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19,493 results for “Populism”
Fig. 1 in External Factors Determining The Reproductive Periodicity In A Tropical Population Of The Hairy Crab Pilumnus Vespertilio (Decapoda: Brachyura: Pilumnidae)
Fig. 1. Monthly frequency variation of females of Pilumnus vespertilio collected at Inhaca Island from January to December 2002.
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. 3 in Ecological, parasitological and individual determinants of plasma neopterin levels in a natural mandrill population
Fig. 3. Plasma neopterin concentrations (raw values) in relation to P. Gonderi parasitaemia in adult males.
Fig. 1 in Ecological, parasitological and individual determinants of plasma neopterin levels in a natural mandrill population
Fig. 1. Plasma neopterin concentrations (raw values) in relation to individual sex. The bottom and top of the box respectively represent the 25th and 75th quartiles, and the bold horizontal line the median. Whiskers show the interquartile range. Open squares indicate the mean of the distribution. Comparisons are denoted by "*" if significant.
Fig. 2. a in Not playing by the rules: Unusual patterns in the epidemiology of parasites in a natural population of feral horses (Equus caballus) on Sable Island, Canada
Fig. 2. a) Dictyocaulus arnfieldi first-stage larvae showing typical granular appearance and beginning of cuticular separation b) closer view of tail showing stylet, or spear.
Fig. 1 in Not playing by the rules: Unusual patterns in the epidemiology of parasites in a natural population of feral horses (Equus caballus) on Sable Island, Canada
Fig. 1. Map of Sable Island, Canada, which is about 50 km long, 1 km wide at its widest point, and in total, 34 km2 (from Gold et al., 2019).
Fig. 3 in Not playing by the rules: Unusual patterns in the epidemiology of parasites in a natural population of feral horses (Equus caballus) on Sable Island, Canada
Fig. 3. Proportions of third-stage larvae of large and small strongyle species cultured from feces of 81 Sable Island horses in summer 2014, showing an unusual dominance of S. equinus in adult horses. Larvae with a rhabditiform pharynx were rare in young (1–3 years) and adult horses (≥3 years), but common in foals, which could represent larvae of Strongyloides westeri.
Fig. 2 in Effects of introduced sika deer (Cervus nippon) and population control activity on the distribution of Haemaphysalis ticks in an island environment
Fig. 2. Seasonal changes in tick abundance of the dominant species (A) H. megaspinosa, (B) H. longicornis, and (C) H. cornigera on Niijima Island. (Broken line with black dot: Larvae, Dotted-dashes line with back triangles: Nymphs, Solid line with crosses: Adults).
Fig. 3 in Effects of introduced sika deer (Cervus nippon) and population control activity on the distribution of Haemaphysalis ticks in an island environment
Fig. 3. Statistical summary of the abundances of H. megaspinosa larvae. (A) Days since the last sika deer was captured in August–November, (B) days since the last sika deer was captured in August–November for the high sika deer group, and (C) days since the last sika deer was captured in August–November for the low sika deer group. (X mark inside box: mean, lower and upper side of the box: first and third quartiles, line inside box: median, lower and upper error lines 10th and 90th percentiles, respectively, circles: data falling outside 10th and 90th percentiles).
Fig. 1 in Effects of introduced sika deer (Cervus nippon) and population control activity on the distribution of Haemaphysalis ticks in an island environment
Fig. 1. Map of Niijima Island, with locations of foot snare traps (black circle), and tick collection routes for the tick survey conducted June, August, and November of 2018 and February of 2019 (orange area). (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 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).
Fig. 1 in Thorius narismagnus (Amphibia: Plethodontidae): rediscovery at the type locality and detection of a new population
Fig. 1. Locations of historical collection localities and the new localities of Thorius narismagnus in Los Tuxtlas region, Mexico.
Fig. 4. Chromosomes 9 and 11 from different L. spenceri populations. Three representative chromosomes from each animal demonstrate a in The critically endangered species Litoria spenceri demonstrates subpopulation karyotype diversity
Fig. 4. Chromosomes 9 and 11 from different L. spenceri populations. Three representative chromosomes from each animal demonstrate a highly conserved DAPI negative region in the long arms of chromosome 9. A DAPI negative region is observed in the long arm of chromosome 11, but only in the Central Site juveniles and in only one matched chromosome of the Northern Site x Central Site tadpole hybrid. Arrows indicate the chromosome 11 DAPI negative region. Asterisks indicate the paired submetacentric chromosome 11 matched pair of the Northern Site x Central Site tadpole hybrid.
Fig. 3 in Range extension and highest elevational populations of Natrix tessellata in Slovakia
Fig. 3. Individuals of Natrix tessellata from the location in Lisková. (A) Adult female dorsal view. (B) Same individual in ventral view. (C) Overall view on juvenile individual. (D) Detail of the head on the same individual.
Fig. 1 in Range extension and highest elevational populations of Natrix tessellata in Slovakia
Fig. 1. Distribution and range extension of Natrix tessellata in Slovakia. (A) Locations surveyed in the vicinity of Ružomberok and Liptovská Basin. (B) Records of the species in the country. Black line shows cut out area of new locations while (A) is the same area but enlarged. 1 – Ružomberok, 2 – Lisková, 3 – Ružomberok – Rybárpole, 4 – Liptovská Teplá, 5 – Liptovská Mara, 6 – Ružomberok, 7 – Hrboltová, 8 – Hubová, 9 – Stankovany, 10 – Kraľovany, 11 – Vyšné Matejkovo.
Fig. 2 in Range extension and highest elevational populations of Natrix tessellata in Slovakia
Fig. 2. Locations and habitat of Natrix tessellata near Ružomberok. (A) Location in Ružomberok where the first individuals were observed. (B) (C) (D) View on the habitat near Lisková village.
Figure4 in Population Status and Nesting Behavior of Red-Headed Vultures (Sarcogyps Calvus) at Dhorfirdi, Tanahun District, Nepal
Figure4. Change of shift during incubation by a pair of vultures alternately one after another and successfully hatching of the egg shown by (a) incubation by female parent (b) arrival of male parent in the nest (c) change of shift by flying away of the female parent (d) turning of egg by male parent after foraging (e) continue incubation by the male parent as the female parent moves away (e) hatching of egg into the juvenile S. calvus in the nest
ScienceDex guides
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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.