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Figure 4 in The neritid snails of Brunei Darussalam: their geographical, ecological and conservation significance
Figure 4. Side view showing off spire plasticity amongst Nerita species found in Brunei Darussalam. A. Nerita albicilla Linnaeus, 1758. B. Nerita litterata Gmelin, 1791. C. Nerita insculpta Récluz, 1841. D. Nerita patula Récluz, 1841. E. Nerita chamaeleon Linnaeus, 1758. F. Nerita undata Linnaeus, 1758. G. Nerita balteata Reeve, 1855. H. Nerita planospira Anton, 1838. I. Neripteron violaceum (Gmelin, 1791). J. Neripteron cornucopia (Benson, 1836). K. Vittina coromandeliana (G. B. Sowerby I, 1836). L. Neritodryas dubia (Gmelin, 1791). M. Clithon oualaniense (Lesson, 1831). N. Neripteron spirale (Reeve, 1855). O. Nerita histrio Linnaeus, 1758. P. Nerita exuvia Linnaeus, 1758. Markings on I and J: the spire hangs further midway in N. cornucopia compared to N. violaceum. Scale bar on top represents 3 mm, unless stated otherwise.
Figure 1 in The neritid snails of Brunei Darussalam: their geographical, ecological and conservation significance
Figure 1. Brunei Darussalam is situated on the northwest coast of Borneo island in the Southeast Asia and is stretched along the South China Sea coastline. Bottom image shows the localities of Neritidae snails in Brunei. Abbreviations: MC. Jerudong Park Medical Centre (4.9486°N, 114.8283°E). PJ. Pantai Jerudong (4.9583°N, 114.8394°E). ES. Empire site (4.9694°N, 114.8551°E). PP. Pulau Punyit (4.9753°N, 114.8490°E). PT. Pantai Tungku (4.9703°N, 114.8667°E). UB. Universiti Brunei Darussalam (4.9853°N, 114.8994°E). PR. Pelong Rocks (5.0789°N, 115.0528°E). TB. Tanjung Batu (5.0388°N, 115.0617°E). SK. Sungai Kedayan (4.8981°N, 114.9341°E). SBe. Sungai Besar (4.9278°N, 115.0144°E). SBu. Sungai Bunga (4.9155°N, 115.0062°E). SD. Sungai Damuan (4.8689°N, 114.9117°E). BM. Batu Marang (4.9853°N, 115.0308°E). PB. Pulau Bedukang (4.9795°N, 115.0576°E). PS. Pulau Selirong (4.8765°N, 115.1296°E). PPt. Pulau Pepatan (4.9161°N, 115.0459°E). PK. Pulau Kaingaran (4.9474°N, 115.0277°E). Highlighted coastline indicates area with artificial seawalls.
Figure 2 in Spatial and temporal nesting pattern of Sea Turtles in Alas Purwo National Park, and its implications for conservation management practices
Figure 2. Trend of sea turtle nesting in the past 40 years at APNP: (A) L.olivacea, (B) C. mydas, (C) E. imbricata, and (D) D. coriacea.
Figure 1 in Spatial and temporal nesting pattern of Sea Turtles in Alas Purwo National Park, and its implications for conservation management practices
Figure 1. Study location in Alas Purwo National Park's Pancur-Cungur Coast with six hypothetical stations (dot: sector benchmark point).
Figure 4 in Spatial and temporal nesting pattern of Sea Turtles in Alas Purwo National Park, and its implications for conservation management practices
Figure 4. Number of four sea turtles nesting in each month during survey period: (A) L.olivacea, (B) C. mydas, (C) E. imbricata, and (D) D. coriacea.
Figure 3 in First record of the saproxylic beetle Corticeus (= Hypophloeus) unicolor Piller & Mitterpacher, 1783 in Montenegro (Coleoptera: Tenebrionidae) with comments on old-growth forests conservation in the Country
Figure 3. Mixed beech–silver fir–Norway spruce old-growth forest, snag and coarse woody debrys in Biogradska gora National Park, where Corticeus unicolor was collected.
Figure 2 in First record of the saproxylic beetle Corticeus (= Hypophloeus) unicolor Piller & Mitterpacher, 1783 in Montenegro (Coleoptera: Tenebrionidae) with comments on old-growth forests conservation in the Country
Figure 2. Corticeus unicolor: (A) side view and (B) view from above (B). Scale bar: 1 mm. Photos by F. Parisi.
Figure 1. A in Further finding of Bolitophagus reticulatus (Linnaeus, 1767) in Montenegro (Coleoptera: Tenebrionidae) with brief comments on its distribution and conservation
Figure 1. A. Location of Bolitophagus reticulatus finding site in Montenegro. B. Localization of the finding in the Bjelasica mountain range in the Dinaric Alps (Montenegro). Graphic processing Giovanni D'Amico.
Figure 2 in Further finding of Bolitophagus reticulatus (Linnaeus, 1767) in Montenegro (Coleoptera: Tenebrionidae) with brief comments on its distribution and conservation
Figure 2. Mixed forest of Norwegian beech-fir and fallen dead trees in Biogradska Gora National Park, where Bolitophagus reticulatus was found. Photo by F. Parisi.
Figure 3 in Further finding of Bolitophagus reticulatus (Linnaeus, 1767) in Montenegro (Coleoptera: Tenebrionidae) with brief comments on its distribution and conservation
Figure 3. Specimen of Bolitophagus reticulatus collected in Biogradska Gora National Park. Scale bar: 1 mm. The specimen was photographed with a 3D microscope with a full HD camera and LED illumination. Photo by F. Parisi.
Figs. 24-30. 24. Cybister sugillatus Erichsin, 1834 in Aquatic Coleoptera Of Singapore: Species Richness, Ecology And Conservation #
Figs. 24-30. 24. Cybister sugillatus Erichsin, 1834 (Fam. Dytiscidae, 22.0 mm); 25 Hydrocanthus indicus Wehncke, 1876 (Fam. Noteridae, 4.5 mm); 26. Spercheus stangli Schwarz & Barber, 1917 (Fam. Spercheidae, 4.2 mm); 27. Berosus fairmairei Zaitzev, 1908 (Fam. Hydrophilidae, 4.5 mm); 28. Amphiops mater sumatrensis (Sharp, 1873) (Fam. Hydrophilidae, 3.5 mm); 29. Helochares pallens (MacLeay, 1825) (Fam. Hydrophilidae, 3.1 mm);30. Hydrophilus cavisternum Bedel, 1891 (Fam. Hydrophilidae, 32.0 mm).
Figs. 15-17.15 in Aquatic Coleoptera Of Singapore: Species Richness, Ecology And Conservation #
Figs. 15-17.15. Microdytes elgae Hendrich, Balke & Wewalka, 1995 (Fam. Dytiscidae, 2.0 mm); 16. Lacconectus corayi Brancucci, 1986 (Fam. Dytiscidae, 3.7 mm); 17. Hydaticus bipunctatus conjungens Régimbart, 1899 (Fam. Dytiscidae, 13.4 mm).
Figs. 9-14. 9. Lorong Banir, pond 2 in Aquatic Coleoptera Of Singapore: Species Richness, Ecology And Conservation #
Figs. 9-14. 9. Lorong Banir, pond 2. Fully covered with dense stands of the submerged freshwater macrophyte Hydrilla verticullata. Habitat of Canthydrus morsbachi, Laccophilus siamensis siamensis, Hydaticus bipunctatus conjungens, Allocotocerus muelleri, Amphiops mater sumatrensis, Enochrus esuriens, Helochares taprobanicus, H. lentus, H. pallens and Coelostoma subditum; 10. Central Catchment Area, Edge of Nee Soon Swamp Forest: The mats of floating grasses are the habitat of three Neohydrocoptus and eight Singaporean Hydrovatus species; 11. Central Catchment Area, Nee Soon Swamp Forest near former pumphouse. Hydaticus fabricii, Hydrovatus sinister, H. stridulus, H. pudicus, Amphiops mater sumatrensis, Helochares lentus and Enochrus gaggermeieri occur in this pond; 12. Central Catchment Area, temporary puddle on forest floor. Habitat of Copelatus oblitus and C. minutissimus;13. Bukit Timah Nature Reserve. Taban Valley, open forest stream. The shaded springlet of this stream, a true relic site, is the habitat for the most restricted and endangered water beetles in Singapore. Microdytes elgae, M. pasiricus, Lacconectus krikkeni and two species of the genus Hydranea; 14. Central Catchment Area. Shaded, slow flowing and oxygen rich artificial stream in second growth forest. Habitat of most species of the whirligig genus Orectochilus.
Figs. 18-23. 18 in Aquatic Coleoptera Of Singapore: Species Richness, Ecology And Conservation #
Figs. 18-23. 18.Hydaticus fabricii (MacLeay, 1825) (Fam. Dytiscidae, 10.5 mm); 19. Leiodytes nicobaricus (Redtenbacher, 1867) (Fam. Dytiscidae, 2.1 mm); 20. Hydrovatus rufoniger rufoniger (Clark, 1863) (Fam. Dytiscidae, 3.6 mm); 21. Laccophilus medialis Sharp, 1882 (Fam. Dytiscidae, 3.3 mm); 22. Copelatus minutissimus Balfour-Browne, 1939 (Fam. Dytiscidae, 4.1 mm); 23. Eretes griseus (Fabricius, 1781) (Fam. Dytiscidae, 13.5 mm).
Figs. 5-8. 5 in Aquatic Coleoptera Of Singapore: Species Richness, Ecology And Conservation #
Figs. 5-8. 5. Small artificial pond in Botanic Gardens. Almost covered with the free-floating freshwater macrophytesEichhornia crassipes and Salvinia molesta. Habitat of the dytiscids Hydroglyphus inconstans and Leiodytes nicobaricus;6. Former quarry pond in Bukit Batok Nature Park. Habitat of Neohydrocoptus subvittulus, Hydrovatus sinister, H. pudicus, Laccophilus siamensis siamensis, Amphiops mater sumatrensis, Enochrus esuriens, Helochares minor and Paracymus atomus; 7. Botanic Gardens, NIE Ecology Pond. Habitat of Neohydrocoptus bivittis, Enochrus esuriens and Paracymus orientalis; 8. Lorong Banir, pond 1. Habitat of Canthydrus morsbachi, Hydrovatus sinister, Laccophilus siamensis siamensis, Hydaticus reductus, Allocotocerus muelleri, Helochares taprobanicus and H. lentus.
Fig. 2 in Conservation Of The Javan Gibbon Hylobates Moloch: Population Estimates, Local Extinctions, And Conservation Priorities
Fig. 2. Relation between number of groups calling per day and number of census days in the Telaga Warna Nature Reserve (Sept 1999) and Lingo Asri, Dieng mountains (Sept 1998).
Fig. 1 in Conservation Of The Javan Gibbon Hylobates Moloch: Population Estimates, Local Extinctions, And Conservation Priorities
Fig. 1. Current distribution of the Javan gibbon Hylobates moloch. Based on Kappeler, 1984, Asquith et al., 1995, Nijman 2001b, and present study. All areas where the species' presence has been confirmed are indicated in black; areas where the species' possible presence was reported by Andayani et al. (1999) are indicated in white. The three main study areas are: A, Telaga Warna Nature Reserve; B, Gunung Gede Pangrango National Park; C, Dieng mountains. The insert shows Java with all remaining forest patches on the island.
Fig. 1 in Review on parasites of wild and captive giant pandas (Ailuropoda melanoleuca): Diversity, disease and conservation impact
Fig. 1. Distribution of wild giant pandas in six mountain regions (Qinling, Minshan, Qionglai, Liangshan, Daxiangling and Xiaoxiangling) in three Provinces (Gansu, Shaanxi, and Sichuan) of China. Adapted from Wang et al. (2018).
Fig. 13 in Diversity and conservation of terrestrial, freshwater, and marine reptiles and amphibians in Saudi Arabia
Fig. 13. The Egyptian Spiny-tailed Lizard, Uromastyx aegyptia, is hunted and killed by the hundreds and sold either alive or for its meat and eggs.
Fig. 11 in Diversity and conservation of terrestrial, freshwater, and marine reptiles and amphibians in Saudi Arabia
Fig. 11. Snakes of Saudi Arabia. (A) Platyceps elagantissimus. (B) Telescopus dhara. (C) Platyceps rhodarchis. (D) Psammophis schokari. Photos by M. Al Sulimi (A), A. Al Salman (B–C), and A. Aloufi (D).
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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.