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13,117 results for “Map”

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zenodo48/100

Density Layers of selected Points of Interest from Open Street Map

<p>This dataset contains a raster layer of 100*100m resolution showing the density of selected amenities from Open Street Map. The amenities are selected as points of interest, where electric vehicles owners are likely to stop for a moment and recharge their vehicles. This dataset covers Europe and was obtained with the Overpass API. This dataset can be used to identify possible charging location for electric vehicles or any other purpose requiring to quantify the number of amenities in an area.</p> <p>&nbsp;</p> <p>This dataset shows densities of a selection of Points of Interest in Europe from Open Street Map [1].</p> <p>Included countries are:</p> <p>&nbsp;</p> <p><em><strong>country_codes</strong> = [&#39;AT&#39;, &#39;BE&#39;, &#39;BG&#39;, &#39;HR&#39;, &#39;CY&#39;, &#39;CZ&#39;, &#39;DK&#39;, &#39;EE&#39;, &#39;FI&#39;, &#39;FR&#39;, &#39;DE&#39;, &#39;GR&#39;, &#39;HU&#39;, &#39;IE&#39;, &#39;IT&#39;,&#39;LV&#39;, &#39;LT&#39;, &#39;LU&#39;, &#39;MT&#39;, &#39;NL&#39;, &#39;PL&#39;, &#39;PT&#39;, &#39;RO&#39;, &#39;SK&#39;, &#39;SI&#39;, &#39;ES&#39;, &#39;SE&#39;, &#39;AL&#39;, &#39;AD&#39;, &#39;AM&#39;, &#39;BY&#39;, &#39;BA&#39;, &#39;FO&#39;, &#39;GE&#39;, &#39;GI&#39;, &#39;IS&#39;, &#39;IM&#39;, &#39;XK&#39;, &#39;LI&#39;, &#39;MK&#39;, &#39;MD&#39;, &#39;MC&#39;, &#39;ME&#39;, &#39;NO&#39;, &#39;SM&#39;, &#39;RS&#39;, &#39;CH&#39;, &#39;TR&#39;, &#39;UA&#39;, &#39;GB&#39;, &#39;VA&#39;]</em></p> <p>&nbsp;</p> <p>The requests of Points of Interest have been performed with the Overpass API [2] (free of charge).</p> <p>&nbsp;</p> <p>The codes included in each density are listed below :</p> <p>&nbsp;</p> <p><strong><em>&#39;highway&#39;</em></strong><em> = [&#39;&quot;highway&quot;=&quot;motorway&quot;&#39;, &#39;&quot;highway&quot;=&quot;rest_area&quot;&#39;];</em></p> <p><strong><em>&#39;parkings&#39;</em></strong><em> = [&#39;&quot;parking&quot;=&quot;surface&quot;&#39;, &#39;&quot;parking&quot;=&quot;multi-storey&quot;&#39;, &#39;&quot;parking&quot;=&quot;street_side&quot;&#39;, &#39;&quot;parking&quot;=&quot;underground&quot;&#39; , &#39;&quot;park_ride&quot;&#39; ];</em></p> <p><strong><em>&#39;school&#39;</em></strong><em> = [&#39;&quot;amenity&quot;=&quot;college&quot;&#39;, &#39;&quot;building&quot;=&quot;college&quot;&#39;, &#39;&quot;building&quot;=&quot;university&quot;&#39;, &#39;&quot;amenity&quot;=&quot;university&quot;&#39;, &#39;&quot;amenity&quot;=&quot;school&quot;&#39; , &#39;&quot;amenity&quot;=&quot;school&quot;&#39;, &#39;&quot;amenity&quot;=&quot;kindergarten&quot;&#39;, &#39;&quot;amenity&quot;=&quot;library&quot;&#39;];</em></p> <p><strong><em>&#39;health&#39;</em></strong><em>= [&#39;&quot;amenity&quot;=&quot;clinic&quot;&#39;, &#39;&quot;amenity&quot;=&quot;dentist&quot;&#39;, &#39;&quot;amenity&quot;=&quot;school&quot;&#39; , &#39;&quot;amenity&quot;=&quot;doctors&quot;&#39;, &#39;&quot;amenity&quot;=&quot;hospital&quot;&#39;, &#39;&quot;amenity&quot;=&quot;pharmacy&quot;&#39;,&#39;&quot;amenity&quot;=&quot;veterinary&quot;&#39;]; </em></p> <p><strong><em>&#39;cafe&#39;</em></strong><em>= [&#39;&quot;amenity&quot;=&quot;cafe&quot;&#39;,&#39;&quot;amenity&quot;=&quot;ice_cream&quot;&#39;, &#39;&quot;amenity&quot;=&quot;internet_cafe&quot;&#39;]; </em></p> <p><strong><em>&#39;supermarket&#39;</em></strong><em> = [&#39;&quot;shop&quot;=&quot;supermarket&quot;&#39;, &#39;&quot;shop&quot;=&quot;mall&quot;&#39;, &#39;&quot;shop&quot;= &quot;department_store&quot;&#39;, &#39;&quot;shop&quot;= &quot;convenience&quot;&#39;];</em></p> <p><strong><em>&#39;restaurant&#39;</em></strong><em>= [&#39;&quot;amenity&quot;=&quot;restaurant&quot;&#39;];</em></p> <p><strong><em>&#39;fastfood&#39;</em></strong><em> = [&#39;&quot;amenity&quot;=&quot;fast_food&quot;&#39;];</em></p> <p><strong><em>&#39;sport&#39;</em></strong><em>= [&#39;&quot;sport&quot;&#39;]; </em></p> <p><strong><em>&#39;hotel&#39;</em></strong><em> = [&#39;&quot;tourism&quot;=&quot;hotel&quot;&#39;, &#39;&quot;building&quot;=&quot;hotel&quot;&#39;, &#39;&quot;tourism&quot;=&quot;guest_house&quot;&#39;,&#39;&quot;tourism&quot;=&quot;apartment&quot;&#39;,&#39;&quot;tourism&quot;=&quot;hostel&quot;&#39;,&#39;&quot;tourism&quot;=&quot;motel&quot;&#39;,&#39;&quot;tourism&quot;=&quot;camp_site&quot;&#39;]; </em></p> <p><strong><em>&#39;pubs&#39;</em></strong><em> = [&#39;&quot;amenity&quot;=&quot;bar&quot;&#39;,&#39;&quot;amenity&quot;=&quot;pub&quot;&#39;, &#39;&quot;amenity&quot;=&quot;biergarten&quot;&#39;];</em></p> <p><em>&#39;theatre&#39;= [&#39;&quot;amenity&quot;=&quot;theatre&quot;&#39;, &#39;&quot;amenity&quot;=&quot;cinema&quot;&#39;, &#39;&quot;amenity&quot;=&quot;music_venue&quot;&#39;, &#39;&quot;leisure&quot;=&quot;stadium&quot;&#39; ]; </em></p> <p><strong><em>&#39;night&#39;</em></strong><em> = [&#39;&quot;amenity&quot;=&quot;nightclub&quot;&#39;, &#39;&quot;amenity&quot;=&quot;casino&quot;&#39;,&#39;&quot;amenity&quot;=&quot;gambling&quot;&#39;,&#39;&quot;amenity&quot;=&quot;stripclub&quot;&#39;]; </em></p> <p><strong><em>&#39;socio&#39;</em></strong><em>= [&#39;&quot;amenity&quot;=&quot;arts_centre&quot;&#39;, &#39;&quot;amenity&quot;=&quot;community_centre&quot;&#39;, &#39;&quot;amenity&quot;=&quot;social_centre&quot;&#39;, &#39;&quot;amenity&quot;=&quot;music_school&quot;&#39;, &#39;&quot;amenity&quot;=&quot;language_school&quot;&#39;]; </em></p> <p><strong><em>&#39;shop&#39;</em></strong><em> = [&#39;&quot;shop&quot;&#39;];</em></p> <p><strong><em>&#39;tourism&#39;</em></strong><em> = [&#39;&quot;amenity&quot;=&quot;exhibition_centre&quot;&#39;, &#39;&quot;tourism&quot;=&quot;attraction&quot;&#39;,&#39;&quot;tourism&quot;=&quot;viewpoint&quot;&#39;,&#39;&quot;tourism&quot;=&quot;aquarium &quot;&#39;,&#39;&quot;leisure&quot;=&quot;beach_resort &quot;&#39;,&#39;&quot;tourism&quot;=&quot;gallery&quot;&#39;,&#39;&quot;tourism&quot;=&quot;museum&quot;&#39;,&#39;&quot;tourism&quot;=&quot;theme_park&quot;&#39;,&#39;&quot;tourism&quot;=&quot;zoo&quot;&#39;,&#39;&quot;tourism&quot;=&quot;artwork&quot;&#39;];</em></p> <p>&nbsp;</p> <p>The pixel values are the sum of the number of POIs of each type located in the pixel.</p> <p>&nbsp;</p> <p><em>Limitations of the dataset</em></p> <p>- The dataset provides densities of only a selection of points of interests, regardless of its type. The complete list of amenity codes can be found on the OSM Wiki [3].</p> <p>- Ways are only considered through their centre points.</p> <p>&nbsp;</p> <p>[1] &ldquo;Open Street Map.&rdquo; <a href="https://www.openstreetmap.org/">https://www.openstreetmap.org/</a> (accessed Sep. 05, 2023).</p> <p>[2] &ldquo;Overpass API.&rdquo; <a href="https://wiki.openstreetmap.org/wiki/Overpass_API">https://wiki.openstreetmap.org/wiki/Overpass_API</a>&nbsp; (accessed Sep. 05, 2023).</p> <p>[3] &ldquo;Open Street Map Wiki.&rdquo; <a href="https://wiki.openstreetmap.org/wiki/Key:amenity#Sustenance">https://wiki.openstreetmap.org/wiki/Key:amenity#Sustenance</a> (accessed Sep. 05, 2023).</p>

opencc-by-4.0Sep 2023View details →
zenodo48/100

A map selection of wigeon stopover sites (core areas) based on wetland expert knowledge

<p>Stopover areas (core areas only) along the migration route of wigeons tracked with GPS transmitters were selected when they exhibited forests on more than 50% of their total surface or had less than 50% cover by water and/or wetland&nbsp;on the ESA&rsquo;s global land cover map. We created a sample of 5,630 regions of interest (3,403 for training and 2,227 for validation), delineated with polygons assigned to land classes listed in the Table 1. We used archives of Google Earth, ESRI, and BING satellites for the photointerpretation of the land classes as described in Table 1. The classification was performed with a Sentinel-2 MultiSpectral Instrument, Level-2A image collection in Google Earth Engine (GEE) through the R-package Rgee to create a batch process applying the GEE Random forest classifier to each selected core home range. The cloudless (maximum 3%) images were selected within the period from 01/06/2021 to 30/09/2021. The optimal number of trees was estimated at 100 for an out of bag error of 14%. The overall accuracy on the validation sample was 82 %.&nbsp;</p>

opencc-by-4.0Mar 2024View details →
zenodo48/100

Map of Swedish Forest Fires >10ha from 2016-2023

<p><span>A vector map of perimeters of forest fires in Sweden above 10ha from 2016 to 2023 and the Sala Megafire from 2014. Fire locations were identified from multiple sources: the <em>Skogsstyrelsen Skogsbr&auml;nder Map 2020</em>, <em>EFFIS burned area map</em> and the<em> NASA FIRMS MODIS or VIIRS Fire/Hotspot Data</em> thermal anomalies products. <br>For fires from 2018 to 2020, fire perimeters were sourced directly from <em>Skogsbr&auml;nder Map 2020</em> or the <em>EFFIS burned area map</em>. The <em>EFFIS burned area map</em> provided fire occurrence dates. For fires lacking occurrence dates (from <em>Skogsbr&auml;nder Map 2020</em>), we cross-referenced locations and assigned the dates from either the <em>EFFIS burned area map</em> or the <em>MSB incident reports database</em>, using ArcGIS.</span></p> <p><span>Fire locations (points) from 2016, 2017, 2021, 2022 and 2023 were identified from <em>NASA FIRMS MODIS or VIIRS Fire/Hotspot Data</em> thermal anomalies products, the fire date was set as the earliest detection date. We then digitized these fire perimeters using post-fire images from Sentinel-2 (10m x10m resolution). First fire locations were manually examined </span><span>using Sentinel Hub EO Browser as false colour composites (band combination Near Infrared &ndash; Red &ndash; Green) and image chips downloaded for fires over 10ha. We then manually delineated fire perimeters in ArcGIS; unburned areas located within the fires were excluded from fire perimeters. Fire perimeters include areas burned that were not forest land cover; however, fires that occurred on entirely non-forested land were excluded.</span></p> <p><span>&nbsp;</span></p> <p><span>The dataset is in vector (.shp) format with single part polygons representing burned areas; each associated with an occurrence date. This means that fire events with non-continuous burned areas are represented by several single-part polygons, which share the same fire ID number and date.</span></p> <p><span>Data References</span></p> <p><span>European Forest Fire Information System. 2020. EFFIS Burned Area Product. European</span></p> <p><span>Forest Fire Information System -Copernicus. (Available here </span><span><a href="https://forest-fire.emergency.copernicus.eu/applications/data-and-services"><span>https://forest-fire.emergency.copernicus.eu/applications/data-and-services</span></a></span><span>)</span></p> <p><span>&nbsp;</span></p> <p><span>NASA FIRMS MODIS or VIIRS Fire/Hotspot Data,</span> <span>Country Yearly Summary. 2024. (Available here </span><span><a href="https://firms.modaps.eosdis.nasa.gov/country/"><span>https://firms.modaps.eosdis.nasa.gov/country/</span></a></span><span>)</span></p> <p><span><br></span><span>Myndigheten f&ouml;r samh&auml;llsskydd och Beredskap. </span><span>2020. Incident reports from municipal</span></p> <p><span>fire brigades. (Available through direct contact with MSB)</span></p> <p><span>&nbsp;</span></p> <p><span>Skogsstyrelsen. 2020. Skogsbr&auml;nder. (Accessed via Skogsstyrelsen FTP service, under https://www.skogsstyrelsen.se/sjalvservice/karttjanster/geodatatjanster/ftp/)</span></p>

opencc-by-4.0Mar 2024View details →
zenodo48/100

Global Ocean Heat Content Anomalies and Ocean Heat Uptake based on mapping Argo data using local Gaussian processes

<p>Monthly Ocean Heat Content Anomalies (OHCA) in the top 2000 dbar of the ocean are calculated (during 2004-2024, equatorward of 65 degree latitude) subtracting the mean over the period 2004-2024 from the monthly time series of OHC. Yearly OHCA time series are then calculated that include 1. one point per year, i.e., from averaging Jan to Dec (see files ending in &ldquo;yearly.nc&rdquo;), and 2. two points per year, i.e., from averaging Jan to Dec and Jul to Jun, respectively&nbsp; (see files ending in &ldquo;yearly2.nc&rdquo;). OHC fields are mapped using locally stationary Gaussian processes (defined over space and time) with data-driven decorrelation scales (Kuusela and Stein, 2018). A linear time trend was included in the estimate of the mean field (along with spatial terms and harmonics for the annual cycle). Mapping is done separately for different vertical sections: 15-20 dbar, 15-300 dbar, 300-700 dbar, 700-1850 dbar, 1800-1850 dbar. The 15-20 dbar (1800-1850 dbar) section is used to estimate OHCA for 0-15 dbar (1850-2000 dbar), where observations are sparser. Different vertical sections are combined to estimate global OHCA time series for 0-2000 dbar, 0-700 dbar, 700-2000 dbar (as indicated in the file names). The attribute "area" is included in the netcdf files and it tells the corresponding surface area for the estimates. Regions of the ocean that are shallower than 300 m or are not sufficiently well sampled by the Argo array are not included. Maps of the ocean masks used for the different vertical sections can be found in the .png files (blue shading indicates the area used for the horizontal integral); the bathymetry mask by Roemmich and Gilson (included in the file RG_ArgoClim_Temperature_2019.nc at https://sio-argo.ucsd.edu/RG_Climatology.html) is also used to define the ocean mask. Ocean Heat Uptake is calculated from the monthly OHCA and then averaged as described above to produce yearly time series included in the files for the different layers.</p> <p>For the uncertainty at each time point, the standard deviation of each OHCA/OHU value in the time series is included. When plotting a time series, the user may consider, e.g., shading plus/minus 1* or 1.96*standard deviation (corresponding to a&nbsp; confidence level of 68% or 95% respectively). These standard deviations in the files are estimated using spatially and temporally dependent conditional simulations of monthly gridded anomalies. When combining different layers, the standard deviation of the sum is conservatively estimated as the sum of the standard deviations.&nbsp;</p> <p>Finally, OHCA/OHU trends are estimated via a least-squares fit and reported in the variable metadata with uncertainties (confidence level of 68%). Trend uncertainties are estimated by repeating the fit for each member of the conditional simulation ensemble described above.</p> <p>&nbsp;</p>

opencc-by-4.0Nov 2023View details →
zenodo48/100

Oil and Gas Infrastructure Mapping (OGIM) database

<p>The Oil and Gas Infrastructure Mapping (OGIM) database is a global, spatially explicit, and granular dataset of oil and gas infrastructure. It is developed by Environmental Defense Fund (EDF)&nbsp;(<a href="https://www.edf.org/">www.edf.org</a>) and MethaneSAT, LLC (<a href="https://www.methanesat.org/">www.methanesat.org</a>), a wholly owned subsidiary of EDF. The OGIM database helps fill a crucial geospatial data need, by supporting the quantification and source characterization of oil and gas methane emissions. The database is developed via acquisition, analysis, curation, integration, and quality-assurance (performed at EDF) of publicly available geospatial data sources. These oil and gas facility datasets are reported by governments, industry, academics, and other non-government entities.</p> <p>OGIM is a collection of data tables within a GeoPackage. Each data table within the GeoPackage includes locations and facility attributes of oil and gas infrastructure types that are important sources of methane emissions, including: oil and gas production wells, offshore production platforms, natural gas compressor stations, oil and natural gas processing facilities, liquefied natural gas facilities, crude oil refineries, and pipelines. OGIM v2.7 includes approximately 6.7 million features, including 4.5 million point locations of oil and gas wells and over 1.2 million kilometers of oil and gas pipelines.</p> <p>Please see the PDF document in the &ldquo;Files&rdquo; section of this page for more information about this version, including attribute column definitions, key changes since the previous version, and more. Full details on database development and related analytics can be found in the following Earth System Science Data (ESSD) journal paper. Please cite this paper when using any version of the database:</p> <p><span>Omara, M., Gautam, R., O'Brien, M., Himmelberger, A., Franco, A., Meisenhelder, K., Hauser, G., Lyon, D., Chulakadabba, A., Miller, C., Franklin, J., Wofsy, S., and Hamburg, S.: Developing a spatially explicit global oil and gas infrastructure database for characterizing methane emission sources at high resolution, Earth Syst. Sci. Data Discuss.,&nbsp;</span><a href="https://doi.org/10.5194/essd-15-3761-2023"><span>https://doi.org/10.5194/essd-15-3761-2023</span></a><span>, 2023.</span></p> <p>Important note: While the results section of this manuscript is specific to v1 of the OGIM, the methods described therein are the same methods used to develop and update v2.7. Additionally, while we describe our data sources in detail in the manuscript above, and include maps of all acquired datasets, this open-access version of the OGIM database does not include the locations of about 300 natural gas compressor stations in Russia. Future updates may include these locations when appropriate permissions to make them publicly accessible are obtained.&nbsp;</p> <p>OGIM v2.7 is based on public-domain datasets reported in February 2025 or prior. Each record in OGIM indicates a date (SRC_DATE) when the original source of the record was published or last updated. Some records may contain out-of-date information, for example, if a facility&rsquo;s status has changed since we last visited a data source. We anticipate updating the OGIM database on a regular cadence and are continually including new public domain datasets as they become available.</p> <p>---</p> <p>Point of Contact at Environmental Defense Fund and MethaneSAT, LLC: Madeleine O&rsquo;Brien (maobrien@methanesat.org) and Mark Omara (momara@edf.org).</p>

opencc-by-4.0Jun 2024View details →
zenodo48/100

Mapping Mobility Motivation Survey

<p>The Mapping Mobility motivation study was conducted within the ongoing H2020 project named <a href="https://actionproject.eu/">ACTION</a> (pArticipatory sCience Toolkit agaInst pollutiON) on citizen science. Volunteers participate to citizen science initiatives for multiple reasons: personal enjoyment, desire for improvement or achievement, establishment of personal relationships, care for the environment, etc.<br> Studying motivation and investigating the factors influencing people participation to citizen science projects is an essential aspect in the analysis of citizen science communities. Understanding the reasons that foster people to engage can support the successful design and implementation of effective participant involvement tasks, as well as pave the way for long-term engagement.<br> The goal of the study is to analyse the motivation to participate of a specific citizen science community focused on fighting air pollution in the Mapping Mobility pilot supported by the ACTION project. More info on the pilot available at <a href="https://actionproject.eu/citizen-science-pilots/mapping-mobility/">https://actionproject.eu/citizen-science-pilots/mapping-mobility/</a>.</p> <p>The Mapping Mobility motivation study is part of the study about motivation in citizen science projects conducted within the ACTION project (<a href="https://doi.org/10.5281/zenodo.5753092">https://doi.org/10.5281/zenodo.5753092</a>). The survey&nbsp;was designed and administered using the <a href="https://coney.cefriel.com/">Coney</a>&nbsp;toolkit.</p> <p>The research object adopts the <a href="https://www.researchobject.org/ro-crate/1.0/">RO-Crate</a>&nbsp;specification. Files made available within the research object&nbsp;are:</p> <ul> <li><em>*-procedure.ttl</em>&nbsp;contains the RDF representation of the structure of the&nbsp;conversational survey (questions, answers, etc.)&nbsp;using the <a href="https://w3id.org/survey-ontology">Survey Ontology</a></li> <li><em>*-results.ttl&nbsp;</em>contains the RDF representation of the answers collected using the <a href="https://w3id.org/survey-ontology">Survey Ontology</a></li> <li><em>*-survey.tll </em>contains a comprehensive&nbsp;RDF representation of the survey data&nbsp;using the <a href="https://w3id.org/survey-ontology">Survey Ontology</a></li> <li><em>*-results.csv </em>contains the CSV of the answers collected</li> </ul>

opencc-by-4.0Dec 2021View details →
zenodo48/100

Building Exposure map

<p>Building Exposure map is a layer in support to Area Of Interest (AOI) definition for a Tsunami event. It&nbsp;provides an estimation of the number of buildings exposed to the tsunami event.</p> <p>&nbsp;</p>

opencc-by-4.0Dec 2021View details →
zenodo48/100

Night Population map

<p>Night Population map is&nbsp;a layer in support to Area Of Interest&nbsp;definition for an earthquake event. It provides an estimation of a population exposed to earthquake event in the examined area, based on the population occupancy during night hours.</p>

opencc-by-4.0Dec 2021View details →
zenodo48/100

A cross-disorder dosage sensitivity map of the human genome

<p>This repository contains data from Collins et al., <em>A cross-disorder dosage sensitivity map of the human&nbsp;genome</em> (2022), including:</p> <p>1. <strong>Collins_rCNV_2022.dosage_sensitivity_scores.tsv.gz</strong>: This file contains predicted probabilities of haploinsufficiency (pHaplo) and triplosensitivity (pTriplo) for 18,641 autosomal protein-coding genes as defined in Gencode v19.</p> <p>2. <strong>Collins_rCNV_2022.sliding_window_sumstats.tar.gz</strong>: This compressed directory contains rCNV association summary statistics for 54 phenotypes from genome-wide sliding window meta-analyses. Please refer to the README file included in this compressed directory for more details.</p> <p>3. <strong>Collins_rCNV_2022.gene_association_sumstats.tar.gz</strong>: This compressed directory contains rCNV association summary statistics for 54 phenotypes from exome-wide gene-based meta-analyses. Please refer to the README file included in this compressed directory for more details.&nbsp;</p> <p>4. <strong>Collins_rCNV_2022.gene_features_matrix.tar.gz</strong>: This compressed directory contains gene-level feature annotations for 145 features and 18,641 autosomal protein-coding genes. Please refer to the README file included in this compressed directory for more details.&nbsp;</p> <p>Smaller data files have been provided as supplemental tables alongside the publication online.</p> <p>Please also refer to the original publication for details on data sources, study design, methods, and other analyses.</p>

opencc-by-4.0Mar 2022View details →
zenodo48/100

Unit Map and Dips/Strikes of Sakarya Vallis, Gale Crater, Mars

<p>This dataset comprises the unit map derived from 3D analysis of Sakarya Vallis in Gale crater, Mars. The units are named Package 1&ndash;7. These packages have been extrapolated from morpho-stratigraphic analysis of a HiRISE scene in PRo3D. They have been further extrapolated using underlying image data. Included here is a shapefile representing the marker bed (Milliken et al. 2010) in Gale crater. The &quot;CDD&quot; refers to the Central Debris Deposit, identified by Hughes (2021).</p> <p>The structural data represents dip measurements along the boundaries of these packages within the feature; the &quot;sub-package&quot; data represent layering within the packages. For more on how dip is calculated in PRo3D, see https://pro3d.space/.</p> <p>Finally, the profiles mark the locations where topographic profiles were extracted for constructing cross-sections, as discussed in the thesis Persaud (2022).</p> <p>These data are intended to be displayed with the HiRISE ORI (https://doi.org/10.5281/zenodo.5808371) and CTX ORI mosaic (https://doi.org/10.5281/zenodo.5808357) over Sakarya Vallis, and over the basemap over the northwest of Aeolis Mons (https://doi.org/10.5281/zenodo.5808381).</p> <p>Format: SHP, SHX, DBF, PRJ, QPJ<br> Projection: Equidistant cylindrical<br> Datum: Spheroid (r = 3396.190 km)</p> <p>N.B. the PROJ4 format of the project is &quot;+proj=eqc +lat_ts=0 +lat_0=0 +lon_0=0 +x_0=0 +y_0=0 +a=3396190 +b=3396190 +units=m +no_defs&quot;</p>

opencc-by-4.0Dec 2021View details →
zenodo48/100

Data files belonging to the paper "Dealing with clustered samples for assessing map accuracy by cross-validation"

<p>Mapping of environmental variables often relies on map accuracy assessment through cross-validation with the data used for calibrating the underlying mapping model. When the data points are spatially clustered, conventional cross-validation leads to optimistically biased estimates of map accuracy. Several papers have promoted spatial cross-validation as a means to tackle this over-optimism. Many of these papers blame spatial autocorrelation as the cause of the bias and propagate the widespread misconception that spatial proximity of calibration points to validation points invalidates classical statistical validation of maps. In the paper related to these data, we present and evaluate alternative cross-validation approaches for assessing map accuracy from clustered sample data.&nbsp;</p> <p>&nbsp;</p> <p>The study area is western Europe, constrained in the north at 52&deg; latitude&nbsp;and at -10&deg; and 24&deg; longitude The projection is IGNF:ETRS89LAEA (Lambert azimuthal equal area projection).</p> <p>&nbsp;</p> <p><strong>Files:</strong></p> <p>agb.tif&nbsp; = above ground biomass (AGB) map from&nbsp;version 3 of the 2017 CCI-Biomass product (<a href="https://catalogue.ceda.ac.uk/uuid/5f331c418e9f4935b8eb1b836f8a91b8">https://catalogue.ceda.ac.uk/uuid/5f331c418e9f4935b8eb1b836f8a91b8</a>)<br> AGBstack.tif&nbsp; = covariates used for predicting AGB<br> aggArea.tif&nbsp; = coarse&nbsp;grid used for simulation in the model-based methods<br> ocs.tif&nbsp; = soil organic carbon stock (OCS) map (0-30 cm) from&nbsp;Soilgrids (<a href="https://www.isric.org/explore/soilgrids">https://www.isric.org/explore/soilgrids</a>)<br> OCSstack.tif&nbsp; = covariates used for predicting OCS<br> strata.xxx&nbsp;= 100 compact geo-strata (ESRI shape) created with the spcosa package; used for generating clustered samples<br> TOTmask.tif&nbsp; = mask of the area covered by the covariates</p> <p>&nbsp;</p> <p><strong>Details and data sources of the covariates in AGBstack.tif and OCSstack.tif:</strong></p> <table> <tbody> <tr> <td> <p><strong>Name</strong></p> </td> <td> <p><strong>Description</strong></p> </td> <td> <p><strong>Source</strong></p> </td> <td> <p><strong>Note</strong></p> </td> </tr> <tr> <td> <p>ai</p> </td> <td> <p>Aridity Index</p> </td> <td> <p><a href="https://chelsa-climate.org/downloads/">https://chelsa-climate.org/downloads/</a></p> </td> <td>Version 2.1</td> </tr> <tr> <td> <p>bio1</p> </td> <td> <p>Mean annual air temperature [&deg;C]</p> </td> <td><a href="https://chelsa-climate.org/downloads/">https://chelsa-climate.org/downloads/</a></td> <td>Version 2.1</td> </tr> <tr> <td> <p>bio5</p> </td> <td> <p>Mean daily maximum air temperature of the warmest month [&deg;C]</p> </td> <td><a href="https://chelsa-climate.org/downloads/">https://chelsa-climate.org/downloads/</a></td> <td>Version 2.1</td> </tr> <tr> <td> <p>bio7</p> </td> <td> <p>Annual range of air temperature [&deg;C]</p> </td> <td><a href="https://chelsa-climate.org/downloads/">https://chelsa-climate.org/downloads/</a></td> <td>Version 2.1</td> </tr> <tr> <td> <p>bio12</p> </td> <td> <p>Annual precipitation [kg/m<sup>2</sup>]</p> </td> <td><a href="https://chelsa-climate.org/downloads/">https://chelsa-climate.org/downloads/</a></td> <td>Version 2.1</td> </tr> <tr> <td> <p>bio15</p> </td> <td> <p>Precipitation seasonality [kg/m<sup>2</sup>]</p> </td> <td><a href="https://chelsa-climate.org/downloads/">https://chelsa-climate.org/downloads/</a></td> <td>Version 2.1</td> </tr> <tr> <td> <p>gdd10</p> </td> <td> <p>Growing degree days heat sum above 10&deg;C</p> </td> <td><a href="https://chelsa-climate.org/downloads/">https://chelsa-climate.org/downloads/</a></td> <td>Version 2.1</td> </tr> <tr> <td> <p>clay</p> </td> <td> <p>Clay content [g/kg] of the 0-5cm layer</p> </td> <td> <p><a href="https://soilgrids.org/">https://soilgrids.org/</a></p> <p>&nbsp;</p> </td> <td> <p>Only used for AGB</p> </td> </tr> <tr> <td> <p>sand</p> </td> <td> <p>Sand content [g/kg] of the 0-5cm layer</p> </td> <td><a href="https://soilgrids.org/">https://soilgrids.org/</a></td> <td>as above</td> </tr> <tr> <td> <p>pH</p> </td> <td> <p>Acidity (Ph(water)) of the 0-5cm layer</p> </td> <td><a href="https://soilgrids.org/">https://soilgrids.org/</a></td> <td>as above</td> </tr> <tr> <td> <p>glc2017</p> </td> <td> <p>Landcover 2017</p> </td> <td> <p><a href="https://land.copernicus.eu/global/products/lc">https://land.copernicus.eu/global/products/lc</a>, reclassified&nbsp; to: closed forest, open forest,&nbsp; natural non-forest veg., bare &amp; sparse veg. cropland, built-up, water</p> </td> <td> <p>Categorical variable</p> </td> </tr> <tr> <td> <p>dem</p> </td> <td> <p>Elevation</p> </td> <td> <p><a href="https://www.eea.europa.eu/data-and-maps/data/copernicus-land-monitoring-service-eu-dem">https://www.eea.europa.eu/data-and-maps/data/copernicus-land-monitoring-service-eu-dem</a></p> </td> <td> <p>&nbsp;</p> </td> </tr> <tr> <td> <p>cosasp</p> </td> <td> <p>Cosine of slope aspect</p> </td> <td> <p>Computed with the terra package from elevation</p> </td> <td>Computed @25m resolution; next aggregated to 0.5km</td> </tr> <tr> <td> <p>sinasp</p> </td> <td> <p>Sine of slope aspect</p> </td> <td>Computed with the terra package from elevation</td> <td>as above</td> </tr> <tr> <td> <p>slope</p> </td> <td> <p>Slope</p> </td> <td>Computed with the terra package from elevation</td> <td>as above</td> </tr> <tr> <td> <p>TPI</p> </td> <td> <p>Topographic position index</p> </td> <td>Computed with the terra package from elevation</td> <td>as above</td> </tr> <tr> <td> <p>TRI</p> </td> <td> <p>Terrain ruggedness index</p> </td> <td>Computed with the terra package from elevation</td> <td>as above</td> </tr> <tr> <td> <p>TWI</p> </td> <td> <p>Topographic wetness index</p> </td> <td> <p>Computed with SAGA from 500m resolution (aggregated) dem</p> </td> <td>&nbsp;</td> </tr> <tr> <td> <p>gedi</p> </td> <td> <p>Forest height</p> </td> <td> <p><a href="https://glad.umd.edu/dataset/gedi">https://glad.umd.edu/dataset/gedi</a></p> </td> <td> <p>Zone: NAFR</p> </td> </tr> <tr> <td> <p>xcoord</p> </td> <td> <p>X coordinate</p> </td> <td> <p>Using a mask created from the other covariates</p> </td> <td>&nbsp;</td> </tr> <tr> <td> <p>ycoord</p> </td> <td> <p>Y coordinate</p> </td> <td>Using a mask created from the other covariates</td> <td>&nbsp;</td> </tr> <tr> <td> <p>Dcoast</p> </td> <td> <p>Distance from coast</p> </td> <td> <p>Using a land mask created from the other covariates</p> </td> <td>&nbsp;</td> </tr> </tbody> </table> <p>&nbsp;</p>

opencc-by-4.0Dec 2021View details →
zenodo48/100

New maps of global geologic provinces and tectonic plates: global tectonics data and QGIS project file

<p>The global tectonics data compilation is a set of raster and vector data that are useful for investigating tectonics past and present. &nbsp;The datasets are useful on their own or can be used in GIS software, which includes the QGIS project file for convenience. &nbsp;The datasets include our new models for tectonic plate boundaries and deformation zones, geologic provinces and orogens. &nbsp;Additional datasets include earthquake and volcano locations, geochronology, topography, magnetics, gravity, and seismic velocity.</p> <p>The global tectonics collection is suitable for research and educational purposes.</p>

opencc-by-4.0Mar 2022View details →
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Greenland Ice Sheet crevasse map from ArcticDEM

<p><em>This dataset is produced using the ArcticDEM v3 mosaic. Since release, the new ArcticDEM v4.1 mosaic has been released, and I have developed newer and open-source methods for extracting crevasse geometries from ArcticDEM and REMA strips. I am happy to help direct you towards the solution or dataset most appropriate for your needs - please contact me at thomas.r.chudley@durham.ac.uk.</em></p> <p><strong>Data Description</strong></p> <p><em>Title</em>: Greenland Ice Sheet crevasse map from ArcticDEM<br><em>Version</em>: 1.00<br><em>Format</em>: GeoTiff<br><em>Projection</em>: WGS84 / NSIDC Sea Ice Polar Stereographic North (EPSG: 3413)<br><em>Resolution</em>: 2 m (binary) and 200 m (fraction)<br><em>Size</em>: 3.5 GB (total binary) and 22 MB (total fraction)<br><em>Citation</em>: Chudley et al. (2021) <a href="https://doi.org/10.1029/2021JF006287" target="_blank" rel="noopener">https://doi.org/10.1029/2021JF006287</a><br><em>Contact</em>: Tom Chudley<br><em>Email</em>: thomas.r.chudley@durham.ac.uk</p> <p><strong>Products</strong></p> <p>This dataset contains crevasse locations identified from the ArcticDEM v3 mosaic. There are two primary products: a 2 m binary crevasse map, and a 200 m crevasse fraction map. It is divided into the six IMBIE 'Rignot' drainage basins: central west (CW), southwest (SW), southeast (SE), northeast (NE), north (NO), northwest (NW).</p> <p><em>This dataset is for scientific purposes only. The method is not able to detect&nbsp;metre-scale&nbsp;and snow-covered crevasses, and&nbsp;should not be used for field safety purposes.</em></p> <p><em><strong>2 m crevasse binary</strong></em></p> <p>Byte GeoTiff product indicating derived crevasses at 2 m resolution. File naming convention is <em>crevasse_binary_XX_2m.tif</em>, where XX is the IMBIE basin code.</p> <p>Values have the following meaning:&nbsp;</p> <ul> <li>0: No data</li> <li>1: No crevasses identified</li> <li>2: Crevasses identified</li> </ul> <p><em><strong>200 m crevasse fraction</strong></em></p> <p>Float32 GeoTiff product indicating fraction of 200 m grid cell identified as crevasses in the 200 m product. File naming convention is <em>crevasse_fraction_XX_2m.tif</em>, where XX is the IMBIE basin code.</p> <p>Values have the following meaning:&nbsp;</p> <ul> <li>0 - 1: Fraction of grid cell identified as crevasse in 2 m dataset</li> <li>-9999: No data</li> </ul> <p><strong>Method</strong></p> <p>The full processing chain for data derivation is described in Chudley et al. (2021). A binary crevasse mask of the Greenland Ice Sheet is generated using ArcticDEM v3 mosaic data at 2 m resolution (Porter et al., 2018), with data processed in Google Earth Engine (Gorelick et al., 2017). The ArcticDEM is cropped to the GIMP ice mask (Howat et al., 2014), before a smoothed elevation model is generated by performing an image convolution with a circular kernel of 50 m radius. Residuals greater than 1 m between the smoothed and raw elevation values were identified as crevasses. To compare with public velocity datasets (and derived strain rates, stress, etc.), the 2 m dataset was aggregated (using GDAL) into grid cells to match the resolution (200 m) of the Making Earth System Data Records for Use in Research Environments (MEaSUREs) ice sheet surface velocity grid (Joughin, 2010; 2021). Aggregated values represent the fraction of grid cell area classified as crevasses.</p> <p><strong>Caveats</strong></p> <ul> <li>The method, including kernel size was tuned manually based on the region of interest of the original Chudley et al. (2021) paper. As such, it may not be optimal for other regions of interest on the ice sheet, in particular in the east, where medial moraines and marginal valleys are more prevalent (see caveat #4).</li> <li>The ArcticDEM is derived from optical MAXAR imagery. As such, snow-filled crevasses will not be identified here, which will be problematic above the ablation zone.</li> <li>Following comparison with Uncrewed Aerial Vehicle (UAV) data in Chudley et al. (2021), the approximate lower bound of crevasse width identified is ~10 m. These are large crevasses, far greater than are commonly encountered in safe fieldwork environments.</li> <li>This method is relatively crude: at its core, it is effectively a high-pass filter applied to the ArcticDEM mosaic. As such, there are false positives that occur around other supraglacial features (rivers, moraines, etc.) as well as marginal features (proglacial geomorphology, fjord sikkusak, etc.) that are captured in regions where the GIMP ice mask does not accurately capture the terrestrial ice extent at the time of ArcticDEM data capture. Users are encouraged to critically evaluate data in their areas of interest using the 2 m binary map and external data, even when intending to use only the 200 m fraction dataset.</li> </ul> <p><strong>Citation</strong></p> <p>When using this data, please cite the method as being from:</p> <p>Chudley, T. R., Christoffersen, P., Doyle, S. H., Dowling, T. P. F., Law, R., Schoonman, C. M., Bougamont, M., &amp; Hubbard, B. (2021). Controls on water storage and drainage in crevasses on the Greenland Ice Sheet. Journal of Geophysical Research: Earth Surface, 126, e2021JF006287. <a href="https://doi.org/10.1029/2021JF006287">https://doi.org/10.1029/2021JF006287</a>.</p> <p><strong>Acknowledgements</strong></p> <p>Initial processing chain created whilst Chudley was supported by a Natural Environment Research Council Doctoral Training Partnership Studentship (Grant No. NE/L002507/1).</p> <p>ArcticDEM v3 mosaic is provided by the Polar Geospatial Center under NSF-OPP awards 1043681, 1559691, and 1542736.</p>

opencc-by-4.0Jun 2022View details →
zenodo48/100

Sentinel2GlobalLULC: A dataset of Sentinel-2 georeferenced RGB imagery annotated for global land use/land cover mapping with deep learning (License CC BY 4.0)

<p>Sentinel2GlobalLULC is a deep learning-ready dataset of RGB images from the Sentinel-2 satellites designed for global land use and land cover (LULC) mapping. Sentinel2GlobalLULC v2.1&nbsp;contains 194,877 images in GeoTiff and JPEG format corresponding to 29 broad LULC classes. Each image has 224 x 224 pixels at 10 m spatial resolution and was produced by assigning the 25th percentile of all available observations in the Sentinel-2 collection between June 2015 and October 2020 in order to remove atmospheric effects (i.e., clouds, aerosols, shadows, snow, etc.). A spatial purity value was assigned to each image based on the consensus across 15 different global LULC products available in Google Earth Engine (GEE).&nbsp;</p> <p>&nbsp;</p> <p>Our dataset is structured into 3 main zip-compressed folders, an Excel file with a dictionary for class names and descriptive statistics per LULC class, and a python script to convert RGB GeoTiff images into JPEG format. The first folder called &quot;Sentinel2LULC_GeoTiff.zip&quot;&nbsp;contains 29 zip-compressed subfolders where each one corresponds to a specific LULC class with hundreds to thousands of GeoTiff Sentinel-2 RGB images. The second folder called &quot;Sentinel2LULC_JPEG.zip&quot; contains 29 zip-compressed subfolders with a JPEG formatted version of the same images provided in the first main folder. The third folder called &quot;Sentinel2LULC_CSV.zip&quot; includes 29 zip-compressed CSV files with as many rows as provided images and with 12&nbsp;columns containing the following metadata (this same metadata is provided in the image filenames):&nbsp;</p> <ul> <li>Land Cover Class ID: is the identification number of each LULC class</li> <li>Land Cover Class Short Name: is the short name of each LULC class</li> <li>Image ID: is the identification number of each image within its corresponding LULC class&nbsp;</li> <li>Pixel purity Value: is the spatial purity of each pixel for its corresponding LULC class calculated as the spatial consensus across up to 15 land-cover products&nbsp;</li> <li>GHM Value: is the spatial average of the Global Human Modification index (gHM) for each image</li> <li>Latitude: is the latitude of the center point of each image</li> <li>Longitude: is the longitude of the center point of each image</li> <li>Country Code: is the Alpha-2 country code of each image as described in the ISO 3166 international standard. To understand the country codes, we recommend the user to visit the following website where they present the Alpha-2 code for each country as described in the ISO 3166 international standard:https: //www.iban.com/country-codes</li> <li>Administrative Department Level1: is the administrative level 1 name to which each image belongs</li> <li>Administrative Department Level2: is the administrative level 2 name to which each image belongs</li> <li>Locality: is the name of the locality to which each image belongs</li> <li>Number of S2 images : is&nbsp;the number of found instances in the corresponding Sentinel-2 image collection between June 2015 and October 2020, when compositing&nbsp;and exporting&nbsp;its corresponding&nbsp;image tile</li> </ul> <p>For seven LULC classes, we could not export from GEE all images that fulfilled a spatial purity of 100% since there were millions of them. In this case, we exported a stratified random sample of 14,000 images and provided an additional CSV file with the images actually contained in our dataset. That is, for these seven LULC classes, we provide these 2 CSV files:</p> <ul> <li>A CSV file that contains all exported images for this class&nbsp;</li> <li>A CSV file that contains all images available for this class at spatial purity of 100%, both the ones exported and the ones not exported, in case the user wants to export them. These CSV filenames end with &quot;including_non_downloaded_images&quot;.</li> </ul> <p>To clearly state the geographical coverage of images available in this dataset,&nbsp; we&nbsp;included in the version v2.1, &nbsp;a compressed folder called &quot;Geographic_Representativeness.zip&quot;. This zip-compressed folder&nbsp;contains a csv file&nbsp;for each LULC class that provides the complete list of countries represented in that class. Each csv file has two columns, the first one gives the country code and the second one gives the number of images provided in that country for that LULC class. In addition to these 29 csv files, we provided another csv file that maps each ISO Alpha-2 country code to its original full country name.</p> <p>&copy;&nbsp;<a href="https://doi.org/10.5281/zenodo.5055632">Sentinel2GlobalLULC Dataset&nbsp;</a>by&nbsp;&nbsp;Yassir Benhammou, Domingo Alcaraz-Segura, Emilio Guirado, Rohaifa Khaldi, Boujem&acirc;a Achchab, Francisco Herrera &amp; Siham Tabik&nbsp;is marked with Attribution 4.0 International&nbsp;(CC-BY 4.0)</p>

opencc-by-4.0Jul 2022View details →
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Live Fuel Moisture Content Mapping in the Mediterranean Basin Using Random Forests and Combining MODIS Spectral and Thermal Data

<p>Live fuel moisture content (LFMC), defined as&nbsp;the mass of water in the foliage and small twigs relative to its total dry mass, is a key factor affecting fire potential and determining wildfire danger and activity. Fuel moisture&nbsp;is directly related to the amount of energy needed to evaporate water before ignition. Consequently, high moisture values reduce, or even inhibit, ignitability and subsequent fire spread.</p> <p>To cover the absence of a specific model to estimate LFMC for the Mediterranean Basin at the sub-continental scale, we built an empirical&nbsp;model&nbsp;based on Random Forests (LFMC<sub>RF</sub>) and combining&nbsp;MODIS spectral bands, vegetation indices, land surface temperature, and the day of year as predictors. The details on the modeling and&nbsp;validation methods, and&nbsp;the accuracy of the estimates&nbsp;are in the related publication <strong><a href="https://doi.org/10.3390/rs14133162">Cunill Camprub&iacute; et al., 2022</a></strong>.</p> <p>This dataset contains a collection of&nbsp;weekly&nbsp;LFMC maps&nbsp;from&nbsp;February 2000&nbsp;to December 2021. The maps cover the Mediterranean and part of the Temperate biomes of the Mediterranean Basin.&nbsp;File&nbsp;<em>mapping_area_LFMC-RF_W-1.0.png</em> shows the target mapping areas.</p> <p>Metadata:</p> <ul> <li>Spectral Information: MODIS MCD43A4 C.6</li> <li>Land Surface Temperature: MODIS MOD11A2 C.6</li> <li>Land Cover Mask: MODIS MCD12Q1 C.6</li> <li>Coordinate Reference System: Native MODIS Sinusoidal</li> <li>Temporal Resolution: Weekly (W)</li> <li>Spatial Resolution: ~500 m</li> <li>File Format: NetCDF v.4</li> <li>Scale Factor: 0.01</li> </ul> <p>Fundings:</p> <p>The&nbsp;study was funded by the MICINN (RTI2018-094691-B-C31), European Union&rsquo;s Horizon 2020-Research and Innovation Framework Programme under grant agreement no. 101003890 project FirEUrisk, the National Natural Science Foundation of China (U20A20179, 31850410483), and the talent proposals in Sichuan Province (2020JDRC0065) from Southwest University of Science and Technology (18ZX7131).</p>

opencc-by-4.0Aug 2022View details →
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Mapping mineralogical heterogeneities at the nm-scale by scanning electron microscopy in modern Sardinian stromatolites: Deciphering the origin of their laminations

<p>These are the raw or processed data used for a paper published in Chemical Geology&nbsp;by Debrie&nbsp;et al. (2022), entitled &quot;Mapping mineralogical heterogeneities at the nm-scale by scanning electron microscopy in modern Sardinian stromatolites: Deciphering the origin of their laminations&quot;, <a href="https://doi.org/10.1016/j.chemgeo.2022.121059">https://doi.org/10.1016/j.chemgeo.2022.121059</a></p> <p>The data content is summarized in the List_description_of_data.xlsx&nbsp;file</p>

opencc-by-4.0Aug 2022View details →
zenodo48/100

Architectural Languages for the Microservices Architecture: A systematic mapping study [Data set]

<p>This repository contains all artifacts related to the study: Architectural Languages for the Microservices Architecture: A systematic mapping study.</p>

opencc-by-4.0Aug 2022View details →
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Distribution and habitat suitability maps for Central European steppe plants

<p>This dataset contains distribution maps for Central European steppe plants and coordinates of species occurrence points used by Div&iacute;&scaron;ek et al. (2022) to calibrate habitat suitability models. These models were projected onto past climates and the resulting habitat suitability maps for 10 periods since the Last Glacial Maximum (LGM) are also included. These maps were further used as input data for simulations of species migration from climatically suitable areas in the LGM to identify those that may have served as a source for colonisation of the species&#39; current ranges. For each species, we present maps of climatically suitable areas during the LGM and mid-Holocene (for the latter period, only areas accessible from the LGM are shown), as well as maps of the &quot;source areas&quot; from which the species may have colonised the regions occupied today.</p>

opencc-by-4.0Sep 2022View details →
zenodo48/100

COCO, LVIS, Open Images V4 classes mapping

<p>This repository contains a mapping between the classes of COCO, LVIS, and Open Images V4 datasets into a unique set of 1460 classes.</p> <p>COCO [Lin et al 2014] contains 80 classes, LVIS [gupta2019lvis] contains 1460 classes, Open Images V4 [Kuznetsova et al. 2020] contains 601 classes.</p> <p>We built a mapping of these classes using a semi-automatic procedure in order to have a unique final list of 1460 classes. We also generated a hierarchy for each class, using <a href="https://wordnet.princeton.edu/">wordnet</a></p> <p>This repository contains the following files:</p> <ul> <li><em>coco_classes_map.txt</em>, contains the mapping for the 80 coco classes</li> <li><em>lvis_classes_map.txt</em>, contains the mapping for the 1460 coco classes</li> <li><em>openimages_classes_map.txt</em>, contains the mapping for the 601 coco classes</li> <li><em>classname_hyperset_definition.csv</em>, contains the final set of 1460 classes, their definition and hierarchy</li> <li><em>all-classnames.xlsx</em>, contains a side-by-side view of all classes considered</li> </ul> <p>This mapping was used in VISIONE [Amato et al. 2021, Amato et al. 2022]&nbsp; that is a content-based retrieval system that supports various search functionalities (text search, object/color-based search, semantic and visual similarity search, temporal search). For the object detection VISIONE uses&nbsp;three pre-trained models: VfNet [Zhang et al. 2021] (trained on COCO dataset), Mask R-CNN [He et al. 2017] (trained on LVIS), and a <a href="http://tfhub.dev/google/faster_rcnn/openimages_v4/inception_resnet_v2/1">Faster R-CNN+Inception ResNet</a>&nbsp; (trained on the Open Images V4).</p> <p>This is&nbsp;repository&nbsp;is released under a Creative Commons Attribution license, please cite the following paper if you use it&nbsp;in your work in any form:</p> <blockquote> <pre>@inproceedings{amato2021visione, title={The visione video search system: exploiting off-the-shelf text search engines for large-scale video retrieval}, author={Amato, Giuseppe and Bolettieri, Paolo and Carrara, Fabio and Debole, Franca and Falchi, Fabrizio and Gennaro, Claudio and Vadicamo, Lucia and Vairo, Claudio}, journal={Journal of Imaging}, volume={7}, number={5}, pages={76}, year={2021}, publisher={Multidisciplinary Digital Publishing Institute} } </pre> </blockquote> <p>&nbsp;</p> <p>&nbsp;</p> <p><em><strong>References:</strong></em></p> <p>[Amato et al. 2022] Amato, G. et al. (2022). VISIONE at Video Browser Showdown 2022. In: , et al. MultiMedia Modeling. <em>MMM 2022. Lecture Notes in Computer Science</em>, vol 13142. Springer, Cham. <a href="https://doi.org/10.1007/978-3-030-98355-0_52">https://doi.org/10.1007/978-3-030-98355-0_52</a></p> <p>[Amato et al. 2021]&nbsp; Amato, G., Bolettieri, P., Carrara, F., Debole, F., Falchi, F., Gennaro, C., Vadicamo, L. and Vairo, C., 2021. The visione video search system: exploiting off-the-shelf text search engines for large-scale video retrieval.&nbsp;<em>Journal of Imaging</em>,&nbsp;<em>7</em>(5), p.76.</p> <p>[Gupta et al.2019] Gupta, A., Dollar, P. and Girshick, R., 2019. Lvis: A dataset for large vocabulary instance segmentation. In&nbsp;<em>Proceedings of the IEEE/CVF conference on computer vision and pattern recognition</em>&nbsp;(pp. 5356-5364).</p> <p>[He et al. 2017] He, K., Gkioxari, G., Doll&aacute;r, P. and Girshick, R., 2017. Mask r-cnn. In&nbsp;<em>Proceedings of the IEEE international conference on computer vision</em>&nbsp;(pp. 2961-2969).</p> <p>[Kuznetsova et al. 2020] Kuznetsova, A., Rom, H., Alldrin, N., Uijlings, J., Krasin, I., Pont-Tuset, J., Kamali, S., Popov, S., Malloci, M., Kolesnikov, A. and Duerig, T., 2020. The open images dataset v4.&nbsp;<em>International Journal of Computer Vision</em>,&nbsp;<em>128</em>(7), pp.1956-1981.</p> <p>[Lin et al. 2014] Lin, T.Y., Maire, M., Belongie, S., Hays, J., Perona, P., Ramanan, D., Doll&aacute;r, P. and Zitnick, C.L., 2014, September. Microsoft coco: Common objects in context. In&nbsp;<em>European conference on computer vision</em>&nbsp;(pp. 740-755). Springer, Cham.</p> <p>[Zhang et al. 2021] Zhang, H., Wang, Y., Dayoub, F. and Sunderhauf, N., 2021. Varifocalnet: An iou-aware dense object detector. In&nbsp;<em>Proceedings of the IEEE/CVF Conference on Computer Vision and Pattern Recognition</em>&nbsp;(pp. 8514-8523).</p> <p>&nbsp;</p>

opencc-by-4.0Oct 2022View details →
zenodo48/100

A Map of Land Use and Land Cover in Southern Malawi Derived from Sentinel-2 Data (2023)

<h3><strong>Overview</strong></h3> <p>The land use and land cover map comprises the Mulanje and Phalombe districts, in Southern Malawi. It includes five classes: forest, natural vegetation, cropland, wetland, and other lands. The map is derived from Sentinel-2 mosaics, resulting in a spatial resolution of 10 meters, for 2023.&nbsp;</p> <p>&nbsp;</p> <h3><strong>Map Accuracy</strong></h3> <p>The land use and land cover map achieves an overall accuracy of 89%. Details of user and producer accuracies are provided in Table 1.</p> <p>Table 1:&nbsp; Land use and land cover classification validation,including overall, producer (PA) and user (UA) accuracies values for each class.</p> <div> <table> <tbody> <tr> <td> <p><strong>Class&nbsp;</strong></p> </td> <td> <p><strong>Producer Accuracy</strong></p> </td> <td> <p><strong>User Accuracy</strong></p> </td> </tr> <tr> <td> <p>Cropland</p> </td> <td> <p>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; 93%</p> </td> <td> <p>&nbsp; &nbsp; &nbsp; &nbsp;85%</p> </td> </tr> <tr> <td> <p>Wetland</p> </td> <td> <p>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp;100%</p> </td> <td> <p>&nbsp; &nbsp; &nbsp; 100%</p> </td> </tr> <tr> <td> <p>Other Lands</p> </td> <td> <p>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp;90%</p> </td> <td> <p>&nbsp; &nbsp; &nbsp; &nbsp;95%</p> </td> </tr> <tr> <td> <p>Forest</p> </td> <td> <p>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp;79%</p> </td> <td> <p>&nbsp; &nbsp; &nbsp; 90%</p> </td> </tr> <tr> <td> <p>Natural Vegetation</p> </td> <td> <p>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; 90%</p> </td> <td> <p>&nbsp; &nbsp; &nbsp; 90%</p> </td> </tr> <tr> <td> <p><strong>Overall Accuracy</strong></p> </td> <td><br> <p><strong>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp;89%</strong></p> </td> </tr> </tbody> </table> </div> <h3>&nbsp;</h3> <h3><strong>Files descripion</strong></h3> <ul> <li>MLW_Sentinel_LULC_2023.tif / .qml: land use and land cover map and QGIS style file</li> <li>training_samples.gpkg: training samples with class labels</li> <li>validation_samples.gpkg: validation samples with class labels</li> </ul>

opencc-by-4.0May 2024View details →

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Last verified 2026-04-29Open record