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Figure. Observed (S obs) and estimated species richness for Chao 2, Jackknife 2, and Bootstrap, calculated for Lumbricidae in East Serbia. Vertical dashed lines represent 50%, 75%, and 100% of the sampling effort, respectively. in A nonparametric approach in quantifying species richness of Lumbricidae in East Serbia, Balkan Peninsula
Figure. Observed (S obs) and estimated species richness for Chao 2, Jackknife 2, and Bootstrap, calculated for Lumbricidae in East Serbia. Vertical dashed lines represent 50%, 75%, and 100% of the sampling effort, respectively.
Figure. Measurement data plotted for all nestlings as a function of age for the black stork: a) wing length (WL), b) head length (HL), c) bill length (BL), and d) tarsus length. in Age estimation of black stork (Ciconia nigra) nestlings from wing, bill, head, and tarsus lengths at the time of ringing
Figure. Measurement data plotted for all nestlings as a function of age for the black stork: a) wing length (WL), b) head length (HL), c) bill length (BL), and d) tarsus length.
Figure. Phylogram showing phylogenetic relationships estimated using maximum likelihood analysis of 16S rRNA and COXI gene revealed the grouping of Orthochirus iranus, O. farzanpay, O. stockwelli, O. zagrosensis, O. innesi (JQ514244.1 Morocco), and O. bicolor (KT716038.1 India), with the outgroup species Androctonus crassicauda (FJ217732). in A study of genetic diversity among different population of Orthochirus sp. based on cytochrome C oxidase subunit I and 16srRNA sequencing
Figure. Phylogram showing phylogenetic relationships estimated using maximum likelihood analysis of 16S rRNA and COXI gene revealed the grouping of Orthochirus iranus, O. farzanpay, O. stockwelli, O. zagrosensis, O. innesi (JQ514244.1 Morocco), and O. bicolor (KT716038.1 India), with the outgroup species Androctonus crassicauda (FJ217732).
Figure 4 in Estimation of individual growth of the violet oyster Chama coralloides Reeve, 1846 (Bivalvia: Venerida) using Schnute model cases
Figure 4. Fitted growth curves for the best cases of the Schnute model for a population of C. coralloides in Acapulco, Guerrero, Mexico (* indicates the best model).
Figure 2 in Estimation of individual growth of the violet oyster Chama coralloides Reeve, 1846 (Bivalvia: Venerida) using Schnute model cases
Figure 2. Monthly frequency distribution of lengths (bars) and modal groups (curves) for C. coralloides in Acapulco, Guerrero, Mexico.
Fig. 2 in Assessment Of Census Techniques For Estimating Density And Biomass Of Gibbons (Primates: Hylobatidae)
Fig. 2. Cumulative number of groups of Müller's gibbon, Hylobates muelleri, as observed during range mapping in Kayan Mentarang National Park (KMNP) and Sungai Wain protection forest (SWPF), East Kalimantan, Indonesia.
Fig. 1 in Assessment Of Census Techniques For Estimating Density And Biomass Of Gibbons (Primates: Hylobatidae)
Fig. 1. The island of Borneo showing the location of the two study areas. Grey shading indicates the area in which range mapping of all gibbon groups was executed, the straight lines indicate the transects, and the triangles indicate the listening positions from which the fixed point counts were made.
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.
Glacial-interglacial Circumpolar Deep Water temperatures during the last 800,000 years: estimates from a synthesis of bottom water temperature reconstructions
<p>Data used for our paper "Glacial-interglacial Circumpolar Deep Water temperatures during the last 800,000 years: estimates from a synthesis of bottom water temperature reconstructions" published in Climate of the Past (https://doi.org/10.5194/cp-20-2055-2024).</p> <p>Please see the paper for full details, or email us for further info (dcha@norceresearch.no).</p>
Fig. 4 in Persistence of snake carcasses on roads and its potential effect on estimating roadkills in a megadiverse country
Fig. 4. Survival curves (i.e., probability of persistence on the road) for snake carcasses on primary and secondary roads in the municipality of Filandia, department of Quindío, Central Andes of Colombia. Kaplan-Meier estimates based on a sample size N = 81 snake carcasses.
Fig. 2 in Persistence of snake carcasses on roads and its potential effect on estimating roadkills in a megadiverse country
Fig. 2. Images of some species of snakes present in the study area and used in the field experiments. (A) Mastigodryas boddaerti, (B) Tantilla melanocephala, (C) Dipsas sanctijoannis, (D) Erythrolamprus epinephelus, (E) Leptodeira annulata, (F) Oxyrophus petolarius. Photos by Lina M. Robayo-Palacio (A), Fernando Vargas-Salinas (B–D), Ana María Ospina-L (E), and Wolfgang Buitrago-González (F).
Fig. 1 in Persistence of snake carcasses on roads and its potential effect on estimating roadkills in a megadiverse country
Fig. 1. Geographic location of the study area. Primary road (Autopista del Café) and the secondary road connecting Autopista del Café with the town of Filandia in the department of Quindío, Central Andes of Colombia. Adapted from SIG Quindío 2016. http://190.85.164.56/sigquindioiii/
Fig. 3 in Persistence of snake carcasses on roads and its potential effect on estimating roadkills in a megadiverse country
Fig. 3. (A) Relationship between weight and body length (Ln = natural logarithm) of snake carcasses used in this study. (B) Relationship between body length of snake carcasses and their persistence time on two roads with different levels of vehicular traffic.
Fig. 4 in Population Estimates And Distribution Patterns Of Irrawaddy Dolphins (Orcaella Brevirostris) And Indo-Pacific Finless Porpoises (Neophocaena Phocaenoides) In The Kuching Bay, Sarawak
Fig. 4. Mapping of selected re-sighted Irrawaddy dolphins represented by photographs of the right sides of their dorsal fins in the Kuching Bay area.
Fig. 3 in Population Estimates And Distribution Patterns Of Irrawaddy Dolphins (Orcaella Brevirostris) And Indo-Pacific Finless Porpoises (Neophocaena Phocaenoides) In The Kuching Bay, Sarawak
Fig. 3. Relative densities for Irrawaddy dolphins (a) and finless porpoises (b). Densities are represented as the number of sightings per km searched in 2 × 2 km grid cells. This includes all on-effort sightings and all effort tracks from the start of the project in Jun.2008 through Oct. 2011.
Fig. 2 in Population Estimates And Distribution Patterns Of Irrawaddy Dolphins (Orcaella Brevirostris) And Indo-Pacific Finless Porpoises (Neophocaena Phocaenoides) In The Kuching Bay, Sarawak
Fig. 2. Distribution of on-effort sightings made during 2010–2011 DISTANCE surveys of the Kuching area. Sea conditions and logistical constraints limited survey coverage of the upper Northwestern most corner of the Santubong-Salak block.
Fig. 1 in Population Estimates And Distribution Patterns Of Irrawaddy Dolphins (Orcaella Brevirostris) And Indo-Pacific Finless Porpoises (Neophocaena Phocaenoides) In The Kuching Bay, Sarawak
Fig. 1. Kuching area survey "strata". Shapes for areas were created in Google Earth, creating slight mis-match with the base maps used in ArcGIS.
Figure 3 in Size estimation of Synbranchus marmoratus and Synbranchus madeirae (Teleostei) based on isolated cranial and post-cranial bones
Figure 3. – Map of north-central Chile showing the oceanic islands and Chañaral Island where Pseudocaranx chilensis was sighted.
Figure 2 in Size estimation of Synbranchus marmoratus and Synbranchus madeirae (Teleostei) based on isolated cranial and post-cranial bones
Figure 2. – Individual Pseudocaranx chilensis swimming over the kelp bed at Chañaral Island (depth ~ 5 m).
ScienceDex guides
Understand access before you commit
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.