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9,937 results for “Endemicity”
Fig. 2 in The most northeastern record of the Turkish endemic viper, Pelias barani (Böhme and Joger, 1984), from northeastern Anatolia: two viper species in a valley
Fig. 2. Dorsal (A) and ventral (B) views of typical head pattern, and each side of the head (C–D) in a female specimen of Pelias barani from the Çağlayan Valley, Fındıklı, Turkey. Photos by Serkan Gül.
Fig. 1 in The most northeastern record of the Turkish endemic viper, Pelias barani (Böhme and Joger, 1984), from northeastern Anatolia: two viper species in a valley
Fig. 1. Distribution map of Pelias barani and PelIas kaznakovI (created using ArcGIS 10.4). Red stars: Pelias barani from Mebert et al. (2015), blue star: new locality record for Pelias barani, yellow stars: known localities of PelIas kaznakovI. Inset map indicates previously known localities. Photo by Serkan Gül.
Fig. 4 in The most northeastern record of the Turkish endemic viper, Pelias barani (Böhme and Joger, 1984), from northeastern Anatolia: two viper species in a valley
Fig. 4. Proximity of nearest known Pelias barani and Pelias kaznakovI localities (map generated using Google Earth 7.3.2). Blue pin marker: Pelias barani from Mebert et al. (2015), red pin markers: PelIas kaznakovI from Mebert et al. (2015) and Gül et al. (2016b), yellow pin marker: new locality record of Pelias barani in this study. Distance between blue and yellow pin markers is ~19 km. Note that the short distance between Pelias barani and PelIas kaznakovI localities in the Çağlayan Valley indicates a potential contact zone.
Fig 4 in Unexpectedly high Sphaerodactylus diversity on a Caribbean island: new locality for the Honduran endemic Sphaerodactylus dunni Schmidt, 1936 (Gekkonidae: Sphaerodactylidae) on Utila Island, Honduras
Fig 4. Pictures of an adult Sphaerodactylus dunni photographed in 2014, in Pico Bonito National Park, La Cieba, Honduras, to provide direct comparison and aid in confirmation of the species' presence on Utila Island. Photos by Tom W. Brown.
Fig 2 in Unexpectedly high Sphaerodactylus diversity on a Caribbean island: new locality for the Honduran endemic Sphaerodactylus dunni Schmidt, 1936 (Gekkonidae: Sphaerodactylidae) on Utila Island, Honduras
Fig 2. Key diagnostic features (outlined in white or indicated in blue) used to identify the captured individual as Sphaerodactylus dunni on Isla de Utila, Honduras. (A) Three supralabial scales positioned beneath/level to the lower anterior half of each eye; (B) nine narrow sub-digital lamellae on digit IV (described range of 7–11); (C) keeled dorsal scales (not outlined) and usually a superciliary spine located at or posterior to the level of the mid-eye; (D) subcaudal scales in alternating series on tail. Photos by Tom W. Brown.
Fig 3 in Unexpectedly high Sphaerodactylus diversity on a Caribbean island: new locality for the Honduran endemic Sphaerodactylus dunni Schmidt, 1936 (Gekkonidae: Sphaerodactylidae) on Utila Island, Honduras
Fig 3. Google Earth © map hosted on the IUCN platform for Sphaerodactylus dunni (Townsend et al. 2013), illustrating the known range of the species on mainland Honduras, modified to include the new locality on Utila Island (X), part of Islas de la Bahía. Map data: see Google Earth (https://www.google.com/earth/) and Townsend et al. (2013).
Fig 1 in Unexpectedly high Sphaerodactylus diversity on a Caribbean island: new locality for the Honduran endemic Sphaerodactylus dunni Schmidt, 1936 (Gekkonidae: Sphaerodactylidae) on Utila Island, Honduras
Fig 1. An adult Sphaerodactylus dunni photographed upon capture at its newly reported locality on Isla de Utila, Honduras. Photo by Tom W. Brown.
Fig. 4 in Insights into the natural history of the endemic Harlequin Toad, Atelopus laetissimus Ruiz-Carranza, Ardila-Robayo, and Hernández-Camacho, 1994 (Anura: Bufonidae), in the Sierra Nevada de Santa Marta, Colombia
Fig. 4. Habitat suitability estimate (upper left panel), minimum convex polygon of extent of occurrence (EEO, upper right panel), and area of occupation (AOO, lower left panel) of Atelopus laetissimus. The total deforested area for the analyzed period and species occurrence locations are provided in red.
Figure 3 in Insights into the natural history of the endemic Harlequin Toad, Atelopus laetissimus Ruiz-Carranza, Ardila-Robayo, and Hernández-Camacho, 1994 (Anura: Bufonidae), in the Sierra Nevada de Santa Marta, Colombia
Figure 3. Acoustic repertoire of the advertisement call of Atelopus laetissimus. Conventional pulsed call (A), unpulsed short call (B), partially pulsed short call (C), pulsed short call (D), partially pulsed short call before pulsed call (E), and partially pulsed short call within pulsed call (F). The corresponding author will provide tables of raw data for individual specimens on request.
Fig. 2 in Insights into the natural history of the endemic Harlequin Toad, Atelopus laetissimus Ruiz-Carranza, Ardila-Robayo, and Hernández-Camacho, 1994 (Anura: Bufonidae), in the Sierra Nevada de Santa Marta, Colombia
Fig. 2. Temporal variation of the number of recaptures (A) and movement patterns (B) of Atelopus laetissimus.
Fig. 1 in Insights into the natural history of the endemic Harlequin Toad, Atelopus laetissimus Ruiz-Carranza, Ardila-Robayo, and Hernández-Camacho, 1994 (Anura: Bufonidae), in the Sierra Nevada de Santa Marta, Colombia
Fig. 1. (A) Temporal variation of relative abundance (ind/[h × obs]). (B) Population density (m2) per habitat of Atelopus laetissimus. Roman numerals represent the months of the surveys.
Fig. 5 in Insights into the natural history of the endemic Harlequin Toad, Atelopus laetissimus Ruiz-Carranza, Ardila-Robayo, and Hernández-Camacho, 1994 (Anura: Bufonidae), in the Sierra Nevada de Santa Marta, Colombia
Fig. 5. Estimated annual habitat loss for Atelopus laetissimus in the last decade in the potential distribution (A), area of occurrence (AOO, B), and extent of occurrence (EOO, C).
Figure 1 in First record of the southwestern Indian Ocean endemic Apolemichthys kingi (Teleostei: Pomacanthidae) from Sainte Marie Island, Madagascar
Figure 1. – Map of Madagascar (A) with the locations where the specimen of Apolemichthys kingi was photographed in 2018 (Sainte Marie Island, site B) and identified in 2013 (north of Tôlanaro, site C). Image of the specimen photographed in site B (B), caught and identified in site C (C), and in South Africa (D). Photography credits: J. Wickel (B), S. Fennessy (C), A. D. Connell (D).
Fig. 4 in The neglected diversity: Description and molecular characterisation of Trypanosoma haploblephari Yeld and Smit, 2006 from endemic catsharks (Scyliorhinidae) in South Africa, the first trypanosome sequence data from sharks globally
Fig. 4. Bayesian Inference (BI)/Maximum Likelihood (ML) analysis showing the phylogenetic position of Trypanosoma haploblephari (Yeld and Smit, 2006) genotypes representing morphotypes A and B inferred from partial 18S rRNA gene sequences. Comparative sequences representing known Trypanosoma species, with Trypanosoma avium (KT728402) as outgroup, were obtained from GenBank. Tree topologies for both the BI and ML trees were identical; the nodal support values (BI/ML) are represented on the BI tree. Some branches have been shortened with each //= 0.04 substitutions per site.
Fig. 3 in The neglected diversity: Description and molecular characterisation of Trypanosoma haploblephari Yeld and Smit, 2006 from endemic catsharks (Scyliorhinidae) in South Africa, the first trypanosome sequence data from sharks globally
Fig. 3. Micrographs of Trypanosoma haploblephari (Yeld and Smit, 2006) morphotype A (A–C) and T. haploblephari morphotype B (D–F) in Giemsa-stained blood films of Haploblepharus pictus and Poroderma pantherinum, respectively. Blood stage with kinetoplast (k) and undulating membrane (μm) visible (A–C); slender forms (B, E); presence of a flagellum (f) in deeply stained individuals (C, F). Scale bar: 10 μm.
Fig. 2 in The neglected diversity: Description and molecular characterisation of Trypanosoma haploblephari Yeld and Smit, 2006 from endemic catsharks (Scyliorhinidae) in South Africa, the first trypanosome sequence data from sharks globally
Fig. 2. Line drawing of Trypanosoma haploblephari (Yeld and Smit, 2006) from the host Poroderma pantherinum (Slide HE18-18) next to a drawing of a red blood cell.
Fig. 2 in Wide geographic distribution of overlooked parasites: Rare Microsporidia in Gammarus balcanicus, a species complex with a high rate of endemism
Fig. 2. Bayesian phylogenetic reconstruction of Microsporidia based on partial small ribosomal subunit rDNA alignment (Supplementary data 1). Labels in bold and in blue frames are parasites of Gammarus balcanicus found in the present study. These labels show the name of the parasite (in case of described species) or in the case of undescribed taxa the name consist of: M. sp (= Microsporidium sp.) followed by clade number sensu Vossbrinck and Debrunner-Vossbrinck (2005), MOTU, haplogroup number (e.g. b01, b02), then the country where it was found (two letter ISO code, see Table S1), the number of infected populations (=pop.), and the total number of infected individuals (=ind.). Labels with accession numbers are parasite sequences taken from GenBank. These labels show the accession number, the parasite name given in the associated publication, the order of the host (except for amphipod hosts where the family is provided). Microsporidia clade numbers are as in Vossbrinck and Debrunner-Vossbrinck (2005). Branches are collapsed for the two genera Nosema and Dictyocoela (triangle sizes not reflecting actual size). Abbreviation: PP, Bayesian posterior probability. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)
Fig. 1 in Wide geographic distribution of overlooked parasites: Rare Microsporidia in Gammarus balcanicus, a species complex with a high rate of endemism
Fig. 1. Gammarus balcanicus sampling sites. Sites are identified by black dots with numbers as in Table S1 (87). See Additional Table S1 for details (e.g. sampling sizes, GPS coordinates). Countries identified with ISO code. Map created by authors using Qgis 2.18.4 (QGIS Development Team 2009).
Fig. 3 in Wide geographic distribution of overlooked parasites: Rare Microsporidia in Gammarus balcanicus, a species complex with a high rate of endemism
Fig. 3. Geographic distribution of the main rare Microsporidia infecting Gammarus balcanicus, showing their occurrence in other gammarid species over Europe. Each map (A–H) refers to the parasite taxa presented in the bottom-right inset. The host and geographic range of the Microsporidia based on this study and 1) literature data: Terry et al. (2004); Wattier et al. (2007); Krebes et al. (2010); Ovcharenko et al. (2010); Bacela-Spychalska et al. (2012); Rode et al. (2013); Grabner et al., 2014; 2015; 2017; Bojko et al. (2015); 2017; 2018; Weigand et al. (2016); Quiles et al. (2019); 2) Gen Bank sequences: MT645708 (Chen,Y. and Jiang, H. direct submission); KP699690 (Bacela-Spychalska, K. direct submission) and 3) Bacela and Ovcharenko, unpublished data.
Fig. 5 in A new endemic genus of eomyid rodents from the early Miocene of Japan
Fig. 5. Time-scaled phylogeny of eomyid rodents and paleogeography of Japan. A. Time-scaled 50% majority-rule tree of eomyid rodents, using the "equal" scaling method. B. Schematic paleogeography of the eastern margin of Asia from the Oligocene to the middle Miocene. Noda and Goto (2004) and NUMO (2004) were referred for the schematic figure, both of which compiled paleogeographic and tectonic information from the primary literatures cited therein. Black lines with shaded area indicate shorelines and land masses. Light gray lines show current coastlines of both Japan and east Asia. Note that Japan was part of the continent during the late Oligocene and progressively drifted during the Miocene. More details are provided in the text.
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Allen Brain Atlas
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Annotated Behaviour and Observability Dataset (ABODe)
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DANDI Archive for NWB datasets
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International Brain Laboratory public data
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OpenNeuro
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