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FIGURE 2 in Two new critically endangered species of Vellozia (Velloziaceae) from the Campos Rupestres of Espinhaço Range, Brazil
FIGURE 2. Vellozia flavida Mello-Silva ex Magri. A: Habit. B: Detail of the fruit. C: Detail of the flower and immature fruit. Credit of photos A: R.A. Magri; B and C: R.B. Almeida.
FIGURE 4 in Two new critically endangered species of Vellozia (Velloziaceae) from the Campos Rupestres of Espinhaço Range, Brazil
FIGURE 4. Vellozia formosa Mello-Silva ex Magri. A and B: General aspect of the plant. C: apical portion of leaf blade showing the indument. D: detail of the hypanthial emergences. Illustration based on specimen R. Mello-Silva 4370 (SPF).
FIGURE 1 in Two new critically endangered species of Vellozia (Velloziaceae) from the Campos Rupestres of Espinhaço Range, Brazil
FIGURE 1. Vellozia flavida Mello-Silva ex Magri. A and B: General aspect of the plant. C: apical portion of the leaf blade. D: detail of the hypanthial emergences. Illustration based on specimen R.B. Almeida 841 (SPF).
FIGURE 1. Cheniella tsoongii X. Peng, K. W. Jiang & T. Y in Cheniella tsoongii (Leguminosae: Cercidoideae), a rare, critically endangered new species from southern China
FIGURE 1. Cheniella tsoongii X. Peng, K. W. Jiang & T. Y. Tu, sp. nov. A. Habitat; B. Reproductive branch; C. Leaves and branches; D. Tendrils; E. Stipules; F. Young inflorescence; G. Young flower; H. Old flower; I. Young inflorescence, showing bracts and bracteoles; J. Young inflorescence, showing hypanthia; K. Bud; L. Lateral view of a flower, showing the reflexed calyx lobes and hypanthium greatly shorter than pedicel; M. Adaxial surface of leaf; N. Abaxial surface of leaf; O. Young legume; P. Mature legume. Scale bar in K, L, M, N, O and P = 1 cm. Photographs taken by Zhi Xie (A–D, G, J, P); Tie-Yao Tu (E, F, H, I, K, L); Xia Peng (M–O).
FIG. 2 in Discerning the Environmental Drivers of Annual Migrations in an Endangered Amphibian
FIG. 2. Comparison of arrival dates for male and female flatwoods salamanders. Plots are standardized from 1 October and separated by year, i.e., 10–11 is the fall 2010–spring 2011 breeding season. Within year comparisons are made with Wilcoxon rank-sum tests.
FIG. 1 in Discerning the Environmental Drivers of Annual Migrations in an Endangered Amphibian
FIG. 1. Daily counts of individuals as a proportion of the total number of individuals available for capture for each year. Major tick marks are set at January 1, and minor tick marks are months.
FIG. 3 in Otolith Microstructure Analysis Elucidates Spawning and Early Life Histories of Federally Endangered Fishes in the San Juan River
FIG. 3. Razorback Sucker age as a function of length (SL). Colored dots indicate otolith ages, and black squares are predicted ages produced from the linear growth function.
FIG. 1. Colorado Pikeminnow and Razorback Sucker larvae for this study were selected from 2009 in Otolith Microstructure Analysis Elucidates Spawning and Early Life Histories of Federally Endangered Fishes in the San Juan River
FIG. 1. Colorado Pikeminnow and Razorback Sucker larvae for this study were selected from 2009 to 2017 larval fish collections made in the San Juan River between reach 6, near Farmington, NM, and reach 1, near the terminus of the San Juan River in Lake Powell.
FIG. 4 in Otolith Microstructure Analysis Elucidates Spawning and Early Life Histories of Federally Endangered Fishes in the San Juan River
FIG. 4. Back-calculated spawn dates of Colorado Pikeminnows produced from otolith ages (Plot B: Actual), from the transformed linear equations (Plot A: Best-fit), and from the published function (Nesler et al., 1988; Plot C: Published). Data are from larvae collected from 2010 to 2017 in the San Juan River. Dashed gray vertical bars denote weekly intervals.
Figure 4 in First ecological assessment of the endangered Lichtenfelder's Tiger Gecko (Goniurosaurus lichtenfelderi) from northern Vietnam: micro-habitat and macro-climatic niche comparisons between island and mainland populations
Figure 4. (A) Substrate types between island and mainland populations of Goniurosaurus lichtenfelderi; (B) Number of observed individuals at positions (in or out) in different time intervals; (C) Elevations resided by island and mainland populations; (D) Distances from the observed animal to the near stream shore among four study areas.
Figure 2 in Distribution of tiger salamanders in northern Sonora, Mexico: comparison of sampling methods and possible implications for an endangered subspecies
Figure 2. Relationship between mean volume filtered and mean DNA index (±95% confidence interval) for sites where we detected Western Tiger Salamanders (Ambystoma mavortium) with eDNA methods. For every 1% increase in volume of water filtered, DNA recovered decreased by 1.42% (DNA Index = e1.54 [95%CI = 4.14] × Volume (ml) −1.42 [95%CI = 0.80]; R2 = 0.25).
Figure 3 in Distribution of tiger salamanders in northern Sonora, Mexico: comparison of sampling methods and possible implications for an endangered subspecies
Figure 3. Effect of total aquatic vegetation (standardized) on detection of Western Tiger Salamanders (Ambystoma mavortium; ±95% confidence interval), based on all sampling methods. Total aquatic vegetation is the sum of percent cover of emergent vegetation, submerged vegetation, and algae.
Figure 3 in First ecological assessment of the endangered Lichtenfelder's Tiger Gecko (Goniurosaurus lichtenfelderi) from northern Vietnam: micro-habitat and macro-climatic niche comparisons between island and mainland populations
Figure 3. Micro-habitat characteristics of Goniurosaurus lichtenfelderi (A) Substrate temperature; (B) Canopy coverage; (C) Height above the ground in relation to the Snout-Vent Length (From low to high levels mentioned the frequency of captured animals); (D) Stream section type; (E) Surface substrate condition; (F) Activity status.
Figure 1 in Distribution of tiger salamanders in northern Sonora, Mexico: comparison of sampling methods and possible implications for an endangered subspecies
Figure 1. Waterbodies sampled for Western Tiger Salamanders (Ambystoma mavortium) and sub-species in northern Sonora, Mexico, during 2015-2018. Yellow circles indicate locations where salamanders were estimated to be present, white circles indicate where salamanders were not detected, and turquoise triangles indicate sites where Jones et al. (1988) sampled in 1983 and did not detect A. mavortium. The red star indicates the approximate location of Cananea, Sonora.
Figure 6 in First ecological assessment of the endangered Lichtenfelder's Tiger Gecko (Goniurosaurus lichtenfelderi) from northern Vietnam: micro-habitat and macro-climatic niche comparisons between island and mainland populations
Figure 6. Comparisons of macro-climatic niches of Goniurosaurus lichtenfelderi between island and mainland populations. (A) Climate niche space of the mainland population; (B) Climate niche space of the mainland population along the first two axes of the PCA-env (The solid (100%) and dashed contour (50%) lines illustrate the available macro-climate space); (C) The contribution of 19 climatic variables for loading PCA-env axes and the percentage of inertia explained by axes one and two.
Figure 5 in First ecological assessment of the endangered Lichtenfelder's Tiger Gecko (Goniurosaurus lichtenfelderi) from northern Vietnam: micro-habitat and macro-climatic niche comparisons between island and mainland populations
Figure 5. (A) Scatterplot of all variable groups for the first (Dim1) and second (Dim2) axes in the Multiple factor analysis (MFA) (green triangles as inactive groups, red triangles as active groups or variables); (B) Scatterplot of all qualitative variables in the Multiple correspondence analysis (MCA); (C) The first four important variables of the Dim1; and (D) The Dim2; (E) Scatter diagram illustrating the micro-habitat niche space of island and mainland populations.
Figure 1 in First ecological assessment of the endangered Lichtenfelder's Tiger Gecko (Goniurosaurus lichtenfelderi) from northern Vietnam: micro-habitat and macro-climatic niche comparisons between island and mainland populations
Figure 1. Records of Goniurosaurus lichtenfelderi (orange circles – surveyed locations; blue green circles – other recorded occurrences); (1): Bai Tu Long National Park, Quang Ninh Province (2): Chi Linh District, Hai Duong Province, (3): Yen Tu Mountain, Quang Ninh Province, (4): Tay Yen Tu Nature Reserve, Bac Giang Province. The background depicts elevation in northern Vietnam and southern China (from dark blue to red indicating higher elevation).
Figure 2 in First ecological assessment of the endangered Lichtenfelder's Tiger Gecko (Goniurosaurus lichtenfelderi) from northern Vietnam: micro-habitat and macro-climatic niche comparisons between island and mainland populations
Figure 2. (A) Natural micro-habitat of Goniurosaurus lichtenfelderi; (B) An adult male resting on a moss-rock substrate.
Figure 2 in Remote sensing and citizen science to characterize the ecological niche of an endemic and endangered Costa Rican poison frog
Figure 2. Land cover classification of the study area in the South Pacific of Costa Rica for 2019 using Sentinel-2 spatial data.
Figure 1 in Remote sensing and citizen science to characterize the ecological niche of an endemic and endangered Costa Rican poison frog
Figure 1. Map of the study area in the South Pacific of Costa Rica (1:1,250,000 scale and Coordinate Reference System (CRS) WGS84) for the analysis of the ecological niche of P. vittatus using data generated during 2020. Main towns are shown. Large protected areas are represented by their management category: 1: Corcovado National Park; 2: Piedras Blancas National Park; 3: Golfo Dulce Forest Reserve; 4: Paso de la Danta Biological Corridor. Sources: Costa Rica Atlas 2014, Costa Rica Conservation Areas National System (SINAC) 2016 and 2020. Photograph of Phyllobates vittatus by Marina Garrido-Priego.
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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.