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Figure 4 in Does the location of coastal brackish waters determine diversity and abundance of zooplankton assemblages?
Figure 4. Seasonal (monthly) changes in the total zooplankton abundance (mean, minimum, and maximum densities) (ind. dm–3) in the Vistula Lagoon and Lake Łebsko in 2010–2011.
Figure 6 in Does the location of coastal brackish waters determine diversity and abundance of zooplankton assemblages?
Figure 6. Seasonal (monthly) changes in the total zooplankton biomass (mean, minimum, and maximum values) (mg. dm–3) in the Vistula Lagoon and Lake Łebsko in 2010–2011.
Figure 15 and 16. Two adults P. bicolor were observed near the location where P in New ecological information on the little-known Sumatran endemics Black-and-white langur Presbytis bicolor Aimi & Bakar, 1992 (Primates: Cercopithecidae)
Figure 15 and 16. Two adults P. bicolor were observed near the location where P. bicolor was fed by a Domestic dog, 8 December 2021, Sekernan Subdistrict, Muaro Jambi District, Jambi Province (Photo: Muhammad Iqbal).
Fig, 1. A map of Singapore and southern Johor showing the sites examined (Ο) and the locations where Brachidontes striatulus was collected (•) (locations 7a and 11). The locations are numbered in order of ascending salinity, except location 7a; 1: Sungei Mandai, 0‰; 2: West Coast, 1‰; 3, Sungei Danga, 2‰; 4, Kim Seng Canal, 2‰; 5, Sungei Sekudai, 5‰; 6, Sungei Serangoon, 9‰; 7, Siglap Canal, 10‰; 7a, Siglap Canal, 20‰; 8, Kallang River, 11‰; 9, Upper Rochor Canal, 12‰; 10, Kallang River, 13‰; 11, Lower Rochor Canal, 16‰; 12, Sungei Senibong, 17‰; 13, Whampoa/Kallang River junction, 19‰; 14, Rochor Canal mouth, 19‰; 15, Sungei Sembawang, 20‰; 16, Sungei Pandan, 22‰; 17, Sungei Plentong, 22‰; 18, Lim Chu Kang Road end, 24‰; 19, Sungei Simpang, 24‰; 20, Sembawang Park, 25‰; 21, Causeway, 25‰; 22, Kranji bund, 25‰; 23, Stulang Laut, 26‰; 24, West Coast Drain 2, 27‰; 25, Singapore River, 27‰. in Brachidontes Striatulus (Bivalvia Mytilidae) Introduced Into Singapore
Fig, 1. A map of Singapore and southern Johor showing the sites examined (Ο) and the locations where Brachidontes striatulus was collected (•) (locations 7a and 11). The locations are numbered in order of ascending salinity, except location 7a; 1: Sungei Mandai, 0‰; 2: West Coast, 1‰; 3, Sungei Danga, 2‰; 4, Kim Seng Canal, 2‰; 5, Sungei Sekudai, 5‰; 6, Sungei Serangoon, 9‰; 7, Siglap Canal, 10‰; 7a, Siglap Canal, 20‰; 8, Kallang River, 11‰; 9, Upper Rochor Canal, 12‰; 10, Kallang River, 13‰; 11, Lower Rochor Canal, 16‰; 12, Sungei Senibong, 17‰; 13, Whampoa/Kallang River junction, 19‰; 14, Rochor Canal mouth, 19‰; 15, Sungei Sembawang, 20‰; 16, Sungei Pandan, 22‰; 17, Sungei Plentong, 22‰; 18, Lim Chu Kang Road end, 24‰; 19, Sungei Simpang, 24‰; 20, Sembawang Park, 25‰; 21, Causeway, 25‰; 22, Kranji bund, 25‰; 23, Stulang Laut, 26‰; 24, West Coast Drain 2, 27‰; 25, Singapore River, 27‰.
Fig. 7 in Genetic and morphological variation of metacercariae of Microphallus piriformes (Trematoda, Microphallidae): Effects of paraxenia and geographic location
Fig. 7. Variability of metacercarial body shape within hemipopulations and infrapopulations of M. piriformes. A: Absolute and relative morphological disparity (MD) of metacercariae within hosts of the same species. B: Distribution of morphological disparity (MD) within individual snails grouped by host species and sampling location.
Fig. 4 in Genetic and morphological variation of metacercariae of Microphallus piriformes (Trematoda, Microphallidae): Effects of paraxenia and geographic location
Fig. 4. Haplotype networks, COI sequence (369 bp); TCS algorithm; dashes correspond to mutations. A: color reflects sampling location. B: color reflects host species.
Fig. 5 in Genetic and morphological variation of metacercariae of Microphallus piriformes (Trematoda, Microphallidae): Effects of paraxenia and geographic location
Fig. 5. PCA-ordination of individual M. piriformes metacercariae body shapes grouped by host species. PC1 can be interpreted as a deepness of a "waist" between locomotory and generative body parts; PC2 can be interpreted as a width of locomotory body part. B: Pairwise post-hoc comparison; significant value are shown as bold (considering Holmes correction for multiple comparison); host species: sax – L. saxatilis; obt – L. obtusata; sampling site: Kib - Barents Sea, Kiberg; Kor – White Sea, Korga-Islet; Zel – Barents Sea, Dalnie Zelentsy.
Fig. 1 in Genetic and morphological variation of metacercariae of Microphallus piriformes (Trematoda, Microphallidae): Effects of paraxenia and geographic location
Fig. 1. The map of the study region (image: TerraMetrics, map data: Google). Sample collection sites (Tromsø city, Kiberg settlement, Dalnie Zelentsy settlement, Sredny Island) are shown.
Fig. 8 in Genetic and morphological variation of metacercariae of Microphallus piriformes (Trematoda, Microphallidae): Effects of paraxenia and geographic location
Fig. 8. Body size of M. piriformes metacercariae from different host species and sampling locations. Mean centroid size and 95% confidence interval obtained via bootstrap.
Fig. 3 in Genetic and morphological variation of metacercariae of Microphallus piriformes (Trematoda, Microphallidae): Effects of paraxenia and geographic location
Fig. 3. Bayesian inference based on COI sequence (369 bp); 15000000 generation; GTR + I + G substitution model; A posteriori probabilities are indicated by node shapes; sample name includes parasite species (pir – M. piriformes, pyg – M. pygmaeus, tri – M. triangulatus, sim – M. similis), sample number, geographic region and location (WSk – White Sea, Korga-Islet; WSy – White Sea, Yakovleva; DZe – Barents Sea, Dalnie Zelentsy; Kib - Barents Sea, Kiberg; Tro - Norwegian Sea, Tromsø), host species (sax – L. saxatilis; arc – L. arcana; comp – L. compressa; obt – L. obtusata; fab – L. fabalis). Identical haplotypes and the FST-value of differentiation between populations (Weir, and Cockerham, 1984) are shown in Supplementary Table 1. Branch color reflects geographic region.
Fig. 1 in From incidental findings to systematic discovery: locating and monitoring a new population of the endangered Harlequin Toad
Fig. 1 Location and boundaries of the Alexander Skutch Biological Corridor (ASBC) in the province of San José, Costa Rica.
Fig. 3 in From incidental findings to systematic discovery: locating and monitoring a new population of the endangered Harlequin Toad
Fig. 3 Males, females, and juveniles of Atelopus varius found in the Alexander Skutch Biological Corridor. (A) Male found during February surveys. (B) Sleeping male in the leaf litter in the same location of a male in Fig. 2(A). (C) and (E) are juveniles high above the river bank, at least 3–4 m high in the vegetation of the understory, and juvenile (C) is sleeping. (D) A female Harlequin Toad sleeping on the vegetation five m above the river.
Fig. 2 in From incidental findings to systematic discovery: locating and monitoring a new population of the endangered Harlequin Toad
Fig. 2 Detail of Atelopus varius individuals found during February and June 2017 in the ASBC. The left column includes males; the right column includes females. Males (B) and (C) were photographed as found, as were females (E), (G), and (H). Note the spread-out basking position of female (G).
Figure 1. - Map showing the locations where seahorses H. hippocampus were recorded. 1 in Variables psicológicas implicadas en el desempeño laboral docente
Figure 1. - Map showing the locations where seahorses H. hippocampus were recorded. 1: Bueu; 2: Toralla Island.
Fig. 1. Location and vegetation types where small mammals were sampled between November 2012 and September 2013 in Small mammals from the lasting fragments of Araucaria Forest in southern Brazil: a study about richness and diversity
Fig. 1. Location and vegetation types where small mammals were sampled between November 2012 and September 2013, at Piraí do Sul National Forest, ParanÁ state, Brazil (A, Pine Plantation; B, Riparian Forest; C, Araucaria Plantation; D, Natural Regeneration forest; E, High Altitude forest). Original distribution of Atlantic Forest biome (light gray) and Araucaria forest (dark gray).
Fig. 1. Location map and the geological section. A in A new Y-shaped trace fossil attributed to upogebiid crustaceans from Early Pleistocene of Italy
Fig. 1. Location map and the geological section. A. The study region on the map of Italy. B. Location of the study area. C. Location of the studied section. D. The studied section with indication of Parmaichnus stironensis igen. nov. et isp. nov.
Figure 4A-B. Migration pathways from the Laniakea, O in Ocean pathways and residential foraging locations for satellite tracked green turtles breeding at French Frigate Shoals in the Hawaiian Islands
Figure 4A-B. Migration pathways from the Laniakea, O'ahu foraging site to French Frigate Shoals for two females and one male. The male tracking documented a round-trip migration with the return to Laniakea followed by a move to Kāne'ohe Bay, O'ahu. Year of tracking is indicated on the map.
Figure 9 A-E in Ocean pathways and residential foraging locations for satellite tracked green turtles breeding at French Frigate Shoals in the Hawaiian Islands
Figure 9 A-E. Home ranges for four females and one male green turtle that migrated from French Frigate Shoals to five other neritic foraging areas. Large colored circles indicate 1 km radius around each position. Black circles indicate positions with LC 1, 2 or 3 data. Black lines outline the Minimum Convex Polygons for Minimum Home Range and Full Home Range areas.
Figure 5 in Ocean pathways and residential foraging locations for satellite tracked green turtles breeding at French Frigate Shoals in the Hawaiian Islands
Figure 5. Foraging areas destinations/origins for 19 of the 20 green turtles tracked from 1992- 2014. Transmissions from one turtle stopped midway between French Frigate Shoals and the Main Hawaiian Islands.
Figure 8 A-B in Ocean pathways and residential foraging locations for satellite tracked green turtles breeding at French Frigate Shoals in the Hawaiian Islands
Figure 8 A-B. Home range for two female green turtles that migrated to 'Ewa Beach, O'ahu from French Frigate Shoals. Large colored circles indicate 1 km radius around each position. Black circles indicate positions with LC 1, 2 or 3 data. Black lines outline the Minimum Convex Polygons for Minimum Home Range and Full Home Range areas. Both 'Ewa turtles occupied two Minimum Home Range areas.
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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.