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1,138 results for “Modis”

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zenodo36/100

Global oceanic seamless POC concentration products derived from MODIS-Terra

<p>The dataset integrates seamless POC concentration daily products for the global ocean from 2001 to 2008, derived from MODIS-Terra&lsquo;s XGBoost satellite retrieval products.&nbsp; The POC concentration in the product used int32 to integer data, specifically, the raw POC concentration (mg m-3) is first multiplied by 10000 and then rounded using int32.</p>

opencc-by-4.0Mar 2024View details →
zenodo36/100

MST NDSI Collection: A Cloud-free MODIS NDSI Dataset (2001–2022) for Tibetan Plateau Generated by a LightGBM-Based Method Using Multivariate Features

<p>1. Cloud-free MODIS normalized difference snow index (NDSI) dataset for Tibetan Plateau from 2001 to 2022&nbsp;is generated.</p> <p>2. This dataset is derived from daily 500-m MODIS NDSI datasets (MOD10A1 and MYD10A1).</p> <p>3. This dataset is provided using a WGS_1984_UTM_45N projection, with the data format of TIFF images.&nbsp;</p> <p>4. The NDSI value ranges from -10,000-10,000, corresponding to the raw NDSI band of MOD10A1 and MYD10A1. The fill value is set to -32768.</p> <p>5. Due to the large amount of data, the data for each year has been divided into several split archives (YYYY.partX.rar).</p> <p>6. Each RAR contains NDSI data for one year (January to December). After uncompressing into the TIFF format, the files are named as "NDSI_Daily_YYYY_mm_dd.tif" for NDSI data and "NDSI_Daily_YYYY_mm_dd.tif".</p> <p>7. The accuracy of this collection has been well validated by simulation experiments.</p> <p>8. This version includes data from 2017 to 2022 (https://doi.org/10.5281/zenodo.14177009). Version 1 includes data from 2001 to 2004 (https://doi.org/10.5281/zenodo.14027672). Version 2 includes data from 2005 to 2010(https://doi.org/10.5281/zenodo.14038846). Version3 includes data from 2011 to 2016 (https://doi.org/10.5281/zenodo.14089925).<br><br><br></p>

opencc-by-4.0Nov 2024View details →
zenodo36/100

A High-Quality Reprocessed MODIS Fraction of absorbed Photosynthetically Active Radiation Dataset (HiQ-FPAR)(Version 1)

<p>The High-Quality Fraction of absorbed Photosynthetically Active Radiation (HiQ-FPAR) is derived from reprocessed MODIS FPAR C6.1 product by SpatioTemporal Information Compositing Algorithm (STICA). This method integrates information from multiple dimensions, including pixel quality information, spatiotemporal correlation, and original observations, to improve the raw MODIS FPAR retrievals with poor quality. The HiQ-FPAR covers the period from 2000 to 2022, with spatial resolutions of 500m/5km for global vegetation area and temporal resolutions of 8 days.</p> <p>Ground-based verification results show that HiQ-FPAR performs better than the original MODIS product (MOD15A2H C6.1). Time series curves of the HiQ-FPAR exhibit reduced abnormal fluctuations and better alignment with expected phenological patterns. Additionally, the agreement with ground measurements increases gradually as raw data quality decreases. HiQ-FPAR was found to be more continuous and consistent than MODIS FPAR on a global scale from both spatial and temporal perspectives, especially in the equatorial regions where optical remote sensing usually cannot achieve good performance. Thus, We anticipate that HiQ-FAPR with better spatio-temporal continuity will better support varying global FPAR time series applications.</p> <p>Here, we offer a product version with a spatial resolution of 5km and a temporal resolution of 8 days. Another version has a spatial resolution of 500 meters and is available through Google Earth Engine (https://code.earthengine.google.com/?asset=projects/verselab-398313/assets/HiQ_FPAR/wgs_500m_8d).</p> <p>More details about HiQ-Fpar can be found at https://github.com/Gardenias-123/HiQ-FPAR</p>

opencc-by-4.0Mar 2024View details →
zenodo36/100

Long-term Continuous Red and Near-infrared Channel Reflectance from MODIS, 2001-2023 (LCREF-MODIS)

<p><strong>Usage Notes</strong>:<br>This is the updated LCREF-MODIS dataset (v3.2) consists of BRDF-normalized MODIS red and near-infrared surface reflectance. The LCREF-MODIS product was used to calibrate and benchmark the AVHRR surface reflectance to produce a temporally consistent record of surface reflectance prior to the MODIS era. It was also used to generate LCSPP-MODIS (previously known as LCSIF-MODIS) as a benchmark.</p> <p><strong>Key updates in version 3.2 include:</strong></p> <ul> <li><strong>Quality Flags</strong>: New quality flag layer enables users to identify whether a pixel is derived from observed surface reflectance (QA=0), high-quality gap-filled values (QA=1), lower-quality gap-filled based on the mean seasonal cycle (QA=2), or missing entirely (QA=3). We advice the user to rely only on observed and high-quality gap-filled values for their analyses.</li> <li><strong>Extension:</strong> to include observations from the year of 2023.</li> <li><strong>Snow mask:&nbsp;</strong>we note that all pixels marked with percent_snow &gt;0 in the original MCD43C1.v061 have been removed. This conservative approach was applied to reduce bias during cross-calibration, since unlike MODIS, AVHRR does not have a reliable snow detection algorithm. Therefore, surface reflectance values in high latitude regions are almost entirely gap-filled and should never be used for analysis for both LCREF-AVHRR and LCREF-MODIS. We encourage users to use only QA=0 and QA=1 pixels for their analysis. Alternatively, users can use LCREF-MODIS from the previous version for high latitude regions (v3.1), which did not mask out snow-covered pixles.&nbsp;</li> </ul> <p>The user can choose between LCREF-AVHRR and LCREF-MODIS for the overlapping period from 2001-2023. The two datasets are generally consistent during this overlapping period, although LCREF-MODIS shows a stronger greening trend between 2001-2023. For studies exploring the long-term vegetation dynamics, the user can either use only LCREF-AVHRR or use a blend dataset of LCREF-AVHRR and LCREF-MODIS as a sensitivity test.&nbsp;</p> <ul> <li>The LCREF-AVHRR v3.2 (1982-2023) is available at <a href="https://doi.org/10.5281/zenodo.11905959" target="_blank" rel="noopener">10.5281/zenodo.11905959</a></li> </ul> <p>The LCREF-AVHRR dataset was used as the input to generate LCSPP-AVHRR (previously known as LCSIF-AVHRR), and it can also be used to derive temporally consistant records of NDVI, NIRv, kNDVI, and other vegetation indices based on red and NIR surface reflectance variables. The user can access LCSPP products at:</p> <ul> <li>LCSPP-AVHRR v3.2 (1982-2000): <a href="https://doi.org/10.5281/zenodo.7916850" target="_blank" rel="noopener">10.5281/zenodo.7916850</a></li> <li>LCSPP-AVHRR v3.2 (2001-2023): <a href="https://doi.org/10.5281/zenodo.11906675" target="_blank" rel="noopener">10.5281/zenodo.11906675</a></li> <li>LCSPP-MODIS v3.2(2001-2023): <a href="https://doi.org/10.5281/zenodo.11657458" target="_blank" rel="noopener">10.5281/zenodo.11657458</a></li> </ul> <p>A manuscript describing the technical details is available at <a href="https://arxiv.org/abs/2311.14987" target="_blank" rel="noopener">https://arxiv.org/abs/2311.14987</a>, which detailed the uses and limitations of the dataset. All data outputs from this study are available at 0.05&deg; spatial resolution and biweekly temporal resolution in NetCDF format. Each month is divided into two files, with the first file &ldquo;a&rdquo; representative of the 1<sup>st</sup> day to the 15<sup>th</sup> day of a month, and the second file &ldquo;b&rdquo; representative of the 16<sup>th</sup> day to the last day of a month.</p> <p><strong>Abstract:</strong></p> <p>Satellite-observed solar-induced chlorophyll fluorescence (SIF) is a powerful proxy for the photosynthetic characteristics of terrestrial ecosystems. Direct SIF observations are primarily limited to the recent decade, impeding their application in detecting long-term dynamics of ecosystem function. In this study, we leverage two surface reflectance bands available both from Advanced Very High-Resolution Radiometer (AVHRR, 1982-2023) and MODerate-resolution Imaging Spectroradiometer (MODIS, 2001-2023). Importantly, we calibrate and orbit-correct the AVHRR bands against their MODIS counterparts during their overlapping period. Using the long-term bias-corrected reflectance data from AVHRR and MODIS, a neural network is trained to produce a Long-term Continuous SIF-informed Photosynthesis Proxy (LCSPP) by emulating Orbiting Carbon Observatory-2 SIF, mapping it globally over the 1982-2023 period. Compared with previous SIF-informed photosynthesis proxies, LCSPP has similar skill but can be advantageously extended to the AVHRR period. Further comparison with three widely used vegetation indices (NDVI, kNDVI, NIRv) shows a higher or comparable correlation of LCSPP with satellite SIF and site-level GPP estimates across vegetation types, ensuring a greater capacity for representing long-term photosynthetic activity.</p> <p>&nbsp;</p>

opencc-by-4.0Dec 2023View details →
zenodo36/100

Long-term Continuous SIF-informed Photosynthesis Proxy reconstructed with MODIS surface reflectance (LCSPP-MODIS), 2001-2023

<p><strong>Usage Notes</strong>:<br>This is the updated LCSPP dataset (v3.2), reconstructed using the MODIS record from 2001&ndash;2023. Previously referred to as "LCSIF," the dataset was renamed to emphasize its role as a SIF-informed long-term photosynthesis proxy derived from surface reflectance and to avoid confusion with directly measured SIF signals. The MODIS-based LCSPP is generated as an ancillary product to complement and benchmark the LCSPP-AVHRR product from 1982-2023.</p> <p>Key updates in version 3.2 include:</p> <ul> <li><strong>Improved Calibration</strong>: Enhanced consistency in calibration methods, addressing technical limitations in version 3.1 including applying more stringent quality filtering and snow masks.</li> <li><strong>Quality Flags</strong>: New quality flag layer enables users to identify whether a pixel is derived from observed surface reflectance (QA=0), high-quality gap-filled values (QA=1), lower-quality gap-filled based on the mean seasonal cycle (QA=2), or missing entirely (QA=3). We advice the user to rely only on observed and high-quality gap-filled values for their analyses.</li> <li><strong>Extension</strong> to include observations from the year of 2023.</li> </ul> <p>LCSPP-AVHRR repositories can be accessed via the following links:</p> <ul> <li>LCSPP-AVHRR v3.2 (1982-2000): <a href="https://doi.org/10.5281/zenodo.7916850" target="_blank" rel="noopener">10.5281/zenodo.7916850</a></li> <li>LCSPP-AVHRR v3.2 (2001-2023): <a href="https://doi.org/10.5281/zenodo.11906675" target="_blank" rel="noopener">10.5281/zenodo.11906675</a></li> </ul> <p>The user can choose between LCSPP-AVHRR and LCSPP-MODIS for the overlapping period from 2001-2023. The two datasets are generally consistent during this overlapping period, although LCSPP-MODIS shows a stronger greening trend between 2001-2023. For studies exploring the long-term vegetation dynamics, the user can either use only LCSPP-AVHRR or use a blend dataset of LCSPP-AVHRR and LCSPP-MODIS as a sensitivity test.&nbsp;</p> <p>In addition, the updated long-term continuous reflectance datasets (LCREF), used for the production of LCSPP, can be accessed using the following links:</p> <ul> <li>LCREF-AVHRR v3.1 (1982-2023): <a href="https://doi.org/10.5281/zenodo.11905959" target="_blank" rel="noopener">10.5281/zenodo.11905959</a></li> <li>LCREF-MODIS v3.1 (2001-2023): <a href="https://doi.org/10.5281/zenodo.11657458" target="_blank" rel="noopener">10.5281/zenodo.11657458</a></li> </ul> <p>A manuscript describing the technical details is available at <a href="https://arxiv.org/abs/2311.14987" target="_blank" rel="noopener">https://arxiv.org/abs/2311.14987</a>, while detailed the uses and limitations of the dataset. In particular, we note that <strong>LCSPP</strong> <strong>is a reconstruction of SIF-informed photosynthesis proxy and should not be treated as SIF measurements</strong>. Although LCSPP has demonstrated skill in tracking the dynamics of GPP and PAR absorbed by canopy chlorophyll (APARchl), it is not suitable for estimating fluorescence quantum yield.</p> <p>All data outputs from this study are available at 0.05&deg; spatial resolution and biweekly temporal resolution in NetCDF format. Each month is divided into two files, with the first file &ldquo;a&rdquo; representative of the 1<sup>st</sup> day to the 15<sup>th</sup> day of a month, and the second file &ldquo;b&rdquo; representative of the 16<sup>th</sup> day to the last day of a month.</p> <p><strong>Abstract:</strong></p> <p>Satellite-observed solar-induced chlorophyll fluorescence (SIF) is a powerful proxy for the photosynthetic characteristics of terrestrial ecosystems. Direct SIF observations are primarily limited to the recent decade, impeding their application in detecting long-term dynamics of ecosystem function. In this study, we leverage two surface reflectance bands available both from Advanced Very High-Resolution Radiometer (AVHRR, 1982-2023) and MODerate-resolution Imaging Spectroradiometer (MODIS, 2001-2023). Importantly, we calibrate and orbit-correct the AVHRR bands against their MODIS counterparts during their overlapping period. Using the long-term bias-corrected reflectance data from AVHRR and MODIS, a neural network is trained to produce a Long-term Continuous SIF-informed Photosynthesis Proxy (LCSPP) by emulating Orbiting Carbon Observatory-2 SIF, mapping it globally over the 1982-2023 period. Compared with previous SIF-informed photosynthesis proxies, LCSPP has similar skill but can be advantageously extended to the AVHRR period. Further comparison with three widely used vegetation indices (NDVI, kNDVI, NIRv) shows a higher or comparable correlation of LCSPP with satellite SIF and site-level GPP estimates across vegetation types, ensuring a greater capacity for representing long-term photosynthetic activity.</p> <p>&nbsp;</p>

opencc-by-4.0Dec 2023View details →
zenodo36/100

Senator Beck Basin Radiative Forcing at MODIS overpass (2005-2023 WY)

<p>Data used in:&nbsp;</p> <p>Naple, P., Skiles, S. M., Lang, O. I., Rittger, K., Lenard, S. J. P., Burgess, A., Painter, T. H. (2023). Dust 774 on snow radiative forcing and contribution to melt in the Colorado River Basin over the MODIS record. 775 ESS Open Archive. https://doi.org/10.22541/essoar.172987451.11953219/v1</p> <p>This is qa/qc'd radiative forcing validation data from two snow energy balance instrumentation towers in Senator Beck Basin Study Area, San Juan Mountains, CO. Measurements are from nearest hour to MODIS overpass</p> <p>All data originates from the Center for Snow and Avalanche Studies, and if used they should be recognized, please see their&nbsp;data policy:&nbsp;<a href="https://snowstudies.org/csas-archival-data/">https://snowstudies.org/csas-archival-data/</a>&nbsp;</p> <p>Radiative forcing is calculated using Equation 1 from Painter et al. 2007</p> <p>&nbsp;</p> <p>Painter, T. H., Barrett, A. P., Landry, C. C., Neff, J. C., Cassidy, M. P., Lawrence, C. R., ... &amp; Farmer, G. L. (2007). Impact of disturbed desert soils on duration of mountain snow cover. <em>Geophysical Research Letters</em>, <em>34</em>(12).</p>

opencc-by-4.0Oct 2023View details →
zenodo36/100

AnisoVeg: Anisotropy and Nadir-normalized MODIS MAIAC datasets for satellite vegetation studies in South America

<p><strong>Dataset paper under review.</strong></p> <p><strong>Contact Ricardo Dalagnol (ricds@hotmail.com) for more information.</strong></p> <p>&nbsp;</p> <p><strong>Data:</strong>&nbsp;AnisoVeg: Anisotropy and Nadir-normalized MODIS MAIAC datasets for satellite vegetation studies in South America</p> <p><strong>Scale factor</strong>: 10000</p> <p><em>obs: the no_samples layer does not have scale.</em></p> <p><strong>Coverage:</strong>&nbsp;South America land</p> <p><strong>Time period:</strong>&nbsp;2000 to 2021&nbsp;(starting in March 2000)</p> <p><strong>Spatial resolution:</strong>&nbsp;0.009107388 degree equivalent to ~1 km</p> <p><strong>Temporal resolution:</strong>&nbsp;Monthly</p> <p><strong>Coordinate reference system:</strong>&nbsp;geographic projection, datum WGS-84</p> <p><strong>Processing details summary (more detailed explanation in the&nbsp;paper):</strong></p> <ul> <li>The original MODIS (MAIAC) data were described by Lyasputin et al. 2011 (<a href="https://doi.org/10.1029/2010JD014986">https://doi.org/10.1029/2010JD014986</a>). The daily MODIS (MAIAC) surface reflectance data from collection 6, acquired from Terra and Aqua satellites, are available from the MCD19A1 product (<a href="https://ladsweb.modaps.eosdis.nasa.gov/archive/allData/6/MCD19A1">https://ladsweb.modaps.eosdis.nasa.gov/archive/allData/6/MCD19A1</a>). The Bidirectional Reflectance Distribution Function (BRDF) model parameters are available from MCD19A3 product (<a href="https://ladsweb.modaps.eosdis.nasa.gov/archive/allData/6/MCD19A3">https://ladsweb.modaps.eosdis.nasa.gov/archive/allData/6/MCD19A3</a>)</li> <li>The daily MCD19A1 data at 1 km spatial resolution were normalized using the BRDF parameters and Ross-Thick Li-Sparse (RTLS) model considering (1) a fixed nadir view and a 45 deg.&nbsp;solar zenith angle&nbsp;using the parameters from the MCD19A3 product; and (2) backward and forward scattering. For the nadir (NAD) product, the nadir normalization was taken. For the anisotropy (ANI) product, we calculated the backward minus forward surfaces for each layer, resulting in the ANI product.</li> <li>The daily data were aggregated into monthly composites by the pixel&rsquo;s median.</li> <li>The tiles that cover the South America were mosaicked and re-projected from sinusoidal to geographic projection</li> <li>The Normalized Difference Vegetation Index (NDVI) and Enhanced Vegetation Index (EVI) were calculated using standard formulas. The EVI parameters were: C1 = 6, C2 = 7.5, L = 1, G = 2.5</li> </ul> <p><strong>File(s) format:</strong></p> <ul> <li>Zip files&nbsp;- one per year. NAD are the nadir-normalized products and ANI the anisotropy.&nbsp;Inside zip files there are&nbsp;raster files with &quot;.tif&quot; format, one per month window.</li> <li>The filename syntax is &quot;maiac_southamerica_month_PRODUCT_YYYY_MM_LAYER_latlon.tif&quot;, where YYYY is the year (e.g. 2000), MM is the month with two digits (e.g. 03 for March), PRODUCT is either nadir or anisotropy, and LAYER can be bands 1-8, EVI and NDVI.</li> <li>There is also the number of samples (no_samples) layers for each date, which can be used to filter composites with a minimum desirable number of daily observations.&nbsp;</li> </ul> <p>&nbsp;</p> <p><strong>Code:</strong>&nbsp;<a href="https://github.com/ricds/maiac_processing">https://github.com/ricds/maiac_processing</a></p> <p>&nbsp;</p> <p><strong>Acknowledgements:</strong>&nbsp;R.D. was supported by Sao Paulo Research Foundation (FAPESP) grants 2015/22987-7 and 2019/21662-8. FHW was supported by FAPESP grant 2015/50484-0. Part of this work was carried out at the Jet Propulsion Laboratory, California Institute of Technology, under a contract with the National Aeronautics and Space Administration (NASA). The funders had no role in the study design, data collection and analysis, including the decision to publish or prepare the manuscript. We thank the MODIS MAIAC team from NASA for providing the freely available MODIS (MAIAC) daily dataset.</p> <p>&nbsp;</p> <p><strong>Auxiliary data of AnisoVeg:</strong></p> <ul> <li>Backscattering data of AnisoVeg:&nbsp;<a href="https://doi.org/10.5281/zenodo.6040299">https://doi.org/10.5281/zenodo.6040299</a> and&nbsp;<a href="https://doi.org/10.5281/zenodo.6040790">https://doi.org/10.5281/zenodo.6040790</a></li> <li>Forward scattering data of AnisoVeg:&nbsp;<a href="https://doi.org/10.5281/zenodo.6048784">https://doi.org/10.5281/zenodo.6048784</a> and&nbsp;<a href="https://doi.org/10.5281/zenodo.6048793">https://doi.org/10.5281/zenodo.6048793</a></li> </ul> <p>&nbsp;</p> <p><strong>Layers available at Google Earth Engine (GEE):</strong></p> <ul> <li>EVI Anisotropy:&nbsp;<a href="https://code.earthengine.google.com/?asset=projects/anisoveg/assets/evi_anisotropy">https://code.earthengine.google.com/?asset=projects/anisoveg/assets/evi_anisotropy</a></li> <li>EVI Nadir:&nbsp;<a href="https://code.earthengine.google.com/?asset=projects/anisoveg/assets/evi_nadir">https://code.earthengine.google.com/?asset=projects/anisoveg/assets/evi_nadir</a></li> </ul> <p>Obs: these require&nbsp;a (free) google earth engine account.</p> <p>&nbsp;</p> <p><strong>Dataset usage</strong>: This dataset is a product of hundreds of hours of coding starting in 2016 with the first author PhD work and then into his Postdoc, and many more hundreds hours of data processing.&nbsp;Data is free to use, but if you use this dataset, please cite the dataset paper or this repository (while paper is under review). Invitation for collaboration are welcomed.</p> <ul> </ul> <p>&nbsp;</p> <p><strong>While the paper is under review, for use of this dataset please cite:</strong></p> <p>Dalagnol, Ricardo; Galv&atilde;o, L&ecirc;nio Soares; Wagner, Fabien Hubert; Moura, Yhasmin Mendes; &nbsp;Gon&ccedil;alves, Nathan; Wang, Yujie; Lyapustin, Alexei; Yang, Yan; Saatchi, Sassan; Arag&atilde;o, Luiz Eduardo Oliveira e Cruz.&nbsp;(2022). &quot;AnisoVeg: Anisotropy and Nadir-normalized MODIS MAIAC datasets for satellite vegetation studies in South America&quot;. (Version v1) [Data set]. Zenodo.&nbsp;https://doi.org/10.5281/zenodo.3878879</p>

opencc-by-4.0Feb 2022View details →
zenodo36/100

MODYS-video: 2D Human pose estimation data and Dyskinesia Impairment Scale scores from children and young adults with dyskinetic cerebral palsy

<p>The dataset contains the 2D coordinates in pixels of body landmarks (wrists, ankles, shoulders, hips, knees and ankles) extracted from 188 videos of 34 children with dyskinetic cerebral palsy using DeepLabCut [1] and appertaining clinical scores of the Dyskinesia Impairment Scale (DIS) [2].</p> <p>The videos were collected during the item &ldquo;lying in rest&rdquo; and &ldquo;sitting in rest&rdquo; of the DIS&nbsp;at three time points during a clinical trial on the effect of intrathecal baclofen [3]. Children had a mean age of 14y2m (SD 4.0), 26 were male. Their gross motor function classification system level ranged from IV-V and their manual ability classification system level from III-V. Original videos have length of 4-35 seconds with a resolution of 720x575 pixels and are sampled with 25 Hz. We added stick figures to complement the data for context and ease of understanding. They were created from the 2D coordinates that were extracted with a likelihood &gt;0.8.</p> <p>Clinical scoring was performed by three trained experts (according to the DIS) on the original videos. Within the items &ldquo;lying in rest&rdquo; and &ldquo;sitting in rest&rdquo; the amplitude and duration of dystonia and choreoathetosis of the trunk, proximal right arm, proximal left arm, proximal right leg and proximal left leg are scored on a 0-4 ordinal scale and calculated towards a percentage score between 0-1.</p> <p>The dataset can be used in a machine learning approach to automatically assess dystonia and choreoathetosis of children with dyskinetic cerebral palsy using 2D coordinates of body points extracted from videos.</p> <p>&nbsp;</p> <p>References:</p> <p>1.&nbsp;Mathis, A., et al., DeepLabCut: markerless pose estimation of user-defined body parts with deep learning. Nat Neurosci, 2018. 21(9): p. 1281-1289.</p> <p>2.&nbsp;Monbaliu, E., et al., The dyskinesia Impairment Scale: a new instrument to measure dystonia and choreoathetosis in dyskinetic cerebral palsy. Dev Med Child Neurol, 2012. 54: p. 278-283.</p> <p>3.&nbsp;Bonouvrie, L.A., et al., The Effect of Intrathecal Baclofen in Dyskinetic Cerebral Palsy: The IDYS Trial. Ann Neurol, 2019. 86: p. 79-90.</p> <p>&nbsp;</p> <p>&nbsp;</p>

opencc-by-4.0Nov 2021View details →
zenodo36/100

Global Daily Surface Blue-sky Albedo Climatology and Land Cover Climatology Dataset from 20-year MODIS Products (500m)

<p>Only the first days of each month were uploaded to Zenodo due to the data storage limitation, and the full dataset is available at http://glass.umd.edu/albedo_clim/.</p> <p>Surface albedo plays a critical role in climate, hydrological, and biogeochemical modeling and weather forecasting.&nbsp;Therefore, precisely mapping surface albedo climatology globally is necessary to better parameterize environmental systems.&nbsp;We generated a new global surface blue-sky actual and snow-free albedo climatology dataset from 20-year MODIS products from the Google Earth Engine (GEE).&nbsp;</p> <p>The 500m global surface blue-sky daily albedo climatology dataset follows the basic MODIS product format and employed the sinusoidal projection.&nbsp; It includes historical and snow-free blue-sky albedo climatology data.&nbsp;For application convenience, the land cover climatology of MODIS product (MCD12Q1) is also generated and attached.&nbsp;The International Geosphere-Biosphere Programme (IGBP) and PFT classification climatology of MCD12Q1 since 2001&nbsp;were also generated.</p>

opencc-by-4.0Mar 2022View details →
zenodo36/100

Ocean Color Data: Modis-aqua_chl-a (JJA, 2002-2018)

<p>Ocean Color Data: Modis-aqua_chl-a (JJA, 2002-2018)&nbsp; downloaded from the ADAM Platform (https://reliance.adamplatform.eu/) used furing the FORCeS eScience course &#39;Tools in Climate Science: Linking Observations with Modelling&#39;.</p> <p>&nbsp;</p> <p>MODIS Chlorophyll-a Concentration This algorithm returns the near-surface concentration of chlorophyll-a (chlor_a) in mg m-3, calculated using an empirical relationship derived from in situ measurements of chlor_a and remote sensing reflectances (Rrs) in the blue-to-green region of the visible spectrum. The implementation is contingent on the availability three or more sensor bands spanning the 440 - 670 nm spectral regime. The algorithm is applicable to all current ocean color sensors. The chlor_a product is included as part of the standard Level-2 OC product suite and the Level-3 CHL product suite. The current implementation for the default chlorophyll algorithm (chlor_a) employs the standard OC3/OC4 (OCx) band ratio algorithm merged with the color index (CI) of Hu et al. (2012). As described in that paper, this refinement is restricted to relatively clear water, and the general impact is to reduce artifacts and biases in clear-water chlorophyll retrievals due to residual glint, stray light, atmospheric correction errors, and white or spectrally-linear bias errors in Rrs. As implemented, the algorithm diverges slightly from what was published in Hu et al. (2012) in that the transition between CI and OCx now occurs at 0.15 &lt; CI &lt; 0.2 mg/m3 to ensure a smooth transition.</p> <p>&nbsp;</p>

opencc-by-4.0Mar 2022View details →
zenodo36/100

ACIA500: a 500 m annual cropping intensity dataset for monsoon Asia based on MODIS data

<p>This dataset provides 500m-grid crop intensity map of monsoon Asia (some countries) from 2001&nbsp;to 2021.</p> <p>***&nbsp;Updated crop intensity map for 2021</p> <p>*** The data file is in &ldquo;.tif&quot; format</p> <p>*** Temporal Resolution: Yearly</p> <p>*** Pixel size: 500 m</p> <p>*** Projection information: EPSG: 4326</p> <p>The map boundary employed in this database does not imply the expression of any opinion whatsoever on the part of us concerning the legal status of any country, territory, city or area or its authorities, or concerning the delimitation of its frontiers or boundaries.</p>

opencc-by-4.0Sep 2021View details →
dryad36/100

Discrete fire events, their severity, and their ignitions, as derived from MODIS MCD 14ML active-fire detection data for Indonesia, 2002-2019

<p class="MsoNormal"><strong><span>1. PUBLICATION CORRESPONDING TO THESE DATA</span></strong></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Sloan, Sean*; Locatelli, Bruno; Andela, Niels; Cattau, Megan E.; Gaveau, David; Tacconi, Luca. 2022 'Declining Severe Fire Activity on Managed Lands in Equatorial Asia'. <em>Communications Earth &amp; Environment</em>. DOI: 10.1038/s43247-022-00522-6.</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>*Corresponding author email: sean.sloan@viu.ca</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><strong><span>2. ABSTRACT OF THE DATA</span></strong></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>The GIS data and corresponding attribute data described here pertain to discrete fire events, their severity, and their ignitions, as derived on the basis of daily MODIS Collection 6 MCD14ML active-fire detections (AFDs).  Data on fire events and their ignitions are provided separately, as two data files.  These data files on fire events and ignitions may however be linked to each other by the data user.  Fire-event severity is quantified per fire event and reported in the data file for fire events.</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>A fire event is a cluster of MODIS Collection 6 MCD14ML active-fire detections (AFDs) wherein each AFD has a spatial (&lt;=1-km) and temporal (&lt;=4-day) proximity to another AFD in the same fire event, inferring thus a relational co-occurrence amongst AFDs in time and space.  In other words, a fire event is considered a likely occasion of burning wherein all constituent AFDs are related to each other in time and space, either directly (as for proximate AFDs) or indirectly (as in the case of a large area of fire activity that spread progressively over time and space from an initial source). </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Each fire event has a designated ignition AFD, being the AFD of the fire event with the earliest detection date.  A given fire event can have more than one ignition AFD if the ignitions all share same earliest detection date.  The ignition AFD(s) is the nominal initial source of the burning described by the corresponding fire event.  All other, non-ignition AFDs of a fire event are deemed its 'propagation' AFDs, since these AFDs follow from the ignitions, temporally and spatially.</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>See Figure 4 in the publication by Sloan et al. for an illustration of the geography of fire events and their ignition AFDs.  </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Fire events and their ignitions were derived from standard science-quality MODIS Collection 6 MCD 14ML AFD data, commonly referred to as fire 'hotspot' data.  Data were detected by both the Terra and Aqua satellite sensors daily for Indonesia between July 2002 and December 2019.  Information on these input data are provide by the two citations below.  The publication of Sloan et al. provides methodological details on how the MODIS Collection 6 MCD 14ML AFD data were processed into discrete fire events and ignitions. </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>EarthData. MODIS Collection 6 Active-Fire Detections standard scientific data (MCD14ML), NASA EarthData, https://earthdata.nasa.gov/firms (2019).</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Giglio, L., Schroeder, W. &amp; Justice, C. O. The Collection 6 MODIS active fire detection algorithm and fire products. <em>Remote Sensing of Environment</em> 178, 31-41, (2016).</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>  </span></p> <p class="MsoNormal"><strong><span>3. DATA FILES</span></strong></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Two data files are distributed here – one for discrete fire events, and another for the ignition AFDs of each fire event.  The data files are provided in a GIS-compatible format, and also as a generic text format, as described below.</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><strong><span>3.1 GIS VERSION</span></strong></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Data files in GIS-compatible format are provided as 'feature classes' within an ArcGIS file geodatabase 'Sloan_MODIS_FireEvents_Ignitions_2002_2019.gdb'.  These data files can be viewed and manipulated using either ArcGIS Desktop or ArcGIS Pro software.  There is one feature class for fire events, and another file for ignitions.</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><u><span>Sloan_MODIS_FireEvents_Ignitions_2002_2019.gdb\nfire4_all_spatial_fire_2002_2019_joins_sp_LC</span></u></p> <p class="MsoNormal"><span>This file pertains to fire events.  All AFDs of a given fire event are included, without differentiation as to whether the AFDs are ignition AFDs or other (propagation) AFDs.  Fire events are assigned unique ID values and basic attribute data.</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><u><span>Sloan_MODIS_FireEvents_Ignitions_2002_2019.gdb\nfire4_all_spatial_fire_2002_2019_igs_sp_LC</span></u></p> <p class="MsoNormal"><span>This file pertains to ignitions. Only ignition AFDs are included for a given fire event.  Fire events corresponding to the ignitions are assigned unique ID values and basic attribute data.</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><strong><span>3.2 CSV TEXT VERSION</span></strong></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Both data files are also supplied as comma-separated value (CSV) text files for viewing and manipulation in non-GIS software, such as Excel, text editors, or any statistical software.  The text files can also be read into various GIS software.  CSV-formatted files have the same file name and attribute fields as the corresponding GIS-formatted data files.  These CSV-formatted data files (as well as the GIS-formatted data files) include attribute data on the latitude and the longitude of each AFD.  </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Attribute field names are included as the first row of values in a CSV file.  </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>No 'text qualifiers' like quotations (" ") or inverted commas ('') are used to designate text/string values within the CSV file.  Text values appear directly between commas in the CSV data file, e.g.,  …,Kalimantan_Southern,…  .</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Note two points of caution for working with these CSV data:</span></p> <p class="MsoListParagraphCxSpFirst"><span> </span></p> <p class="MsoListParagraphCxSpMiddle"><span>i)<span>                    </span></span><span>Microsoft Excel may be used for a partial view of the data file nfire4_all_spatial_fire_2002_2019_joins_sp_LC.csv, but it is not recommended for working with this data file.  This is because the number of records/rows in this csv file slightly exceeds that maximum that may be read by Excel, which is just over 1 million.  This limitation does not apply to the other csv file, however.</span></p> <p class="MsoListParagraphCxSpMiddle"><span> </span></p> <p class="MsoListParagraphCxSpLast"><span>ii)<span>                  </span></span><span>The GIS-formatted data files employ 'null values' in their attribute tables, and so the corresponding 'values' in the CSV-formatted data files are similarly null.  For null values, no value whatsoever is ascribed, not even 0.  In the syntax of a CSV file (apparent upon opening the file in any text editor like Microsoft Notepad), a null value is denoted by two consecutive commas without any value, text, or space between them.  If a CSV file were opened in Excel, a cell assigned a null value would be blank, not 0 or otherwise.  This denotes the correct transcription of the GIS-formatted data.  This feature will not impede the correct reading of these CSV data by whatever software.  Users are made aware of this feature merely to ensure the proper input of these data into whatever software.</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><strong><span>4. DATA STRUCTURE / GEOGRAPHY</span></strong></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>The GIS-formatted data files are 'point data', i.e., they map the geography of AFDs as individual 'points', in keeping with how these MODIS MCD14ML AFD data were originally structured.  For the GIS-formatted data files, each record/row in its corresponding attribute tables corresponds <em>geographically</em> to single AFD 'point', regardless of whether that AFD belongs to a fire event comprised of many AFDs.  In the parlance of GIS files, the files depict 'single-part' point features.  The unique ID field [nfireID2] serves to denote the fire event to which a given AFD belongs.</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Similarly, for the CSV-formatted data files, each record/row of values corresponds to a single AFD.</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>There are 1,232,377 records for the data file 'nfire4_all_spatial_fire_2002_2019_joins_sp_LC'.</span></p> <p class="MsoNormal"><span>There are 720795 records for the data file 'nfire4_all_spatial_fire_2002_2019_igs_sp_LC'.</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><strong><span>5. ATTRIBUTE FIELDS</span></strong></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>In the data files, while some attribute fields pertain to the individual AFD as the unit of observation (e.g., the land-cover class coincident with the AFD), other attribute fields correspond to the larger 'fire event' to which the individual AFD belongs (e.g., the total duration of fire activity for the fire event).  Accordingly, for certain attribute fields pertaining to the fire event as a whole, their values will appear 'duplicated' in the data file amongst those individual AFDs (records) that constitute the fire event in question.  Whether a given attribute field pertains to the individual AFD or to its constituent fire event is denoted below for each field.  </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Each AFD is assigned a unique ID field denoting its constituent fire event, [nfireID2].  This field is consistent between both data files, so that attribute data for a given fire event may be 'matched' to attribute data for its corresponding ignition AFD(s), and vice versa, on the basis of the common value of the field [nfireID2].</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Note that many attributes below are as originally defined/measured by the input MCD 14ML data, or are derived directly thereof. </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><strong><span>5.1 DATASET nfire4_all_spatial_fire_2002_2019_joins_sp_LC</span></strong></p> <p class="MsoNormal"><span> </span></p> <table class="MsoTableGrid"> <tbody> <tr> <td> <p class="MsoNormal"><strong><span>Field Name</span></strong></p> </td> <td> <p class="MsoNormal"><strong><span>Geography of Attribute Value</span></strong></p> </td> <td> <p class="MsoNormal"><strong><span>Definition</span></strong></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>OID</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Object ID value. Unique values for each AFD (record) in the GIS-formatted data file when viewed in ArcGIS. Field values are -1 in the CSV-formatted data file.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>Peat</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Denotes whether the AFD occurs on peatlands (value=1) as defined in Sloan et al.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MIN_CONFIDE</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The minimum detection confidence of all AFDs in the fire event, where confidence ranges from 1-100%. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MAX_CONFIDE</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The maximum detection confidence of all AFDs in the fire event, where confidence ranges from 1-100%. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MEAN_CONFIDE</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The mean detection confidence of all AFDs in the fire event, where confidence ranges from 1-100%. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>STD_CONFIDE</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The standard deviation of detection confidence of all AFDs in the fire event, where confidence ranges from 1-100%. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>SUM_FRP</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The sum total of all fire-radiative power (FRP) measures for all AFDs in the fire event. Units are megawatts. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MEAN_FRP</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The mean of all fire-radiative power (FRP) measures for all AFDs in the fire event. Units are megawatts. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MIN_FRP</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The minimum of all fire-radiative power (FRP) measures for all AFDs in the fire event. Units are megawatts. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MAX_FRP</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The maximum of all fire-radiative power (FRP) measures for all AFDs in the fire event. Units are megawatts. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MEAN_LATITUD</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The mean latitude of all AFDs in the fire event. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MEAN_LONGITU</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The mean longitude of all AFDs in the fire event. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MIN_ACQ_DAT</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The minimum acquisition date of all AFDs in the fire event (i.e., the ignition AFD detection date). </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MAX_ACQ_DAT</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The maximum acquisition date of all AFDs in the fire event (i.e., the ignition AFD detection date). </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MIN_acq_yer</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The year in which the earliest AFD of the fire event was detected. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MIN_acq_mnt</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The month in which the earliest AFD of the fire event (i.e., ignition AFD) was detected. Months are coded numerically, e.g., 1=January, 12=December.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MAX_acq_mnt</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The month in which the latest AFD of the fire event was detected. Months are coded numerically, e.g., 1=January, 12=December.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MIN_yday</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The detection day of year of the earliest AFD of the fire event, i.e., ignition AFD. Day of year is denoted numerically, where 1=January 1 and 365=December 31.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MAX_yday</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The detection day of year of the latest AFD of the fire event, i.e., ignition AFD. Day of year is denoted numerically, where 1=January 1 and 365=December 31.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>RANGE_yday</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The number of days of duration of the fire event, defined as [MAX_yday]-[MIN_yday]</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>FIRST_subst_r</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Text labels denoting the Indonesian island/region of data processing, e.g., Kalimantan, Papua.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>AF_Count</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>Number of AFDs in the fire event.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>nfireID2</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The unique ID of the fire event to which the AFD belongs.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>Island</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Numerical values coding for major Indonesian islands/region: 1000000=Sumatra; 2000000=Kalimantan; 3000000=Sulawesi; 4000000=Papua.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>FRP_Days</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The severity of the fire event, as defined by Sloan et al., equal to [Sum_FRP] * ([Range_yday]+1).</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>IG_Count</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>Number of ignition AFDs in the fire event</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2002</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> <td> <p class="MsoNormal"><span>The land-cover class coincident with the AFD. The class is coded by a numerical value as per the left-most column in the table in Section 5.3.  The class is that observed for the calendar year in which the AFD occurred, where the year #### is denoted in the field name 'CCI_LC####'.  The land-cover data source is as described in Section 5.3.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2003</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2004</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2005</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2006</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2007</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2008</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2009</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2010</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2011</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2012</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2013</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2014</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2015</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2016</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2017</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2018</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2019</span></p> </td> <td> <p class="MsoNormal"><span> </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>Region</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Text labels denote whether the AFD occurs within one of the two focal regions of Sloan et al.: Southern Kalimantan, or Central South Sumatra. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>POINT_X</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Longitude, given as decimal degrees with WGS84 datum.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>POINT_Y</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Latitude, given as decimal degrees with WGS84 datum.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>POINT_Z</span></p> </td> <td> <p class="MsoNormal"><span>--</span></p> </td> <td> <p class="MsoNormal"><span>Ignore.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>POINT_M</span></p> </td> <td> <p class="MsoNormal"><span>--</span></p> </td> <td> <p class="MsoNormal"><span>Ignore.</span></p> </td> </tr> </tbody> </table> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><strong><span>5.2 DATASET nfire4_all_spatial_fire_2002_2019_igs_sp_LC</span></strong></p> <p class="MsoNormal"><span> </span></p> <table class="MsoTableGrid"> <tbody> <tr> <td> <p class="MsoNormal"><strong><span>Field Name</span></strong></p> </td> <td> <p class="MsoNormal"><strong><span>Geography of Attribute Value</span></strong></p> </td> <td> <p class="MsoNormal"><strong><span>Definition</span></strong></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>OID</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Object ID value. Unique values for each AFD (record) in the GIS-formatted data file when viewed in ArcGIS. Field values are -1 in the CSV-formatted data file.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>IG_Count</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>Number of ignition AFDs in the fire event.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MIN_acq_yer</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The year in which the earliest AFD of the fire event was detected. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MIN_acq_mnt</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The month in which the earliest AFD of the fire event (i.e., ignition AFD) was detected. Months are coded numerically, e.g., 1=January, 12=December.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>FIRST_subst_r</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Text labels denoting the Indonesian island/region of data processing, e.g., Kalimantan, Papua.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>MIN_yday</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The detection day of year of the earliest AFD of the fire event, i.e., ignition AFD. Day of year is denoted numerically, where 1=January 1 and 365=December 31.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>nfireID2</span></p> </td> <td> <p class="MsoNormal"><span>Fire Event</span></p> </td> <td> <p class="MsoNormal"><span>The unique ID of the fire event to which the AFD belongs.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2002</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>The land-cover class coincident with the AFD. The class is coded by a numerical value as per the left-most column in the table in Section 5.3.  The class is that observed for the calendar year in which the AFD occurred, where the year #### is denoted in the field name 'CCI_LC####'.  The land-cover data source is as described in Section 5.3.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2003</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2004</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2005</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2006</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2007</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2008</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2009</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2010</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2011</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2012</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2013</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2014</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2015</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2016</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2017</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2018</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>CCI_LC2019</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>Region</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Text labels denote whether the AFD occurs within one of the two focal regions of Sloan et al.: Southern Kalimantan, or Central South Sumatra. </span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>Peat</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Denotes whether the AFD occurs on peatlands (value=1) as defined in Sloan et al.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>POINT_X</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Longitude, given as decimal degrees with WGS84 datum.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>POINT_Y</span></p> </td> <td> <p class="MsoNormal"><span>AFD</span></p> </td> <td> <p class="MsoNormal"><span>Latitude, given as decimal degrees with WGS84 datum.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>POINT_Z</span></p> </td> <td> <p class="MsoNormal"><span>--</span></p> </td> <td> <p class="MsoNormal"><span>Ignore.</span></p> </td> </tr> <tr> <td> <p class="MsoNormal"><span>POINT_M</span></p> </td> <td> <p class="MsoNormal"><span>--</span></p> </td> <td> <p class="MsoNormal"><span>Ignore.</span></p> </td> </tr> </tbody> </table> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><strong><span>5.3. LAND-COVER ATTRIBUTE DATA</span></strong></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>As noted in Section 5.1 and Section 5.2, the nominal values of the attribute fields 'CCI_LC####' correspond to column 1 of the table below.  These hierarchical values, and their corresponding land-cover classes labels in column 2 of the table, pertain to the land-cover classification of the Copernicus Climate Change Initiative Land-Cover Product of the European Space Agency.   This classification has an annual temporal resolution and 300-meter spatial resolution.  Pertinent citations for these land-cover data are below:</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>ESA. Annual land-cover product, 1992 to 2019/present, based on MERIS 300-m and ancillary SPOT, AVHRR, Sentinel-3 and PROB-V satellite data. European Space Agency (ESA) European Centre for Medium-Range Weather Forecasts (ECMFW) Copernicus Climate Change Service (C3S) Climate Change Initiative (CCI), </span><span><a href="https://cds.climate.copernicus.eu/cdsapp#!/dataset/satellite-land-cover?tab=overview"><span>https://cds.climate.copernicus.eu/cdsapp#!/dataset/satellite-land-cover?tab=overview</span></a></span><span>; </span><span><a href="http://maps.elie.ucl.ac.be/CCI/viewer/download.php"><span>http://maps.elie.ucl.ac.be/CCI/viewer/download.php</span></a></span><span>; </span><span><a href="http://www.esa-landcover-cci.org/"><span>http://www.esa-landcover-cci.org/</span></a></span><span> (2020).</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Pérez-Hoyos, A., Rembold, F., Kerdiles, H. &amp; Gallego, J. Comparison of global land cover datasets for cropland monitoring. <em>Remote Sensing</em> 9, (2017).</span></p> <p class="MsoNormal"><span> </span></p> <p class="MsoNormal"><span>Columns 3 and 4 in the table below illustrate how the original land-cover classes of the Copernicus Climate Change Initiative Land-Cover Product were reclassified for analysis in Sloan et al.   </span></p> <p class="MsoNormal"><em><span> </span></em></p> <table class="MsoNormalTable"> <tbody> <tr> <td> <p class="TableParagraph"><strong><span>1. CCI-LC Class Value</span></strong></p> </td> <td> <p class="TableParagraph"><strong><span>2. CCI-LC Class Label</span></strong></p> </td> <td> <p class="TableParagraph"><strong><span>3. New Class Value for Sloan et al.</span></strong></p> </td> <td> <p class="TableParagraph"><strong><span>4. New Class Label for Sloan et al.</span></strong></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>0</span></p> </td> <td> <p class="TableParagraph"><span>No Data</span></p> </td> <td> <p class="TableParagraph"><span>0</span></p> </td> <td> <p class="TableParagraph"><span>No Data</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>10</span></p> </td> <td> <p class="TableParagraph"><span>Cropland, rainfed</span></p> </td> <td> <p class="TableParagraph"><span>1</span></p> </td> <td> <p class="TableParagraph"><span>Cleared/Cultivated</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>11</span></p> </td> <td> <p class="TableParagraph"><span>Herbaceous cover</span></p> </td> <td> <p class="TableParagraph"><span>1</span></p> </td> <td> <p class="TableParagraph"><span>Cleared/Cultivated</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>12</span></p> </td> <td> <p class="TableParagraph"><span>Tree or shrub cover</span></p> </td> <td> <p class="TableParagraph"><span>1</span></p> </td> <td> <p class="TableParagraph"><span>Cleared/Cultivated</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>20</span></p> </td> <td> <p class="TableParagraph"><span>Cropland, irrigated or post‐flooding</span></p> </td> <td> <p class="TableParagraph"><span>1</span></p> </td> <td> <p class="TableParagraph"><span>Cleared/Cultivated</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>30</span></p> </td> <td> <p class="TableParagraph"><span>Mosaic cropland (&gt;50%) / natural vegetation (tree, shrub, herbaceous cover) (&lt;50%)</span></p> </td> <td> <p class="TableParagraph"><span>2</span></p> </td> <td> <p class="TableParagraph"><span>Mosaic Cropland</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>40</span></p> </td> <td> <p class="TableParagraph"><span>Mosaic natural vegetation (tree, shrub, herbaceous cover) (&gt;50%) / cropland (&lt;50%)</span></p> </td> <td> <p class="TableParagraph"><span>3</span></p> </td> <td> <p class="TableParagraph"><span>Mosaic Natural Veg</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>50</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, broadleaved, evergreen, closed to open (&gt;15%)</span></p> </td> <td> <p class="TableParagraph"><span>4</span></p> </td> <td> <p class="TableParagraph"><span>Forest</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>60</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, broadleaved, deciduous, closed to open (&gt;15%)</span></p> </td> <td> <p class="TableParagraph"><span>4</span></p> </td> <td> <p class="TableParagraph"><span>Forest</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>61</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, broadleaved, deciduous, closed (&gt;40%)</span></p> </td> <td> <p class="TableParagraph"><span>4</span></p> </td> <td> <p class="TableParagraph"><span>Forest</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>62</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, broadleaved, deciduous, open (15‐40%)</span></p> </td> <td> <p class="TableParagraph"><span>4</span></p> </td> <td> <p class="TableParagraph"><span>Forest</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>70</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, needleleaved, evergreen, closed to open (&gt;15%)</span></p> </td> <td> <p class="TableParagraph"><span>4</span></p> </td> <td> <p class="TableParagraph"><span>Forest</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>71</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, needleleaved, evergreen, closed (&gt;40%)</span></p> </td> <td> <p class="TableParagraph"><span>4</span></p> </td> <td> <p class="TableParagraph"><span>Forest</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>72</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, needleleaved, evergreen, open (15‐40%)</span></p> </td> <td> <p class="TableParagraph"><span>4</span></p> </td> <td> <p class="TableParagraph"><span>Forest</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>80</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, needleleaved, deciduous, closed to open (&gt;15%)</span></p> </td> <td> <p class="TableParagraph"><span>4</span></p> </td> <td> <p class="TableParagraph"><span>Forest</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>81</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, needleleaved, deciduous, closed (&gt;40%)</span></p> </td> <td> <p class="TableParagraph"><span>4</span></p> </td> <td> <p class="TableParagraph"><span>Forest</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>82</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, needleleaved, deciduous, open (15‐40%)</span></p> </td> <td> <p class="TableParagraph"><span>4</span></p> </td> <td> <p class="TableParagraph"><span>Forest</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>90</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, mixed leaf type (broadleaved and needleleaved)</span></p> </td> <td> <p class="TableParagraph"><span>4</span></p> </td> <td> <p class="TableParagraph"><span>Forest</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>100</span></p> </td> <td> <p class="TableParagraph"><span>Mosaic tree and shrub (&gt;50%) / herbaceous cover (&lt;50%)</span></p> </td> <td> <p class="TableParagraph"><span>5</span></p> </td> <td> <p class="TableParagraph"><span>Mosaic Shrubland</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>110</span></p> </td> <td> <p class="TableParagraph"><span>Mosaic herbaceous cover (&gt;50%) / tree and shrub (&lt;50%)</span></p> </td> <td> <p class="TableParagraph"><span>5</span></p> </td> <td> <p class="TableParagraph"><span>Mosaic Shrubland</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>120</span></p> </td> <td> <p class="TableParagraph"><span>Shrubland</span></p> </td> <td> <p class="TableParagraph"><span>6</span></p> </td> <td> <p class="TableParagraph"><span>Low/Sparse Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>121</span></p> </td> <td> <p class="TableParagraph"><span>Evergreen shrubland</span></p> </td> <td> <p class="TableParagraph"><span>6</span></p> </td> <td> <p class="TableParagraph"><span>Low/Sparse Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>122</span></p> </td> <td> <p class="TableParagraph"><span>Deciduous shrubland</span></p> </td> <td> <p class="TableParagraph"><span>6</span></p> </td> <td> <p class="TableParagraph"><span>Low/Sparse Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>130</span></p> </td> <td> <p class="TableParagraph"><span>Grassland</span></p> </td> <td> <p class="TableParagraph"><span>6</span></p> </td> <td> <p class="TableParagraph"><span>Low/Sparse Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>140</span></p> </td> <td> <p class="TableParagraph"><span>Lichens and mosses</span></p> </td> <td> <p class="TableParagraph"><span>6</span></p> </td> <td> <p class="TableParagraph"><span>Low/Sparse Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>150</span></p> </td> <td> <p class="TableParagraph"><span>Sparse vegetation (tree, shrub, herbaceous cover) (&lt;15%)</span></p> </td> <td> <p class="TableParagraph"><span>6</span></p> </td> <td> <p class="TableParagraph"><span>Low/Sparse Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>151</span></p> </td> <td> <p class="TableParagraph"><span>Sparse tree (&lt;15%)</span></p> </td> <td> <p class="TableParagraph"><span>6</span></p> </td> <td> <p class="TableParagraph"><span>Low/Sparse Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>152</span></p> </td> <td> <p class="TableParagraph"><span>Sparse shrub (&lt;15%)</span></p> </td> <td> <p class="TableParagraph"><span>6</span></p> </td> <td> <p class="TableParagraph"><span>Low/Sparse Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>153</span></p> </td> <td> <p class="TableParagraph"><span>Sparse herbaceous cover (&lt;15%)</span></p> </td> <td> <p class="TableParagraph"><span>6</span></p> </td> <td> <p class="TableParagraph"><span>Low/Sparse Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>160</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, flooded, fresh or brakish water</span></p> </td> <td> <p class="TableParagraph"><span>7</span></p> </td> <td> <p class="TableParagraph"><span>Flooded Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>170</span></p> </td> <td> <p class="TableParagraph"><span>Tree cover, flooded, saline water</span></p> </td> <td> <p class="TableParagraph"><span>7</span></p> </td> <td> <p class="TableParagraph"><span>Flooded Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>180</span></p> </td> <td> <p class="TableParagraph"><span>Shrub or herbaceous cover, flooded, fresh/saline/brakish water</span></p> </td> <td> <p class="TableParagraph"><span>7</span></p> </td> <td> <p class="TableParagraph"><span>Flooded Vegetation</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>190</span></p> </td> <td> <p class="TableParagraph"><span>Urban areas</span></p> </td> <td> <p class="TableParagraph"><span>8</span></p> </td> <td> <p class="TableParagraph"><span>Other</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>200</span></p> </td> <td> <p class="TableParagraph"><span>Bare areas</span></p> </td> <td> <p class="TableParagraph"><span>8</span></p> </td> <td> <p class="TableParagraph"><span>Other</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>201</span></p> </td> <td> <p class="TableParagraph"><span>Consolidated bare areas</span></p> </td> <td> <p class="TableParagraph"><span>8</span></p> </td> <td> <p class="TableParagraph"><span>Other</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>202</span></p> </td> <td> <p class="TableParagraph"><span>Unconsolidated bare areas</span></p> </td> <td> <p class="TableParagraph"><span>8</span></p> </td> <td> <p class="TableParagraph"><span>Other</span></p> </td> </tr> <tr> <td> <p class="TableParagraph"><span>210</span></p> </td> <td> <p class="TableParagraph"><span>Water bodies</span></p> </td> <td> <p class="TableParagraph"><span>8</span></p> </td> <td> <p class="TableParagraph"><span>Other</span></p> </td> </tr> </tbody> </table>

opencc-zeroAug 2022View details →
zenodo36/100

MODIS daily snow data (STC-MODSCAG/STC-MODDRFS and SPIReS) over the Western US from 2001-2019

<p>This&nbsp;dataset&nbsp;include two MODIS remote sensing snow data used in the study of &quot;<strong>Evaluation of snow processes over the Western United States in E3SM land model</strong>&quot;. The first one is&nbsp;the spatially and temporally complete (STC) Snow-Covered Area and Grain Size (MODSCAG) and MODIS Dust and Radiative Forcing in Snow (MODDRFS) product&nbsp;(STC-MODSCAG/STC-MODDRFS). The second one is the Snow Property Inversion from Remote Sensing (SPIReS) product. They have daily and 0.125 degree resolution and cover the period from 2001-2019.</p> <p>&nbsp;</p>

opencc-by-4.0Oct 2022View details →
dryad36/100

eLUE-GPP (MODIS): A global gross primary productivity product based on ecosystem light-use-efficiency model and MODIS EVI

<p>Gross Primary Productivity (GPP) represents the cumulative amount of carbon dioxide (CO<sub>2</sub>) assimilated by green plants through photosynthesis at specific time intervals and spatial scales. It is the main component of the carbon exchange between the terrestrial biosphere and the atmosphere, and has a major influence on global climate and terrestrial ecosystem functioning. Over the last two decades, the continuous and reliable collection of global land surface variables by EOS-MODIS, and the parallel development of the eddy-covariance flux tower network (FLUXNET) have enabled the integration of MODIS observations with tower measurements for the calibration and validation of remote sensing models to obtain global GPP estimates. Despite the significant progress and success to date, current remote sensing GPP models based on the light use efficiency (LUE) concept share several limitations, including the difficulty in accurately predicting LUE variability and the associated use of land cover maps and look-up tables for biome specific maximum LUE, further down-regulated by coarse resolution interpolated meteorological data, which introduce significant uncertainties in the predicted GPP. To address the above limitations, here we applied a simple yet ecologically sound remote sensing GPP model based on the ecosystem light use efficiency (eLUE) concept, using the more than two decades of global MODIS Enhanced Vegetation Index (EVI) product and the publicly available FLUXDATA2015 dataset, to generate a global 5 km, 16-d GPP product (eLUE-GPP) from February 2000 to March 2024. Cross-validation with 202 flux tower sites (1494 site/year) showed favorable accuracy of eLUE-GPP (hereafter GPP<sub>eLUE</sub>) (<em>R</em><sup>2</sup> = 0.71, RMSE = 2.11 g C m<sup>-2</sup> d<sup>-1</sup>). The uncertainty associated with GPP<sub>eLUE</sub> is comparatively lower than that of the other global GPP datasets (MOD17, FluxSat, VPM, among others). We have also calculated the uncertainty analytically for each GPP estimate based on the law of error propagation, which allows quantification of the error budget in applications such as Earth system model benchmarking and atmospheric inversion. Our estimate of global total annual GPP, averaged over the period 2001-2023, was 138.46±13.92 Pg C yr<sup>-1</sup>. Furthermore, we found a significant increasing trend in global total annual GPP at a rate of 0.28±0.05 Pg C yr<sup>-1</sup> (<em>p</em> &lt; 0.001) from 2001 to 2023, particularly in eastern Asia, northern India, Europe, eastern North America, and central South America. We expect that the eLUE-GPP product will enable a more accurate diagnostic analysis of the global carbon budget and thus contribute to climate change research.</p>

opencc-zeroJun 2024View details →
zenodo36/100

Ice Floe Segmentation of MODIS imagery

<p>In the segmentation output folder you will find:</p> <ul> <li>for each day of analysis: <ul> <li>YYYY-MM-DD-JD_terra_final.tif: the final georeferenced masked floes</li> <li>YYYY-MM-DD-JD_terra.csv: the properties tables for the floes. see https://scikit-image.org/docs/stable/api/skimage.measure.html#skimage.measure.regionprops for a full description of each parameter. The columns are: <ul> <li>label: corresponding number in the .tif file</li> <li>area (in number of pixels)</li> <li>centroid-0: centroid of the floe (row)</li> <li>centroid-1: centroid of the floe (column)</li> <li>axis_major_length</li> <li>axis_minor length</li> <li>orientation: angle between 0th axis (rows) and major axis</li> <li>perimeter: in pixel units</li> <li>intensity mean: average red channel value of floe</li> </ul> </li> </ul> </li> <li>for each year: mask_values_YYYY.txt : text files with columns: <ul> <li>doy: day of year</li> <li>ice area (pixels)</li> <li>total area for analysis (not cloud or land mask)</li> <li>sea ice concentration</li> </ul> </li> <li>reproj_land.tif: the land mask</li> </ul> <ul> <li>df_all_withloc.csv: includes all floe properties from all years- same columns as individual days plus: <ul> <li>year</li> <li>doy: julian day of year</li> <li>perim_km (perimeter in km)</li> <li>area_km (area in km^2)</li> <li>circ: C = 4*pi *area / (perim^2)</li> <li>lon_ps: polar stereographic x values epsg:3413</li> <li>lat_ps: polar stereographic y values epsg:3413</li> <li>lon: epsg:4326</li> <li>lat: epsg:4326</li> </ul> </li> </ul> <p>outisde of the segmnetation output folder:</p> <p>df_stats_all2.csv: a combination of all the mask value files with additional columns:</p> <ul> <li>floe area: total area of floes within the image</li> <li>floe count: total number of floes in the image</li> </ul> <p>&nbsp;</p>

opencc-by-4.0Jun 2024View details →
zenodo36/100

Global daily Aerosol Optical Depth measurements from Moderate Resolution Imaging Spectroradiometer (MODIS) on NASA's Aqua and Terra satellites

<p>This repository contains input MODIS AOD data prepared for &ldquo;Subways and Urban Air Polution&rdquo; by Gendron-Carrier, Gonzalez-Navarro, Polloni and Turner (American Economic Journal: Applied Economics, <a href="https://doi.org/10.1257/app.20180168">https://doi.org/10.1257/app.20180168</a>). The main replication archive is available at <a href="https://doi.org/10.3886/E126401V1">https://doi.org/10.3886/E126401V1</a> .</p> <p>Description of input MODIS AOD data</p> <p>The Moderate Resolution Imaging Spectroradiometers aboard the Terra and Aqua earth-observing satellites provide daily measures of the aerosol optical depth of the atmosphere at a 3km spatial resolution everywhere in the world. Data is available in &lsquo;granules&rsquo; which describe five minutes of satellite time. These granules are available, more or less continuously, from February 24, 2000 for the Terra satellite and from July 4, 2002 for Aqua. During September of 2018, we downloaded all available granules for Terra and Aqua until August 31, 2018 and subsequently consolidated them into daily rasters describing global AOD. In August 2020, we processed additional Terra data. This archive therefore contains daily rasters for Aqua (from 2002-07-04 to 2018-08-31) and Terra (from 2000-02-24 to 2020-07-31). We note that February 2005 data are missing for the Aqua satellite.</p> <p>&nbsp;</p> <p>We use source products MOD04_3K (<a href="https://doi.org/10.5067/MODIS/MOD04_L2.006">https://doi.org/10.5067/MODIS/MOD04_L2.006</a>) and MYD04_3K (<a href="https://doi.org/10.5067/MODIS/MYD04_L2.006">https://doi.org/10.5067/MODIS/MYD04_L2.006</a>). The product files are stored in Hierarchical Data Format (HDF) and we use the &quot;Optical Depth Land And Ocean&quot; layer, which is stored as a Scientific Data Set (SDS) within the HDF file, as our measure of aerosol optical depth. The &quot;Optical Depth Land And Ocean&quot; dataset contains only the AOD retrievals of high quality. We convert all HDF formatted granules to GIS compatible formats using the HDF-EOS To GeoTIFF Conversion Tool (HEG) provided by NASA&rsquo;s Earth Observing System Program. We consolidate GeoTIFF granules into a global raster for each day using ArcGIS. First, we keep only AOD values that do contain information. The missing value is -9999 in AOD retrievals. Second, we create a raster catalog with all the granules for a given day and calculate the average AOD value using the Raster Catalog to Raster Dataset tool. The code used to accomplish this is included for reference purposes in &ldquo;dofiles/old_work&rdquo; of the main replication archive at <a href="https://doi.org/10.3886/E126401V1">https://doi.org/10.3886/E126401V1</a>.</p>

opencc-by-4.0Dec 2020View details →
zenodo36/100

Annual maps of swidden agriculture landscape derived from MODIS vegetation index in northern Laos during 2001-2020

<p>This document (Word) is a brief introduction about the resultant maps of swidden agricultural landscape in northern Laos during 2001-2020 derived from the MODIS13Q1 Normalized Difference Vegetation Index (NDVI) time-series products using a threshold method. For more information about the dataset, one can refer to the paper entitled &ldquo;Swidden agriculture landscape mapping using MODIS vegetation index time series and its spatio-temporal dynamics in northern Laos&rdquo; published in Remote Sensing. The format of this dataset (swidden agriculture landscape) is raster (.tif) with an attribute value of 1. It has a spatial resolution of 250m&times;250m and covers eleven provinces (including Bokeo, Borikhamxay, Huaphanh, Luangnamtha, Luangprabang, Oudomxay, Phongsaly, Vientiane, Xayaboury, Xaysomboon and Xieng-khuang) and one prefecture (Vientiane, Figure 1). The geographic projection is WGS_1984_UTM_Zone_48N.</p>

opencc-by-4.0Dec 2022View details →
zenodo36/100

Coccolithophore blooms days detected by MODIS Level-2 data in Algiers bay between 2003 and 2018

<p>The figures illustrated in this document reflect the days where the coccolithophore blooms were detected for episodes shown in Figure 8 in Harid et al., (2023). The methodology used to produce these figures is described in Harid, (2022); Harid et al., (2023).</p> <p>&nbsp;</p> <p>References:</p> <p>Harid, R. (2022). <em>&Eacute;tude par t&eacute;l&eacute;d&eacute;tection et mesures in-situ des efflorescences algales et de la mati&egrave;re en suspension dans le Bassin Alg&eacute;rien</em> [PhD. thesis]. ENSSMAL, Algiers.</p> <p>Harid, R., Demarcq, H., Amanouche, S., Ait-Kaci, M., Bachari, N.-E.-I., &amp; Houma, F. (2023). Detection of Coccolithophore Bloom Episodes in Algiers Bay Using Satellite and In Situ Analysis. In S. Niculescu (&Eacute;d.), <em>European Spatial Data for Coastal and Marine Remote Sensing</em> (p. 1‑15). Springer International Publishing. <a href="https://doi.org/10.1007/978-3-031-16213-8_1">https://doi.org/10.1007/978-3-031-16213-8_1</a></p> <p>&nbsp;</p>

opencc-by-4.0Jun 2022View details →
zenodo36/100

Snow cover from spectral mixture analysis algorithm SCAG: OLI and MODIS

<p>This data is snow cover fraction&nbsp;from the Snow Covered Area and Grain Size (SCAG) model for Landsat OLI and Terra MODIS. Terra MODIS data are gap filled to better represent on the ground snow. The data was used in the a publication for The Cyrosphere titled Landsat, MODIS, and VIIRS snow cover mapping algorithm performance as validated by airborne lidar datasets,&nbsp;doi.org/10.5194/tc-2022-159. Geotiffs and PNG files for Landsat 8 are self describing. The .mat files for Terra MODIS contain three variables:</p> <p>snow_fraction: the gap filled snow fraction stored as uint8 with 255 as the NoData value and valid values between and including 0 to 100.</p> <p>mstruct: projection structure describing the standard MODIS tile projection structure. The data represent data from tile h08v05 and h09v05</p> <p>RefMatrix: affine spatial referencing matrix for the snow_fraction grid with the projection described by mstruct</p>

opencc-by-4.0Jan 2023View details →
zenodo36/100

2021_2022_MODIS_WaterBodies_Daily_Dekadal_Monthly_Annual

<h4>Overview:</h4> <p>This is a set of images downloaded from NASA for water bodies and then windowed for E4warning study area.&nbsp;</p> <h4>&nbsp;</h4>

opencc-by-4.0May 2024View details →

ScienceDex guides

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These curated guides explain access requirements, typical timelines, costs, and reuse considerations for widely used research datasets.

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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