Find research datasets worth reusing

opennotspecifiedMar 2019View details →

FIGURES 6–11 in Stevenia gilasiani sp. nov. (Diptera: Rhinophoridae): the first woodlouse fly with male sexual-patches

FIGURES 6–11. Stevenia gilasiani sp. nov.. 6–8. Holotype ♂. 6. Detail of thorax, showing two postpronotal setae. 7. Abdomen in dorsal view. 8. Abdomen in lateral view, showing the sexual-patches on tergites 3 and 4. 9–11. Details of cuticle and setae composing the sexual-patches, using scanning electron microscopy (SEM) (paratype, MZUR). 9. Sexual-patches of tergite 3 in ventral view. 10. Seta and porous area. 11. Internal surface of cuticle at of the base of a seta composing a sexualpatch, showing the sieve-like structure at level of porous area.

opennotspecifiedMar 2019View details →

FIGURES 2–5 in Stevenia gilasiani sp. nov. (Diptera: Rhinophoridae): the first woodlouse fly with male sexual-patches

FIGURES 2–5. Stevenia gilasiani Ziegler, Gisondi & Cerretti sp. nov. (holotype ♂). 2. Habitus in lateral view. 3. Head in lateral view. 4. Right wing in dorsal view. 5. Head in frontal view.

opencc-by-4.0Jun 2019View details →

Dataset of "how to communicate when submitting patches: an Empirical Study of the Linux Kernel"

This repository includes the data of the paper "How to Communicate when Submitting Patches: an Empirical Study of the Linux Kernel". It contains three parts: 1) Related online documents. 2) Original questionnaire of the survey. 3) Survey results.

FIGURES 79–84 in Orthoseira variabilis sp. nov., a new diatom from a snow patch in Potter Cove, King George Island, Antarctica

FIGURES 79–84. Orthoseira variabilis sp. nov. SEM. Girdle elements. Fig. 79. Valvocopula with internal silica thickening attached to valve. Fig. 80. Detached open valvocopula. Fig. 81. Broken frustule in internal view showing valve and attached valvocopula with thickened pars interior and poroids. Fig. 82. Open, ligulate copula. Fig. 83. Detail of a copula showing ligula. Fig. 84. Detail of a copula showing tiny poroids and fimbriae. Scale bar: 10 µm (Figs 79–80, 82), 5 µm (Figs 81, 83), 2 µm (Fig. 84).

FIGURES 85–94 in Orthoseira variabilis sp. nov., a new diatom from a snow patch in Potter Cove, King George Island, Antarctica

FIGURES 85–94. Orthoseira variabilis sp. nov. Figs 85–92. LM. Initial cells. Figs 85–87. Girdle view. Figs 88–92. Valve view. Figs 93–94. SEM. Initial valve. Fig. 93. General view. Fig. 94. Detail of central area of specimen in Fig. 93, rotated; note the numerous and incompletely developed carinoportulae. Figures marked with "=" are the same valves with a different focus. Scale bar: 10 µm (Figs 85–93; scale bar is the same for Figs 85–92), 5 µm (Fig. 94).

FIGURES 61–65 in Orthoseira variabilis sp. nov., a new diatom from a snow patch in Potter Cove, King George Island, Antarctica

FIGURES 61–65. Orthoseira variabilis sp. nov. SEM. Specimens in girdle view. Fig. 61. Valve with pore field (arrow) and raised interstriae on the mantle. Note the collum (white arrowhead) separated from the mantle striae by a smooth area (black arrowhead). Figs 62–65. Whole frustules; note the presence of pore fields, step and collum in the mantle, and the cingulum composed by open, ligulate copulae. Collum (white arrowhead) and smooth area of the mantle (black arrowhead) are also indicated in Fig. 64. Fig. 63 is a detail of Fig. 62, rotated. Scale bar: 10 µm.

FIGURES 2–14 in Orthoseira variabilis sp. nov., a new diatom from a snow patch in Potter Cove, King George Island, Antarctica

FIGURES 2–14. Orthoseira variabilis sp. nov. LM. Frustules in girdle view. Note mantle step (Fig. 7, black arrow) and marginal spines (Fig. 14, white arrowheads). Figures marked with "=" are the same frustules with a different focus. Scale bar: 10 µm (Scale bar is the same for Figs 2–13).

FIGURE 1 in Orthoseira variabilis sp. nov., a new diatom from a snow patch in Potter Cove, King George Island, Antarctica

FIGURE 1. Map of the Antarctic Peninsula and South Shetland Islands (left); map of King George Island/Isla 25 de Mayo, showing the location of Potter Cove (right, top); panoramic view of Potter Cove and sampling site (right, center, arrow); close view of the sampling site (right, bottom, arrow).

FIG. 5 in Patch Dynamics Inform Management Decisions in a Threatened Frog Species

FIG. 5. (A) Crawfish Frog movement from Nate's Pond (Hillenbrand Fish and Wildlife Area-West, Greene County, Indiana). One-third of juvenile Crawfish Frogs that metamorphosed at Nate's Pond dispersed to nearby wetlands to breed. Two-thirds of juveniles returned to Nate's to breed. Numbers in parentheses represent counts of individuals. The sizes of the arrows are proportional to the number of individuals. (B) A subset of adult Crawfish Frogs shifted breeding wetlands between years. Colors match the initial wetland from which frogs emigrated. Numbers indicate counts of individuals moving between wetlands. Scale bar ¼ 500 m.

FIG. 4 in Patch Dynamics Inform Management Decisions in a Threatened Frog Species

FIG. 4. Retention of juvenile Crawfish Frogs released at artificial burrows west of Nate's Pond (Hillenbrand Fish and Wildlife AreaWest, Greene County, Indiana). From 24 June–1 August 2015, we used wildlife cameras to determine burrow occupancy. We defined snake predation as instances when frogs no longer appeared after a snake was photographed at burrows. Snake predation (n ¼ 10) and an unknown case of mortality (n¼ 1) are noted.

FIG. 1 in Patch Dynamics Inform Management Decisions in a Threatened Frog Species

FIG. 1. Crawfish Frog breeding wetlands (n ¼ 6) at Hillenbrand Fish and Wildlife Area-West (HFWA-W; Greene County, Indiana). We encircled Nate's and Cattail ponds (bolded text) with drift fence/pitfall trap arrays in 2009– 2016 and sampled at the remaining wetlands (Big, Erosion Control [EC], New, and Nate's Jr.) using funnel traps. We monitored Crawfish Frog breeding (late February through early May) and metamorphosis (mid-June through early August) at Nate's and Cattail, and only breeding at the remaining wetlands. The yellow outline indicates the boundary of HFWAW. Scale bar ¼ 1 km.

FIG. 2 in Patch Dynamics Inform Management Decisions in a Threatened Frog Species

FIG. 2. (A) Newly metamorphosed juvenile Crawfish Frogs at Nate's Pond (Hillenbrand Fish and Wildlife Area-West, Greene County, Indiana) exited with no specific directionality in 2009–2011 and 2014. Exiting frogs were captured by pitfall traps (indicated by yellow squares) positioned every 10 m along the drift fence. Sizes of trap squares are proportional to the number of juveniles exiting from each trap. Numbers next to the traps show the proportion of juveniles exiting from that trap, averaged across the years. (B) Post-breeding adult Crawfish Frogs exhibited a strong tendency to exit Nate's Pond towards the southeast, presumably in the direction of their primary burrow (Heemeyer and Lannoo, 2012). A smaller subset of adults exited east; a much smaller subset exited west. Sizes of trap squares are proportional to the ratio of adults versus juveniles exiting from each trap. We included adults that originated from Nate's Pond and were captured in 2013–2016, and excluded those from 2012 (small sample size, n ¼ 14). We included juveniles captured in 2009–2011 and 2014, and excluded years with small sample sizes (2013, n ¼ 8) and no recruitment (2012 and 2015). Scale bar ¼ 50 m.

opencc-by-4.0Oct 2024View details →

Temperature data collected in turf aggregations, seaweed patches and the water masses in mesocosm in the Oslofjord, Norway

Temperature data collected in turf aggregations, seaweed patches and the water masses in the NIVA mesocosm basins at Solbergstrand, in the Oslofjord, Norway

opencc-by-4.0Jun 2024View details →

Data for the sea ice concentration patch experiments (CESM1)

This dataset is for the SIC patch experiments performed with CESM1.2.1. Each .zip file contains the 40-year average field of a specific patch experiment. The last two digits of each file name denote the patch number, and the first digit (3xx and 7xx) denote +SIC and -SIC experiments, respectively. For example, to calculate the response of TOA fluxes in response to SIC change in the 5th SIC patch, we can calculate the TOA differences in the spw_705 file and spw_305 file.

openOct 2024View details →

SD4EO: Open Street Maps Northern France Patch Dataset

This dataset has been created as part of the deliverables for ESA’s <a href="https://eo4society.esa.int/projects/sd4eo/">SD4EO project</a>. It consists of orthogonal patches from Open Street Maps taken on 2024, which cover large areas in northern France. They corresponds to large Sentinel-2 Tile areas: T31TCJ, T31TCN, T31TDN, T31UDP, T31UEP, T30UWU, T31TCL, T31TDL, T31TDM, T31TEM, T31TEN, T31TFM, T31UDQ, T31UEQ, T30TXT, T30TYS, T30UXU, T30UYU, T31TFN, T31UFP, T31UFQ and T30TVK. Each patch covers an area of approximately 1700x1700 meters (though the exact size may vary slightly with latitude). Patches located at the edges of Sentinel-2 tiles were excluded to avoid potential cutting or distortion issues. Likewise, patches near large bodies of water, including coastlines, were also discarded. It's important to note that, unlike the synthetic image dataset [link], in this case, the patches are always disjoint. To facilitate the use of these images for training generative AI models (such as GANs and Diffusion models), the patch size has been standardized to 512x512 pixels, providing an effective resolution of 3.3 meters per pixel. To simplify their usage, the images are stored in lossless PNG format. Each patch is also accompanied by real RGB+NIR pixel-by-pixel correspondent satellite images from Sentinel-2 in the sibling dataset <a href="https://zenodo.org/records/13957879">doi:10.5281/zenodo.13957879</a> Both this dataset and the Sentinel-2 dataset have been used to train a conditional diffusion model, which generated a synthetic dataset of 46.5 GB that can be accessed at this [<a href="https://zenodo.org/records/13208361">link</a>]. The file naming convention is straightforward:                        Patch_<Tile Name>_<Column Number>_<Row Number>_OSM.png Columns and rows are always referenced within the same tile.   The data from OpenStreetMap (OSM) is licensed under the Open Database License (ODbL). This license allows you to freely use, modify, and distribute the data, provided we follow two key conditions: <ol> <li>Attribution: We must give appropriate credit to OpenStreetMap and its contributors when using their data.</li> <li>Share-Alike: If we modify or build upon the data, you must distribute your derivative works under the same ODbL license.</li> </ol> As a derivative dataset, we share it under the same terms. This ensures that any improvements or enhancements made to the data remain open and available to the public.   The SD4EO Project is funded by ESA’s FutureEO programme under contract no. 4000142334/23/I-DT and is supervised by ESA Φ-lab.

opencc-by-4.0Oct 2024View details →

Unveiling the Characteristics and Impact of Security Patch Evolution

Open the record for dataset details and reuse information.

dryad32/100

Data from: Habitat patch use by fishers in the deciduous forest-dominated landscape of the central Appalachian Mountains, USA

Fishers (Pekania pennanti) are often associated with the coniferous and mixed forests of the northern United States and central Canada, and their ecology has been studied extensively in portions of their distributional range. Recently, natural range expansion and reintroductions have led to recolonization by fishers of portions of the central Appalachian Mountains, USA, where deciduous forest is the dominant vegetation type. We used noninvasive hair snare surveys and microsatellite genetic analysis to detect fishers in the central Appalachian Mountains of Pennsylvania, USA. We used these detections within an occupancy modeling framework to explore habitat patch use by fishers and the forest characteristics and land use features that influenced it. We found that the likelihood of patch use by fishers was related to forests with higher proportions of low-density residential areas. Our results also suggested lower road densities might be related to higher likelihood of fisher patch use. Fishers in Pennsylvania tolerated some forms of land development. Patch use was not driven by forest type or canopy cover, at least within our deciduous forest-dominated study areas. Future research identifying the threshold values at which forest cover and land development affect patch use by fishers in the central Appalachian Mountains will better inform management decisions with respect to sites for future reintroduction of fishers.

opencc-zeroDec 2016View details →

opencc-by-4.0Jul 2021View details →

Seismic wave propagation in partially saturated rocks with a fractal distribution of fluid-patch size

Laboratory experiments on partially saturated rocks show that seismic attenuation can be significant, where the main mechanism is wave-induced local fluid flow (WILFF) due to patchy saturation at different spatial scales. We propose a theory to obtain the seismic properties of partially saturated rocks based on fractal (self-similar) patches, leading to an effective frequency-dependent fluid modulus. The model combines the differential effective medium (DEM) and Biot-Rayleigh theories, where the patches are inclusions incrementally added, such that the effective fluid is assumed the host for the next addition. The analysis shows that the seismic properties are independent on the number of iterations, but depend on the scale range (radius) of the inclusions, fractal dimension Df of the self-similar distribution, parameter \(\theta\) of the exponential distribution, mean radius r0 and variance \({\sigma_r}^2\) of the Gaussian distribution. Forced-oscillation experiments are performed on a limestone sample under partial water-saturation conditions at seismic frequencies (2-500 Hz), to obtain the velocity dispersion and extensional attenuation. The proposed theory provides a reasonable description of the experimental data and other existing measurements on Berea sandstone and tight carbonates.

opencc-zeroNov 2024View details →

Encyclopedia of Life Taxonomy Patch for Dynamic Hierarchy Version 3.1

A taxonomic patch for the <a href="https://eol.org/docs/eol-dynamic-hierarchy">EOL Dynamic Hierarchy</a>.