Find research datasets worth reusing
Search datasets from major research repositories and use ShareScore to quickly assess how well each record supports discovery, access, and reuse.
7,849
datasets available to search
ShareScore release 0.9.0
Dataset results
7,849 results for “Conservancy”
FIGURE 4 in Diversity and distribution of Lentibulariaceae in Bahia state, Brazil: implications for phytogeography and conservation
FIGURE 4. Distribution of Lentibulariaceae species in Protected Areas north (above) and southwest (below) of Chapada Diamantina. APA = Environmental Protection Area, ARIE = Area of Relevant Ecological Interest, MONA = Natural Monument, PE = State Park, PNM = Municipal Natural Park.
FIGURE A1 in Diversity and distribution of Lentibulariaceae in Bahia state, Brazil: implications for phytogeography and conservation
FIGURE A1. Protected Areas in Bahia state that cover the natural distribution of Lentibulariaceae species. Strictly Protected Areas: MONA = Natural Monument (II), PARNA = National Park (II), PE = State Park (II), PNM = Municipal Natural Park (II), REBIO = Biological Reserve (Ia), REVIS = Wildlife Refuge (III). Areas of Sustainable Use: APA = Environmental Protection Area (V), ARIE = Area of Relevant Ecological Interest (IV), PM = City Park (V), RESEX = Extractive Reserve (VI), RPPN = Private Reserve of Natural Heritage (IV).
FIGURE 7. A–B. U in Diversity and distribution of Lentibulariaceae in Bahia state, Brazil: implications for phytogeography and conservation
FIGURE 7. A–B. U. longifolia; C. U. myriocista; D. U. nana; E–F. U. nelumbifolia; G. U. neottioides; H. U. nephrophylla; I. U. nervosa; J. U. parthenopipes; K. U. poconensis; L. U. praelonga; M–N. U. purpureocaerulea; O–P. U. pusilla; Q. U. resupinata; R. U. rostrata; S. U. simulans; T. U. subulata; U–V. U. trichophylla; W. U. tricolor; X–Y. U. triloba. (Photos A, B, D, G, I, J, L, N, O–Q, S, T, W–Y by F.M. Guedes; C, U, V by S. Guzmán; E, F by N.G. Silva; H by J. Allen; K by M.F. Cardoso; M by P.M. Gonella; R by N. Rebbert).
FIGURE 6. A in Diversity and distribution of Lentibulariaceae in Bahia state, Brazil: implications for phytogeography and conservation
FIGURE 6. A. Genlisea aurea; B. G. exhibitionista; C. G. filiformis; D. G. guianensis; E. G. lobata; F. G. repens; G. G. tuberosa; H. G. uncinata; I. Utricularia adpressa; J–K. U. amethystina; L–M. U. blanchetii; N. U. breviscapa; O. U. costata; P. U. cucullata; Q. U. erectiflora; R. U. flaccida; S. U. foliosa; T. U. gibba; U. U. guyanensis; V. U. hydrocarpa; W. U. jamesoniana; X. U. juncea; Y. U. laxa. (Photos A by J.C. Zamora; B by C. Rohrbacher; C by Z. Miranda; D, E, G, H by P.M. Gonella; F, Y by H. Dolsan; I–M, Q, R, U, X by F.M. Guedes; N, O by J. Fabricante; P by M. Hopkins; S. by Y. Canalli; T by A. Nepomuceno; V by G.S. Garcia; W by Y. Gouveia).
FIGURE 3 in Two new species and a new record of Epidendrum (Orchidaceae) from the Carpish Montane Forest Regional Conservation Area, Peru
FIGURE 3. Lankester Composite Digital Plate of Epidendrum churubambense Ocupa, J.Duarte, E.Santiago & Hágsater. A. Habit. B. Flower. C. Dissected perianth. D. Lip, column and ovary, lateral view. E. Column, lateral and ventral view. F. Anther cap and pollinarium. Prepared by L. Ocupa Horna from the holotype.
FIGURE 5 in Diversity and distribution of Lentibulariaceae in Bahia state, Brazil: implications for phytogeography and conservation
FIGURE 5. Distribution of Lentibulariaceae species in Protected Areas at northern and southern coast of Bahia. APA = Environmental Protection Area, ARIE = Area of Relevant Ecological Interest, MONA = Natural Monument, PARNA = National Park, PE = State Park, PM = City Park, PNM = Municipal Natural Park, REBIO = Biological Reserve, RESEX = Extractive Reserve, REVIS = Wildlife Refuge, RPPN = Private Reserve of Natural Heritage.
FIGURE 7 in Two new species and a new record of Epidendrum (Orchidaceae) from the Carpish Montane Forest Regional Conservation Area, Peru
FIGURE 7. Lankester Composite Digital Plate of Epidendrum sanctae-rosae Hágsater, Sauleda, Uribe Vélez & E.Santiago. A. Habit. B. Floral bract. C. Flower. D. Dissected perianth. E. Lip, column and ovary, lateral view and longitudinal section. F. Column. G. Anther cap and pollinarium. Prepared by L. Ocupa Horna from Peruvian specimen (L. Ocupa 300 [USM]).
FIGURE 6 in Two new species and a new record of Epidendrum (Orchidaceae) from the Carpish Montane Forest Regional Conservation Area, Peru
FIGURE 6. Species of Soratae subgroup, Scabrum group, similar to Epidendrum unchogense. A. Epidendrum unchugense Ocupa & E.Santiago. B. Epidendrum llatasii Hágsater, A.G.Diaz & E.Santiago. C. Epidendrum carpishense Hágsater, D.Trujillo & E.Santiago. D. Epidendrum labrychilum Hágsater, Edquén & E.Santiago. Photographs by: L. Ocupa (A) (L. Ocupa 299 [USM]); A. G. Díaz (B) (A. Díaz 83 [HUT]); D. Trujillo (C) (D. Trujillo 78 [HURP]); J. Edquén (D) (J. Edquén 400 [HURP]).
The minimum land area requiring conservation attention to safeguard biodiversity
<p><span>Ambitious conservation efforts are needed to stop the global biodiversity crisis. Here, we estimate the minimum land area to secure important biodiversity areas, ecologically intact areas, and optimal locations for representation of species ranges and ecoregions. We discover that at least 64 million km<sup>2</sup> (44% of terrestrial area) would require conservation attention (ranging from protected areas to land-use policies) to meet this goal. Over 1.8 billion people live on these lands, so responses that promote autonomy, self-determination, equity, and sustainable management for safeguarding biodiversity are essential. Spatially explicit land-use scenarios suggest that 1.3 million km<sup>2</sup> of this land is at risk of being converted to intensive human land-uses by 2030, which requires immediate attention. However, there is a seven-fold difference between the amount of habitat converted under optimistic and pessimistic land-use scenarios, highlighting an opportunity to avert this crisis. Appropriate targets in the post-2020 Global Biodiversity Framework, to encourage conservation of the identified land, would contribute substantially to safeguarding biodiversity.</span></p>
Figure 3 in Distribution, natural history, and conservation of Cambarus dubius in Pennsylvania
Figure 3. Map of the study area in south-western Pennsylvania with Cambarus dubius collection sites (yellow circles), sites with active crayfish burrows (orange circles), and sites without crayfish burrows (red circles).
Figure 2 in Distribution, natural history, and conservation of Cambarus dubius in Pennsylvania
Figure 2. Map of the study area in south-western Pennsylvania with new sites (those not previously surveyed for burrowing crayfish), sites surveyed previously by Loughman et al. (2017), and a historical Ortmann (1905, 1906) site resurveyed by Loughman et al. (2017).
Figure 6 in Distribution, natural history, and conservation of Cambarus dubius in Pennsylvania
Figure 6. Means (red and blue bars), medians (black lines), and standard errors (±) of habitat variables from geographic information system (GIS) databases between sites with crayfish present vs absent. Permutation-based t-tests displayed significant differences (P <0.0024) in variables between sites with C. dubius present vs absent (A–C) and sites with all burrowing crayfish species/burrows present vs absent (D–I). Habitat variables not pictured were not significant.
Figure 1 in Distribution, natural history, and conservation of Cambarus dubius in Pennsylvania
Figure 1. Map of the study area in south-western Pennsylvania. The historical distribution of Cambarus dubius in the state falls between the Chestnut Ridge (1.) and the western extent of the Allegheny Mountains (3.). The Laurel Ridge (2.) is located between the Chestnut Ridge and the Allegheny Mountains.
Figure 5 in Distribution, natural history, and conservation of Cambarus dubius in Pennsylvania
Figure 5. Map of the study area in south-western Pennsylvania showing Cambarus dubius collection sites (blue circles) and sites with active crayfish burrows (orange circles). Four large green spaces and all state game lands are highlighted. Other green spaces include natural areas (n = 3), wild areas (n = 1), public recreational areas (n = 5), state parks (n = 6), easements (n = 2) and a historical site (n = 1). Both Forbes and Gallitzin state forests are non-contiguous. Five major streams and the Quemahoning Reservoir are also highlighted.
Figure 4 in Distribution, natural history, and conservation of Cambarus dubius in Pennsylvania
Figure 4. (a.) Cambarus dubius. (b.) Cambarus dubius burrow with a distinct mud chimney. (c.) Skunk cabbage wetland with Cambarus dubius burrows. (d.) Juvenile Cambarus dubius aggressively attacking baited line used to lure crayfish out of the burrow as described by Loughman et al. (2013).
Data from: A comprehensive evaluation of flowering plant diversity and conservation priority for national park planning in China
<p><span>Establishment of a national park protection system in China, including the latest target proposed to protect at least 30% of the land area, calls for a comprehensive exploration of conservation priorities incorporating multiple diversity facets. We herein evaluate the spatial distribution of Chinese flowering plants from the perspectives of richness, uniqueness, vulnerability, and evolutionary history, by integrating three mega-phylogenies and comprehensive distribution data. </span><span>We </span><span>detect significantly high consistency among hotspots of different diversity measures for Chinese flowering plants, suggesting that multiple facets of evolutionary diversity are concentrically distributed in China. Affording legal protection to these areas is expected to maximize positive conservation outcomes. We propose two integrative diversity indices by incorporating three richness-based and three phylogeny-based measures, respectively. Both methods identify areas with high species richness, but the integrative phylogeny-based index also locates key areas with ancient and unique evolutionary histories </span><span>(e.g.,</span><span> Ailao-Wuliang Mts, </span><span>Dabie Mts, Hainan rainforest, </span><span>Karst area of Yunnan-Guizhou-Guangxi, </span><span>Nanling Mts, and southeast coastal regions)</span><span>. Of all the diversity indices explored, phylogenetic endemism maximizes the incidental protection of other indices in most cases, emphasizing its significance for conservation planning. Finally, 42 priority areas are identified by combining the 5%-criterion hotspots of two integrative indices and the minimum area to protect all threatened species analyzed. These priorities cover only 13.3% of China's land area but host 97.1% of species richness </span><span>(23,394/24,095)</span><span>, 96.5% of endemic species </span><span>(11,841/12,274)</span><span>, 100% of threatened species </span><span>(2,613/2,613)</span><span>, and 99.3% of phylogenetic diversity for flowering plants involved in this study. These frameworks provide a solid scientific basis for national park planning in China.</span></p>
Risk Classification of contaminates sites in Anderstorp using the German Einzelfallbewertung Altlastenstandorte (EB) method from the Hessian Agency for Nature Conservation, Environment and Geology (HLNUG)
<p>This data set includes the documents for risk classifying contaminated sites in Anderstorp, Sweden using the German Einzelfallbewertung Altlastenstandorte (EB) method from the Hessian Agency for Nature Conservation, Environment, and Geology (HLNUG).</p>
A turn in species conservation for hairpin banksias: Demonstration of oversplitting leads to a better management of diversity
<p>We generated SNP genotype data and chloroplast genomic data to test the current taxonomy and infer a population-scale evolutionary scenario for the Hairpin Banksias (<em>B. collina, B. cunninghamii, B. neoanglica, B. spinulosa </em>and <em>B. vincentia</em>) and outgroups using a sample-set comprehensive in its representation of morphological diversity and a two-and-a-half thousand kilometer distribution. Here, we provide an archive of these SNP genotype and chloroplast sequence alignment data.</p>
Supplementary material 1 from: Praz C, Genoud D, Vaucher K, Bénon D, Monks J, Wood TJ (2022) Unexpected levels of cryptic diversity in European bees of the genus Andrena subgenus Taeniandrena (Hymenoptera, Andrenidae): implications for conservation. Journal of Hymenoptera Research 91: 375-428. https://doi.org/10.3897/jhr.91.82761
Table S1. Specimens used in genetic analyses. The unique identifiers are identical to the Sample-ID on BOLD
Conservation genetics of an island-endemic lizard: low Ne and the critical role of intermediate temperatures for genetic connectivity
<p>Island populations are at higher risk of extinction than mainland populations. Therefore, understanding the factors that facilitate connectivity is particularly pressing for the conservation of island taxa. <i>Sceloporus occidentalis becki</i>, the Island Fence Lizard, is an endemic taxon restricted to the Northern Channel Islands, part of a nearshore archipelago in Southern California, USA. Since the Last Glacial Maximum, fence lizard habitat on the Northern Channel Islands has decreased with rising sea levels and increasing temperatures that have reduced the availability of woody vegetation. More recently, the introduction (and subsequent removal) of invasive ungulates over the last 170 years and recovery of vegetation has resulted in further dramatic habitat modification. Given the potential for genetic bottlenecks, the history of habitat alteration, and topographic and landscape complexity, we used landscape and population genetic approaches to characterize patterns of genetic diversity and structure of Island Fence Lizards on Santa Cruz Island, the largest of the Northern Channel Islands. Our analyses revealed shallow population structure across the island, low effective population size (<i>N<sub>e</sub></i> = ~200), and evidence for a recent genetic bottleneck. Landscape genetic analyses showed that connectivity is facilitated by tree canopy cover and shrubland, as well as by intermediate temperatures, emphasizing the importance of woody vegetation and habitats with variable thermal regimes as the climate warms. Combined, these population and landscape genetic analyses suggest that the Island Fence Lizard is of greater conservation concern than currently appreciated, and increased conservation management focus is warranted for this island endemic.</p>
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.