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Fig. 4 in The threat of free-ranging domestic dog to native wildlife: implication for conservation in Southeast Asia

Fig. 4. The spatial distribution of perceived risk from domestic dog (Canis familiaris) across mainland Southeast Asia. Excluded human settlements and water bodies have been marked in white.

Fig. 3 in The threat of free-ranging domestic dog to native wildlife: implication for conservation in Southeast Asia

Fig. 3. Percentage perceived risk in Avian and Mammalian orders. Height of peaks represent number of species scaled to 2, see Supplementary Materials 4 and 5. Orders with two or less species, including Otidiformes, Dermoptera, Perissodactyla, Pholidota, and Proboscidea, were removed for visualisation.

Fig. 2 in The threat of free-ranging domestic dog to native wildlife: implication for conservation in Southeast Asia

Fig. 2. Percentage perceived risk in Red List categories. Height of peaks represent number of species scaled to 2, see Supplementary Materials 4 and 5.

Fig. 1 in The threat of free-ranging domestic dog to native wildlife: implication for conservation in Southeast Asia

Fig. 1. Bayesian networks modelling (a) perceived risk to carnivore mammalian species, (b) perceived risk to non-carnivore mammalian species, (c) perceived risk to Avian species and, (d) the spatial distribution of perceived risk from domestic dogs in mainland Southeast Asia.

Fig. 3 in The bees of Singapore (Hymenoptera: Apoidea: Anthophila): First comprehensive country checklist and conservation assessment for a Southeast Asian bee fauna

Fig. 3. Photographs of selected bee species exemplifying each conservation status. A, NE, Nomia (Maculonomia) elegans (photographed at Ulu Temburong, Brunei); B, CR, Geniotrigona thoracica (photographed in Seremban, Malaysia); C, EN, Xylocopa (Zonohirsuta) dejeanii penangensis (photographed at Ulu Temburong, Brunei); D, VU, Nomia (Acunomia) lusoria; E, VU, Lepidotrigona terminata; F, NT, Homotrigona (Tetrigona) apicalis; G, LC, Amegilla (Zonamegilla) andrewsi; H, NN, Apis (Micrapis) florea; I, DD, Ceylalictus (Ceylalictus) communis. (All photographs by Zestin W. W. Soh)

Fig. 2 in The bees of Singapore (Hymenoptera: Apoidea: Anthophila): First comprehensive country checklist and conservation assessment for a Southeast Asian bee fauna

Fig. 2. Proportion of Singapore's bee species in the national conservation statuses based on the International Union for Conservation of Nature (IUCN) Red List categories: Nationally Extinct (NE), Critically Endangered (CR), Endangered (EN), Vulnerable (VU), Near Threatened (NT), Least Concerned (LC), Data Deficient (DD) and Non-Native (NN). A total of 133 bee species and morphospecies were recorded in Singapore.

Fig. 1 in The bees of Singapore (Hymenoptera: Apoidea: Anthophila): First comprehensive country checklist and conservation assessment for a Southeast Asian bee fauna

Fig. 1. Map of delineated forest patches of CCNR and BTNR. A, Mandai Forest; B, Seletar Forest; C, Nee Soon Swamp Forest; D, Peirce Forest; E, MacRitchie Forest; F, Dairy Farm Nature Park; G, Bukit Timah Nature Reserve; H, Rifle Range.

Fig. 8 in Troubled giants: The updated conservation status of the coconut crab (Birgus latro)

Fig. 8. Birgus latro (Linnaeus, 1767) in its natural habitat on Christmas Island in the Indian Ocean. A, feeding on fruit trees; B, feeding on coconuts. Photographs by Max Orchard.

Fig. 7 in Troubled giants: The updated conservation status of the coconut crab (Birgus latro)

Fig. 7. Threats to Birgus latro (Linnaeus, 1767) while crossing roads during breeding season migrations on Christmas Island in the Indian Ocean. A, cannibalism by coconut crabs; B, crab and vehicle in close proximity; C, recording each road kill incident; D, warning to motorists. Photographs by Max Orchard.

Fig. 10 in Troubled giants: The updated conservation status of the coconut crab (Birgus latro)

Fig. 10. Conservation actions for Birgus latro (Linnaeus, 1767) in Okinawa and Kagoshima Prefectures, Japan. A, the location of Okinawa and Kagoshima Prefectures. The collection of coconut crabs is regulated by legal protective ordinances in the entire Kagoshima Prefecture. B, detail of Okinawa Prefecture showing the islands where the collection of coconut crabs is regulated by legal protective ordinances, shown in red ovals (Tarama Village, Miyakojima City, and Ishigaki City). Islands shown in black ovals (Yonaguni Village, Taketoni Town, and Okinawa Island and its associated islands) do not have protective ordinances for coconut crabs.

Fig. 5 in Troubled giants: The updated conservation status of the coconut crab (Birgus latro)

Fig. 5. Life stages of Birgus latro (Linnaeus, 1767) on Christmas Island in the Indian Ocean. A, juvenile crab with pleon inside small snail shell; B, juvenile with pleon inside larger shell of African giant snail (an introduced species); C, young subadult with hardened pleon that had recently cast off its snail shell. Photographs by Max Orchard.

Fig. 6 in Troubled giants: The updated conservation status of the coconut crab (Birgus latro)

Fig. 6. Birgus latro (Linnaeus, 1767) in its natural habitat on Christmas Island in the Indian Ocean. A, two adults mating; B, gravid female carrying eggs; C, female releasing eggs into the sea. Photographs by Max Orchard.

Fig. 9 in Troubled giants: The updated conservation status of the coconut crab (Birgus latro)

Fig. 9. Threats to Birgus latro (Linnaeus, 1767) on Christmas Island (Indian Ocean) from aggressive, invasive yellow crazy ants (Anoplolepis gracilipes). A, ants attacking the arthrodial membranes between peg articles; B, ants attacking the eyestalks; C, ants swarming on the body of a coconut crab. Photographs by Max Orchard. These images were kindly provided by Atara Film GmbH / NDR Doclights, from the film "Realm of the Robber Crab".

Fig. 4 in Troubled giants: The updated conservation status of the coconut crab (Birgus latro)

Fig. 4. Updated localities where Birgus latro (Linnaeus, 1767) is either extirpated (red, darkest circles) or its continued existence is uncertain (yellow, lightest circles). Note that the scale of the map may imply a wider area of extirpation than is actually known, so reference to the text and Table 3 is recommended to see the exact localities where extirpation is suspected.

Figure 1 in Description, biology and conservation of a new species of Australian tree frog (Amphibia: Anura: Hylidae: Litoria) and an assessment of the remaining populations of Litoria genimaculata Horst, 1883: systematic and conservation implications of an unusual speciation event

Figure 1. Distribution of Litoria myola sp. nov. (formerly termed iS) and the northern (N) and southern (S) lineages of Litoria genimaculata in the Wet Tropics, northeast Queensland. CT, Carbine Tableland; BMC, Black Mountain Corridor; LR, Lamb Range; BK, Bellenden Ker Range; AT, Atherton Tableland; MT, Malbon Thompson Range; GR, Graham Range.

Figure 2 in Description, biology and conservation of a new species of Australian tree frog (Amphibia: Anura: Hylidae: Litoria) and an assessment of the remaining populations of Litoria genimaculata Horst, 1883: systematic and conservation implications of an unusual speciation event

Figure 2. Litoria myola, sp. nov., males (A, a pale individual; B, a heavily marked individual), Kuranda, north-east Queensland.

Figure 3 in Description, biology and conservation of a new species of Australian tree frog (Amphibia: Anura: Hylidae: Litoria) and an assessment of the remaining populations of Litoria genimaculata Horst, 1883: systematic and conservation implications of an unusual speciation event

Figure 3. Spectrogram of the courtship call of Litoria myola sp. nov. (recorded at an air temperature of 25 °C). The spectrogram displays a single courtship call consisting of six notes ('tocs'). The degree of shading displays call intensity.

Figure 7 in Description, biology and conservation of a new species of Australian tree frog (Amphibia: Anura: Hylidae: Litoria) and an assessment of the remaining populations of Litoria genimaculata Horst, 1883: systematic and conservation implications of an unusual speciation event

Figure 7. Rainforest stream habitat, with rocky (A) and sandy (B) substrate, Kuranda, north-east Queensland. Litoria myola sp. nov. and Litoria genimaculata are present at both sites.

opencc-by-4.0Oct 2022View details →

Air temperature and humidity effects on the performance of conservation detection dogs

This is the dataset which underlies the submitted manuscript entitled " Air temperature and humidity effects on the performance of conservation detection dogs". The uploaded data contain an xlsx file,which includes the data, as well as a txt readme file, which explains the header information in the data file.