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Fig. 6 in A comparative exploration of the inquiline and prey species of Nepenthes rafflesiana pitchers in contiguous and fragmented habitat patches in Singapore
Fig. 6. Box and whisker plots show that inquiline taxa were found in different abundances across the different forest types, with several species being confined to the old secondary forests within the Central Catchment Nature Reserve (CCNR). Bold horizontal lines represent median log-transformed number of each inquiline taxon in pitchers from each forest type (denoted by colours); boxes represent interquartile range; whiskers represent maximum values. Taxon names are abbreviated as done in the previous figure; rare inquiline taxa which were present in only one sample are not displayed.
Fig. 12. Habitats. A, a in Review of the genus Rhagovelia Mayr, 1865 (Insecta: Heteroptera: Veliidae) in the Palawan biogeographic region, the Philippines
Fig. 12. Habitats. A, a larger river at Napsan Road, kilometre 29, with high water level after heavy rain; R. palawanensis and R. estrella were recorded in quieter rock pools and between flooded vegetation. B, a small streamlet at Calatoboc Bridge over Northern National Highway was inhabited by R. kawakamii hoberlandti and R. gapudi, new species. Whereas the first species is euryoecious, R. gapudi, new species, prefers such small running waters.
Fig. 2 in A comparative exploration of the inquiline and prey species of Nepenthes rafflesiana pitchers in contiguous and fragmented habitat patches in Singapore
Fig. 2. Habitat types in which Nepenthes rafflesiana plants were found in this study: (a) coastal cliffs; (b) adinandra belukar; (c) old secondary forests (in this case, a tree fall gap within an old secondary forest). Nepenthes rafflesiana plants are indicated by an arrow in panels a and c. Coastal cliffs (a) and adinandra belukar (b) type habitats were mainly found outside the Central Catchment Nature Reserve (CCNR), while old secondary forests type habitats were only found within the CCNR. Despite their different locations, plant communities in which N. rafflesiana were found in coastal cliff habitats (a) and typical adinandra belukar habitats (b) were compositionally highly similar and may both be classified as adinandra belukar type plant communities. (Photographs by: Lam Weng Ngai).
Fig. 1 in A comparative exploration of the inquiline and prey species of Nepenthes rafflesiana pitchers in contiguous and fragmented habitat patches in Singapore
Fig. 1. Nepenthes rafflesiana lower (a) and upper (b) pitchers in situ; location of the Central Catchment Nature Reserve (CCNR) in Singapore (c). Data sources for (c): Singapore Public Data (https://data.gov.sg); Global Administrative Areas Database version 3.6 (https:// gadm.org/data.html). (Photographs by: Lam Weng Ngai).
Fig. 5 in A comparative exploration of the inquiline and prey species of Nepenthes rafflesiana pitchers in contiguous and fragmented habitat patches in Singapore
Fig. 5. Sample-size- (a) and coverage-based (b) rarefaction curves of inquiline species richness from pitchers collected outside of (pink lines) and within (brown lines) the Central Catchment Nature Reserve (CCNR). Lines represent the interpolated (continuous) and extrapolated (dashed) species richness of each forest type, as a function of the number of individuals sampled within it (a) and the estimated sample coverage (b); shaded regions represent the 95% confidence intervals of these estimates; points represent the observed species richness (these are omitted from panel b to prevent the obscuring of other details in the figure).
Fig. 4 in A comparative exploration of the inquiline and prey species of Nepenthes rafflesiana pitchers in contiguous and fragmented habitat patches in Singapore
Fig. 4. Two-dimensional NMDS plot of the pitcher inquiline communities of the sampled Nepenthes rafflesiana pitchers. Each point represents an inquiline community from an individual pitcher, with its colour denoting the location in which it was found (within [brown] or outside [pink] the Central Catchment Nature Reserve [CCNR]), and its shape denoting its pitcher type (triangles denote upper, and circles, lower, pitchers). Texts represent inquiline species centroids, with font sizes proportional to the number of pitchers in which each was found. A species is more likely to occur in a pitcher if the pitcher's point is located close to the species' centroid. Taxon name abbreviations: Dasy = Dasyhelea spp.; Phor = Phoridae; Ar.giv = Armigeres giveni; Ar.kuc = Ar. cf. kuchingensis; Cx.bre = Culex brevipalpus complex; Cx.cur = Cx. curtipalpis; Tp.tnx = Tripteroides tenax; Lest = Lestodiplosis sp.; Nsyr = Nepenthosyrphus sp. raff; Creu = Creutzeria spp.; M2.sp1 = Histiostomatidae genus 1 sp. 1; Naca = Nepenthacarus spp.; Zwic = Zwickia spp.; Nema = nematodes.
Fig. 9 in A comparative exploration of the inquiline and prey species of Nepenthes rafflesiana pitchers in contiguous and fragmented habitat patches in Singapore
Fig. 9. Habitus of Armigeres giveni fourth instar larva (a); Ar. giveni female adult (b); Ar. cf. kuchingensis fourth instar larva (c); Ar. cf. kuchingensis male adult (d). Scale bars represent 1 mm. (Photographs by: Yeo Huiqing).
Fig. 14. Habitats. A in Review of the genus Rhagovelia Mayr, 1865 (Insecta: Heteroptera: Veliidae) in the Palawan biogeographic region, the Philippines
Fig. 14. Habitats. A, the stream below the Ilian Falls northeast of Roxas, running through a forested watershed area, is the type locality of R. matillanoi, new species, and R. abbreviata, new species; R. kawakamii hoberlandti was also found in quiet bays. B, C, the same three species were collected in the stream below the Canequi Falls at Pularaquin, about 20 km north of Taytay.
Fig. 10 in A comparative exploration of the inquiline and prey species of Nepenthes rafflesiana pitchers in contiguous and fragmented habitat patches in Singapore
Fig. 10. Illustrations of mite genera inhabiting Nepenthes rafflesiana pitchers in Singapore: (a) Undescribed genus (male dorsum), (b) Creutzeria sp. (male venter), (c) Zwickia sp. (male dorsum), (d) Nepenthacarus sp. (male dorsum). Scale bars represent 150 micrometres. (Illustrations by: Norman J. Fashing).
Fig. 22. Habitats S in Hybridization Among Western Whiptail Lizards (Cnemidophorus Tigris) In Southwestern New Mexico: Population Genetics, Morphology, And Ecology In Three Contact Zones
Fig. 22. Habitats S of the southern transect, along NM Hwy 80 S of Road Forks (tables 2, 3; figs 3, 5; appendix 1), 22 August 1990. Top. Looking NE in Granite Gap, from the same place as figure 21, bottom. Bottom. Looking NE at Granite Gap from 20.7 km (by road) S of Road Forks; site 39 is 1.2 km to the NE (on left).
Fig. 19. Habitats near the southern transect, W in Hybridization Among Western Whiptail Lizards (Cnemidophorus Tigris) In Southwestern New Mexico: Population Genetics, Morphology, And Ecology In Three Contact Zones
Fig. 19. Habitats near the southern transect, W of Cotton City (tables 2, 3; figs. 3, 5; appendix 1), 22 August 1990. Top. Site 41, Crystal Mine, looking W from NM Hwy 80, at 13.7 km (by road) S of Road Forks. Bottom. Looking SE from the same place as the top photograph; Table Top Mountain (site 47) is the low butte in the distant right.
Fig. 16. Habitats N in Hybridization Among Western Whiptail Lizards (Cnemidophorus Tigris) In Southwestern New Mexico: Population Genetics, Morphology, And Ecology In Three Contact Zones
Fig. 16. Habitats N of Steins, near the central transect (tables 2, 3; figs. 3, 5; appendix 1), 23 August 1990. Top. Looking S behind the allelemobile at abrupt ecotone between grassland and creosote desertscrub, 0.8 km N of site 16. Bottom. Looking W across grassland, with creosote ecotone on left (in near background), from the same place as the top photograph.
Fig. 1 in Sleeping site selection in two Asian viverrids: effects of predation risk, resource access and habitat characteristics
Fig. 1. Home ranges, core areas and sleeping sites of binturongs (Arctictis binturong) and masked palm civets (Paguma larvata). Home ranges (minimum convex polygon [MCP] 95%) and core areas (MCP 50%) with sleeping sites overlaid of (a) three masked palm civets and a female binturong at Tikong, (b) a male binturong at Sesawo, and (c) location of study sites (Sesawo and Tikong) within the study area (Thung Yai Naresuan Wildlife Sanctuary – West). Different gray shades within home ranges represent core areas of each animal.
Fig. 4 in Sleeping site selection in two Asian viverrids: effects of predation risk, resource access and habitat characteristics
Fig. 4. Use and reuse of sleeping sites. Cumulative number of unique sleeping sites in relation to the total number of sites observed for two binturongs (Arctictis binturong) and three masked palm civets (Paguma larvata). Numbers of unique sleeping sites (sites that are not re-used) versus total sleeping sites observed and study areas are indicated in parenthesis.
Fig. 3 in Sleeping site selection in two Asian viverrids: effects of predation risk, resource access and habitat characteristics
Fig. 3. Use of sleeping sites within different forest types. Percentage of different forest types used (denoted as U) for sleeping sites versus forest types available (A) for two binturongs (Arctictis binturong) and three masked palm civets (Paguma larvata). Forest types are: semi-evergreen forest (SEF), mixed deciduous forest (MDF), and dry dipterocarp forest (DDF). Numbers in parenthesis after individual animals represent the number of sleeping sites used in the analysis, excluding reused sites.
Fig. 2 in Sleeping site selection in two Asian viverrids: effects of predation risk, resource access and habitat characteristics
Fig. 2. Use of vertical strata for sleeping sites. Percentage use of different vertical strata of sleeping sites by five radio-collared viverrids (two binturongs Arctictis binturong and three masked palm civets Paguma larvata). Strata are: Above canopy, Canopy, and Sub-canopy. Numbers in parenthesis represent number of sleeping sites where animals were directly observed, excluding reused sites.
FIGURE 1. Buthacus Birula, 1908, representative habitats. A in Systematic Revision Of The Sand Scorpions, Genus Buthacus Birula, 1908 (Buthidae C.L. Koch, 1837) Of The Levant, With Redescription Of Buthacus Arenicola (Simon, 1885) From Algeria And Tunisia
FIGURE 1. Buthacus Birula, 1908, representative habitats. A. Mamshit [Kurnub], Israel, habitat of Buthacus amitaii, sp. nov. B. Naftah to Ong Jmal, Tunisia, habitat of Buthacus arenicola (Simon, 1885). C. Faiyum Oasis, Egypt, habitat of Buthacus leptochelys (Ehrenberg, 1829). D. Ashdod Nizzanim Nature Reserve, Israel, habitat of Buthacus nitzani Levy et al., 1973, stat. nov. E. Yotvata, Israel, habitat of Buthacus arava, sp. nov., and Buthacus yotvatensis Levy et al., 1973, stat. rev. F. Be'er Milka, Israel, Holot Haluza sand dunes, Israel, habitat of Buthacus levyi, sp. nov., and B. nitzani.
Fig. 27 in The Ecology And Migrations Of Sea Turtles 8. Tests Of The Developmental Habitat Hypothesis
Fig. 27. Size structure on four foraging grounds that presumably represent benthic developmental habitat for Lepidochelys kempii. Minimum adult size, indicated by the dashed line, is from Pritchard and Marquez (1973). Sources are: A, Carr and Caldwell (1956); B, Morreale et al. (1992); C, Musick and Limpus (1996); and D, Henwood and Ogren (1987).
Fig. 24 in The Ecology And Migrations Of Sea Turtles 8. Tests Of The Developmental Habitat Hypothesis
Fig. 24. Size structure on four foraging grounds that presumably represent benthic developmental habitats for Chelonia mydas. Minimum adult size, indicated by the dashed line, for C. mydas in the Atlantic (A, B, and D) based on 178 laparoscopies of C. mydas in Panama (Meylan and Meylan, unpubl. data); that for the Pacific (C) from Balazs (1980). Sources are: A, Bjorndal and Bolten (1995); B, Ehrhart et al., (1996); C, Balazs et al., (1987); D, Carr and Caldwell (1956).
Fig. 23 in The Ecology And Migrations Of Sea Turtles 8. Tests Of The Developmental Habitat Hypothesis
Fig. 23. Life cycle models for cheloniid sea turtles that reflect overlap between benthic developmental habitat and other stages of the life cycle. A, Overlap between developmental habitat and the adult migratory pathway as occurs for Chelonia mydas at the Zapatilla Cays, Bocas del Toro Province, Panama (this study, Meylan and Meylan, unpubl. data). B, Overlap between developmental habitat and internesting habitat that apparently occurs for Caretta caretta along the east coast of Florida (Henwood, 1987; Ernest et al., 1989). C, Partial overlap between developmental habitat and the adult foraging range as appears to occur for Eretmochelys imbricata at Mona Island, Puerto Rico (Van Dam and Diez, 1998b), and around Antigua and Barbuda (Fuller et al., 1992). D, Complete overlap between developmental habitat and the adult foraging range that may be common for Chelonia mydas in the Pacific (see text on contradictory evidence).
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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.