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187 results for “species at risk”

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zenodo44/100

Species diversity and extinction risk of vertebrate pollinators in India

<p>This repository includes the data compiled and used for the study of&nbsp;<strong>&lsquo;Species diversity and extinction risk of vertebrate</strong><br><strong>pollinators in India&rsquo;</strong>. If you use these data, please cite them along&nbsp;with our manuscript:</p> <blockquote> <p>Kallivalappil R., Grattarola F., de Alwis Pitts D., Cotter S.C. &amp; Pincheira-Donoso D. (2024). Species diversity and extinction risk of vertebrate<br>pollinators in India. <em>Biodiversity and Conservation</em>.&nbsp;https://doi.org/10.1007/s10531-024-02848-3</p> </blockquote> <p>&nbsp;</p> <h2>Abstract</h2> <p>Animal pollinators underpin the functioning and persistence of&nbsp;ecosystems globally. However, the vital role of pollination is being&nbsp;progressively eroded by the worldwide decline of pollinator species&nbsp;caused by human-induced environmental degradation, resulting in rising&nbsp;costs to biodiversity, agriculture, and economy. Most studies&nbsp;quantifying pollinator diversity and declines have focused on insects,&nbsp;whereas vertebrate pollinators remain comparatively neglected. Here, we<br>present the first comprehensive study quantifying the macroecological&nbsp;patterns of species richness and extinction risk of bird and mammal&nbsp;pollinators in India, a region of extremely high biodiversity and&nbsp;increasing anthropogenic pressure. Our results reveal that hotspots of&nbsp;mammal pollinator diversity are restricted to the south of the Western&nbsp;Ghats, whereas bird pollinator diversity hotspots are scattered&nbsp;throughout the country. Analyses of hotspots of threatened species<br>(based on the IUCN Red List) show that only mammal pollinators are&nbsp;currently classified as threatened in India, whereas multiple hotspots&nbsp;of population declines were observed for birds, and primarily in the&nbsp;Southwest for mammal pollinators. Our analyses failed to identify a role&nbsp;for species traits as drivers of these patterns, whereas most&nbsp;pollinators appear to be threatened by agriculture, logging and hunting&nbsp;for food, and medicinal purposes. Pollinator endangerment has widescale<br>ecological and economic implications such as reduced food production, plant extinction, loss of functional and genetic diversity, and economic damage. We suggest protection of vertebrate pollinators should be emphasised in active conservation agendas in India.</p> <p>&nbsp;</p> <h2>Files</h2> <h3>Spatial</h3> <ul> <li><code>india.gpkg</code></li> <li><code>birds.gpkg</code></li> <li><code>mammals.gpkg</code></li> <li><code>how_to_read_gpkg_data.R</code></li> </ul> <h3>Phylogenetic</h3> <ul> <li><code>PGLS_phylogeny_birds.nex</code></li> <li><code>PGLS_phylogeny_mammals.nex</code></li> </ul> <h3>Tables</h3> <ul> <li><code>all_bird_traits.csv</code></li> <li><code>all_mammals_traits.csv</code></li> <li><code>threatened_mammals_traits.csv</code></li> <li><code>plant_pollinator_dataset.csv</code></li> <li><code>pollinator_plant_dataset.csv</code></li> <li><code>references.txt</code></li> </ul>

opencc-by-4.0Sep 2024View details →
zenodo44/100

Physiological information in Canadian species at risk recovery strategies (animals)

<p>Summary of physiological information contained in Canadian (animal)&nbsp;species at risk recovery strategies (SARA). For each recovery strategy, the dataset includes the species covered, publication dates, taxonomic classification, the number of times physiology was mentioned, the types of physiological traits included, and the threats the associated organism faces.</p>

opencc-by-4.0Sep 2021View details →
dryad40/100

Risk response towards roads is consistent across multiple species in a temperate forest ecosystem

<p>Roads can have diverse impacts on wildlife species, and while some species may adapt effectively, others may not. Studying multiple species' responses to the same infrastructure in a given area can help understand this variation and reveal the effects of disturbance on the ecology of wildlife communities. This study investigates the behavioural responses of four species with distinctive ecological and behavioural traits to roads in the protected Bohemian Forest Ecosystem in Central Europe: European roe deer (<em>Capreolus capreolus), </em>a<em> </em>solitary herbivore; red deer (<em>Cervus elaphus</em>) a gregarious herbivore; wild boar (<em>Sus scrofa</em>), a gregarious omnivore and Eurasian lynx (<em>Lynx lynx</em>), a solitary large carnivore. We used GPS data gathered from each species to study movement behaviour and habitat selection in relation to roads using an integrated step selection analysis. For all species and sexes, we predicted increased movement rates in response to roads, selection of vegetation cover near roads and open areas after road crossings, and increased road avoidance during the day. We found remarkably similar behavioural responses towards roads across species. The behavioural adaptations to road exposure, such as increased movement rates and selection for vegetation cover, were analogous to responses to natural predation risk. Roads were more strongly avoided during daytime, when traffic volume was high. Road crossings were more frequent at twilight and at night within open areas offering food resources. Gregarious animals exposed to roads favoured stronger road avoidance over faster movements. Ungulates crossed roads more at twilight, coinciding with commuter traffic during winter. Despite differences in the ecology and behaviour of the four species, our results showed similar adaptations towards a common threat. These insights can be used by managers to promote safer road crossings where roads interfere with animals' natural behaviour. The continuous expansion of the global transportation network should be accompanied by efforts to understand and minimise the impact of roads on wildlife to assist wildlife management and ensure conservation.</p>

opencc-zeroMar 2024View details →
zenodo40/100

High-Resolution Vector-borne Disease Infection Risk Mapping with Area-to-Point Kriging and Species Distribution Modeling - Datasets

<p>Datasets and notebooks used in the publication High-Resolution Vector-borne Disease Infection Risk Mapping with Area-to-Point Kriging and Species Distribution Modeling</p>

opencc-by-4.0May 2024View details →
zenodo40/100

Figure 3 in America's Most Wanted Fishes: cataloging risk assessments to prioritize invasive species for management action

Figure 3. The proportion of risk statuses of fish families with four or more species assessed at the extent of Florida. Panel (A) shows the proportion of species with high, moderate, low, multiple, and undetermined risk statuses of assessed species (total number of species evaluated in a family). Panel (B) shows the ratio of assessed to unassessed species in a given family (total species in a family). Total species in a family were obtained from FishBase (Froese and Pauly 2023).

opencc-by-4.0Dec 2023View details →
zenodo40/100

Figure 1 in America's Most Wanted Fishes: cataloging risk assessments to prioritize invasive species for management action

Figure 1. The proportion of risk statuses of fish families with four or more species assessed at the extent of the conterminous U.S. Panel (A) shows the proportion of species with high, moderate, low, multiple, and undetermined risk statuses of assessed species (total number of species evaluated in a family). Panel (B) shows the ratio of assessed to unassessed species in a given family (total species in a family). Total species in a family were obtained from FishBase (Froese and Pauly 2023).

opencc-by-4.0Dec 2023View details →
zenodo40/100

Figure 2 in America's Most Wanted Fishes: cataloging risk assessments to prioritize invasive species for management action

Figure 2. The proportion of risk statuses of fish families with four or more species assessed at the extent of the Great Lakes region. Panel (A) shows the proportion of species with high, moderate, low, multiple, and undetermined risk statuses of assessed species (total number of species evaluated in a family). Panel (B) shows the ratio of assessed to unassessed species in a given family (total species in a family). Total species in a family were obtained from FishBase (Froese and Pauly 2023).

opencc-by-4.0Dec 2023View details →
zenodo40/100

Figure 1 in Developing biosecurity plans for non-native species in marine dependent areas: the role of legislation, risk management and stakeholder engagement

Figure 1. Five-stage approach for risk assessment management of NNS in Shetland, adapted from the ecosystem-based risk management framework (Cormier et al. 2013).

opencc-by-4.0Nov 2021View details →
zenodo40/100

FIGURE 2 in Extinction risk or lack of sampling in a threatened species: Genetic structure and environmental suitability of the neotropical frog Pristimantis penelopus (Anura: Craugastoridae)

FIGURE 2: (Left) Maximum clade credibility tree depicting the phylogenetic position of Pristimantis penelopus within the P. ridens series. Numbers on nodes indicate posterior probabilities. Numbers below nodes represent nodal support using the ultrafast bootstrap (see methods). Asterisks indicate nodal support above 95% in both Bayesian and ML methods. (Right) Haplotype network based on 460 bp of the COI region. Numbers of mutational steps are shown on the lines connecting haplotypes. Colors refer to geographic locations shown in Figure 1.

opencc-by-4.0Mar 2017View details →
zenodo40/100

FIGURE 4 in Extinction risk or lack of sampling in a threatened species: Genetic structure and environmental suitability of the neotropical frog Pristimantis penelopus (Anura: Craugastoridae)

FIGURE 4: Potential distribution of Pristimantis penelopus based on ecological niche modeling (red). Yellow dots represents occurrence localities used to calibrate the model. See main text for details.

opencc-by-4.0Mar 2017View details →
zenodo40/100

FIGURE 1 in Extinction risk or lack of sampling in a threatened species: Genetic structure and environmental suitability of the neotropical frog Pristimantis penelopus (Anura: Craugastoridae)

FIGURE 1: Geographic sampling of Pristimantis penelopus. Colored circles indicate sequenced specimens. Different colors represent the populations used in the genetic analysis (see Figure 2 for color codes).

opencc-by-4.0Mar 2017View details →
zenodo40/100

FIGURE 3 in Extinction risk or lack of sampling in a threatened species: Genetic structure and environmental suitability of the neotropical frog Pristimantis penelopus (Anura: Craugastoridae)

FIGURE 3: Phenotypic variation of Pristimantis penelopus across its distribution. Localitites are shown in Appendix 1.

opencc-by-4.0Mar 2017View details →
zenodo40/100

Figure 4 in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 4. Taxa distribution on ships' hulls of the three studied vessels (Esmeralda, USA and ARG tankers) (a) nMDS showing the taxa assemblages in protected vs. exposed areas of the ships' hulls. (b) Taxa richness in exposed and protected areas of the hulls of the three studied vessels. (c) Relationship between the number of taxa found on the hulls and the number of ports visited by each ship.

opencc-by-4.0Jan 2023View details →
zenodo40/100

Figure 6 in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 6. Distribution of the COI haplotypes of Ciona robusta per sample, with their number indicated in the barplot. For each sample, the number of specimens is indicated in parentheses. The correspondence between the haplotypes found in this study, and those referenced in GenBank is given in Table S3.

opencc-by-4.0Jan 2023View details →
zenodo40/100

Figure 2 in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 2. Location of the different areas of the vessel from which the samples were obtained. Protected areas: sea box, rope guard, water discharge holes, top of the rudder and the Kort nozzle. Exposed areas: bilge keel, the helm in general and the rudder. Modified from Sylvester and MacIsaac (2010).

opencc-by-4.0Jan 2023View details →
zenodo40/100

Figure 5 in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 5. Taxa richness recorded in the Talcahuano port on settlement plates made of different types of materials and maintained at different depths for two months total, considering the two periods of time. Values include averages and ± one standard error.

opencc-by-4.0Jan 2023View details →
zenodo40/100

Figure 1 in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 1. The black circle corresponds to the locality where the sampling was carried out in each type of sampling (ships, settlement plates in the port of Talcahuano and natural substrates in the El Manzano pier).

opencc-by-4.0Jan 2023View details →
zenodo40/100

Figure 3. Graphical representation using a in Investigating the risk of non-indigenous species introduction through ship hulls in Chile

Figure 3. Graphical representation using a nMDS based on Bray-Curtis distances, of the taxa assemblages in each sampling type (ships, settlement plates in the Talcahuano port, and natural substrates at El Manzano pier). Stress value is 0.17.

opencc-by-4.0Jan 2023View details →
zenodo40/100

FIGURE 11 in Uncertainties and risks in delimiting species of Cambeva (Siluriformes: Trichomycteridae) with single-locus methods and geographically restricted data

FIGURE 11 | Bayesian phylogenetic tree of Cambeva species obtained from COI data. The vertical red line shows the coalescent branching process estimated by using the single-threshold model in the GMYC combination 4 (strict clock model vs. a coalescent constant population

opencc-by-4.0Oct 2022View details →
zenodo40/100

FIGURE 7 in Uncertainties and risks in delimiting species of Cambeva (Siluriformes: Trichomycteridae) with single-locus methods and geographically restricted data

FIGURE 7 | Coloration pattern of Cambeva species. (A, B). Cambeva guaraquessaba, UFRGS 24554, 37.0 and 36.9 mm SL, respectively, tributary of Guaraqueçaba River basin, Paranaguá Bay. C–D. Cambeva tupinamba, UFRGS 24550, 63.0 mm SL and 39.4 mm SL, Betari River, Ribeira de Iguape River basin.

opencc-by-4.0Oct 2022View details →

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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.

allen-brain-atlas
neuroscienceopenDocumentation, web resources, and API references are available online.
Last verified 2026-04-30Open record

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.

abode-home-cage
behavioral-neuroscienceopenThe DataShare record exposes download links for annotations, documentation, license text, and the zipped per-snippet data directory.
Last verified 2026-04-30Open record

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.

dandi-nwb
electrophysiologyopenPublished Dandiset metadata and archive endpoints are available through the production DANDI API.
Last verified 2026-04-30Open record

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.

ibl
behavioral-neuroscienceopenPublic sessions can be searched and loaded from the IBL public data server through ONE.
Last verified 2026-04-29Open record

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.

openneuro
neuroscienceopenPublished datasets are available on demand over the internet.
Last verified 2026-04-29Open record