnonectes malesianus; (B) Leptobrachium nigrops; (C) Chalcorana parvaccola; (D) Pulchrana rawa; (E) Gonocephalus liogaster; (F) Cyrtodactylus majulah; (G) Cuora amboinensis; (H) Tropidolaemus wagleri.
Fig. 3 in A novel intermediate host for Taenia serialis (Gervais, 1847): The European roe deer (Capreolus capreolus L. 1758) from the Monti Sibillini National Park (MSNP), Italy
Fig. 3. Phylogenetic relationships between two species of Taenia (T. serialis and T. multiceps) and the sample obtained for this study (sample from roe deer).
Fig. 1. Microscope view 100 in A novel intermediate host for Taenia serialis (Gervais, 1847): The European roe deer (Capreolus capreolus L. 1758) from the Monti Sibillini National Park (MSNP), Italy
Fig. 1. Microscope view 100 magnifications of the scolex collected from one of the cysts recovered in a wild European roe deer.
Fig. 2 in A novel intermediate host for Taenia serialis (Gervais, 1847): The European roe deer (Capreolus capreolus L. 1758) from the Monti Sibillini National Park (MSNP), Italy
Fig. 2. Note the meningeal vessels' congestion and the suppurative exudate covering the meningeal surface.
Fig. 2 in Epidemiology of Anaplasma marginale and Anaplasma centrale infections in African buffalo (Syncerus caffer) from Kruger National Park, South Africa
Fig. 2. Individual value plots showing the distribution of results for intensity of infection (log-transformed number of copies/reaction) with Anaplasma marginale (a) and Anaplasma centrale (b), using a real-time qPCR from a managed African buffalo (Syncerus caffer) herd from Kruger National Park, South Africa. Error bars represent one standard error, numbers at the top of figure represent sample size.
Fig. 1 in Epidemiology of Anaplasma marginale and Anaplasma centrale infections in African buffalo (Syncerus caffer) from Kruger National Park, South Africa
Fig. 1. The proportion of animals infected with Anaplasma spp. from a managed African buffalo (Syncerus caffer) herd from Kruger National Park, South Africa. a) The mean prevalence of animals with A. marginale single infection, A. centrale single infection, or co-infections with each other over four age groups: calves (0–1 years old), sub-adults (1–5.5 years old), adults (5.5–15 years) and geriatrics (15 years plus); b) the mean prevalence of new infections with A. marginale or A. centrale for each capture event over the two-and-a-half-year study period. Numbers at the top of figure represent sample size.
Fig. 3 in Epidemiology of Anaplasma marginale and Anaplasma centrale infections in African buffalo (Syncerus caffer) from Kruger National Park, South Africa
Fig. 3. Patterns of infection with Anaplasma spp. based on age and sex for a managed African buffalo (Syncerus caffer) herd from Kruger National Park, South Africa. a) The infection intensity (log-transformed number of copies/reaction) of A. marginale and A. centrale based on age (years); b) overall proportion of animals infected with A. marginale or A. centrale based on sex; c) infection intensity (log-transformed number of copies/reaction) results for A. marginale or A. centrale based on sex. * indicates statistical significance (p <0.05). Error bars are standard error.
Figure 5 in Diversity, distribution, and conservation of millipedes (Myriapoda: Diplopoda) in the Douala-Edéa National Park, Littoral Region of Cameroon
Figure 5. Cluster analysis based on Bray-Curtis index, showing dissimilarity between the different millipede communities in Douala-Edéa National Park.
Figure 4 in Diversity, distribution, and conservation of millipedes (Myriapoda: Diplopoda) in the Douala-Edéa National Park, Littoral Region of Cameroon
Figure 4. Non-Metric Multi-Dimensional Scaling (NMDS) of millipede faunal composition found in five Vegetation types in the Douala-Edéa National Park. Habitat codes are AF = Agroforest, MF = Mangrove forest, PF = Primary forest, OM = Open meadows, SF = Secondary forest.
Figure 3 in Diversity, distribution, and conservation of millipedes (Myriapoda: Diplopoda) in the Douala-Edéa National Park, Littoral Region of Cameroon
Figure 3. Millipede species richness of the different families by habitat types in Douala-Edéa National Park.
Figure 6 in Diversity, distribution, and conservation of millipedes (Myriapoda: Diplopoda) in the Douala-Edéa National Park, Littoral Region of Cameroon
Figure 6. The abundance distribution model of millipede species in the different habitat in Douala-Edéa National Park.
ScienceDex guides
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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.