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Satellite Imagery

Satellite Imagery refers to the capture and analysis of visual data from Earth-orbiting satellites.
This powerful technology allows researchers to monitor and study a wide range of environmental and geographic phenomena, from deforestation and urbanization to natural disasters and climate change.
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Most cited protocols related to «Satellite Imagery»

The methods used here to model population distribution in Africa are adapted from previous work undertaken for East Africa [15] (link)–[17] (link). The methods were modified for ease of replication and to facilitate the incorporation of new data. Full details on population distribution modelling methods are presented in Text S1. Tables summarizing country-level input data are available on the AfriPop website: www.afripop.org.
Recent work showed that GlobCover was the global land cover dataset that, combined with detailed settlement extents, produced the most accurate population distribution data in an African context [17] (link). The GlobCover dataset was modified to accommodate the more detailed settlement extents obtained from satellite imagery and geolocated points. The GlobCover dataset was first resampled to 100 m spatial resolution, and the urban class – which typically overestimates settlement extent size [15] (link), [17] (link) – was removed and the surrounding classes expanded equally to fill the remaining space. The more detailed settlement extents were then overlaid onto the ‘urban class deprived’ land cover map and land covers beneath were replaced to produce a refined land cover map focussed on detailed and precise mapping of human settlements.
Human population census data, official population size estimates and corresponding administrative unit boundaries at the highest level available from the most recent available censuses were acquired for each African country. High resolution census data were available for three countries in Africa: Ghana, Swaziland and Kenya. Kenya data were also available at enumeration area level (finer than level 5) for 58 of the 69 Kenyan districts. Also obtained was a population density map of Namibia at 1 km spatial resolution (for details on the Namibia density map, see description on www.afripop.org). A table summarizing the spatial resolution, year and source of all data used is available on www.afripop.org.
The modelling method distinguishes urban and rural populations in the redistribution of populations. Major settlements have population numbers already derived and validated and this makes up 38% of the total African population. The remaining 62% rural population was redistributed using land cover-based weightings. The refined land cover data and fine resolution population data from Ghana, Kenya, Namibia and Swaziland were used to define per land cover class population densities (i.e. the average number of people per 100×100 m pixel), following approaches previously outlined [15] (link), [17] (link). These land cover specific population densities were then used as weights to redistribute the rural populations within administrative units in the remaining African countries. The population sizes at the national level for each dataset were projected forward to 2010 with rural and urban growth rates estimated by the UN Population Division [18] . The GRUMP urban extents (available online at: http://sedac.ciesin.columbia.edu/gpw) were used to distinguish between urban and rural areas.
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Publication 2012
Body Weight DNA Replication Homo sapiens Negroid Races Rural Population Satellite Imagery
To understand how the lives of Mosul residents have changed in the year following the liberation from ISIS control, we conducted this household survey in September 2018. We started with the same 40 clusters identified for the 2016/7 Mosul household survey [15 ]. For that survey, the residential administrative units or neighborhoods of Mosul were listed. These residential administrative units would commonly contain around 400 households. From this listing, 40 neighborhoods were selected as clusters, 15 in west Mosul and 25 in east Mosul, a ratio approximating the pre-ISIS population distribution of Mosul. In each cluster, a random point was selected using satellite imagery. The survey began with the household nearest to the random start point and moved to the nearest subsequent households until 30 households had been interviewed. A household was defined as a group of people living together, eating from a common kitchen and living in a structure with a separate entrance from the street. The sampling process is described more fully elsewhere [3 ]. For the one-year follow up survey reported here, 30 households were selected from each of 12 clusters randomly chosen from the original 25 in east Mosul, and from eight clusters of the previous 15 west Mosul clusters. A total of 600 households from 20 clusters were interviewed in September 2018. No households included in the 2016/17 survey were sampled again in this 2018 follow-on survey. Data from completed forms were computer entered in SPSS in Baghdad and preliminary analysis conducted there. Further analysis using Stata1 was conducted in Baltimore.
The questionnaire was adapted from the 2016/17 survey. Interviewers began with a household listing of persons in the household on or after July 2017. Demographic and educational characteristics were collected including births, deaths, injuries and marriages. Household and economic characteristics were recorded, as well as employment and economic indicators.
The interview team was composed of four persons with doctoral degrees in community medicine and who had extensive experience in community surveys. All were originally from Mosul. Some interviewers had participated in the 2016/17 survey. Two days of training was provided.
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Publication 2020
Households Injuries Interviewers Physicians Satellite Imagery
Population data for Burundi, Kenya and Rwanda were adjusted forward [10] (link) to estimated 2002 levels using inter-censal growth rates to match the most recent census data used and the majority of the satellite imagery. Three approaches to the creation of gridded population distribution maps were tested. Firstly (EApop1), the census data was simply areal-weighted [10] (link) to a 100 m spatial resolution grid. Secondly (EApop2), the satellite derived settlement map for each country was degraded to the same 100 m grid, and census counts within an administrative unit were then allocated to the grid squares classified as settlement. Administrative units not containing any grid squares that were classified as settlements had their population counts simply areal weighted. Finally (EApop3), the satellite imagery derived settlement maps were degraded to 100 m spatial resolution and ‘burned’ into the Africover land cover layers to create a refined land cover map for the region. Where settlement extent was mapped as smaller in the settlement map than the ‘urban area’ or ‘rural settlement’ classes in Africover, the surrounding land covers were grown to infill the gaps. This refined land cover layer and Kenyan enumeration area census data were then used to define per land cover class population densities (Table S1), were then used as weights to distribute the census data across the entire region to create a population map.
The accuracies of the various population mapping procedures were tested principally using the enumeration area level census data for 50 Kenyan districts (figure 2). Additionally, to provide a finer resolution measure of settlement population mapping accuracy, the Africover settlement extents with assigned populations were used. For each 100 m gridded population distribution map produced, the population numbers falling within each enumeration area and settlement polygon were extracted and compared against the actual population figures, with overall and district-specific root mean square errors (RMSEs) calculated. To explore the effectiveness of the population mapping procedures in the absence of high resolution census data, for Kenya the map production process was repeated using census data at administrative levels 4, 3, 2, 1 and 0 (national). Finally, the maps of Kenya from existing gridded population products (APD, GRUMP, GPW3 and Landscan 2005) were adjusted to 2002 [10] (link), areal weighted to a 100 m grid and compared to the enumeration area census data to obtain estimates of their accuracy relative to the approaches outlined in this paper.
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Publication 2007
Microtubule-Associated Proteins Plant Roots Satellite Imagery
Data for this study are drawn from the SALURBAL project (SALud URBana en America Latina- Urban Health in Latin America), which includes all cities of 100 000 or more inhabitants in 2010 in 11 countries for a total of 371 cities. Each city was defined geographically by administrative units (ie, municipios, comunas, partidos, delegaciones, cantones or corregimientos) that encompassed the urban extent of the city in 2010 using satellite imagery.16 (link) For this study, we included cities for which vital statistics registries were available from 2014 to 2016 and presented good quality of death registry based on a separate analysis of adult mortality.17 (link) We assumed that cities with good levels of registration for adult deaths (coverage of 90% or above) also have good coverage of deaths among infants. We included 286 cities in Argentina, Brazil, Chile, Colombia, Costa Rica, Mexico, Peru and Panama. Eleven cities (five cities in Nicaragua, three cities in Guatemala and El Salvador, respectively) were excluded due to lack of vital registration for the years of study. A total of 74 cities (9 cities in Brazil, 19 in Colombia, 31 in Mexico and 15 in Peru) were excluded because the estimated coverage of adult mortality was considered of low quality. Mean level of mortality coverage in all excluded cities was below 85% and excluded cities had poorer living conditions and lower provision of water connected to public network compared to cities included in this study (online supplemental material).
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Publication 2020
Adult Infant Latinas Peru 15 Satellite Imagery
Fine-scale, satellite imagery-derived land cover datasets were used to reallocate contemporary census-based spatial population count data. Land cover classes were based principally on the MDA GeoCover Land Cover Thematic Mapper (TM) database, a product that provides a consistent global mapping of 13 land cover classes derived from circa 2005, 30 meter spatial resolution Landsat TM spectral reflectance data [28] . The GeoCover imagery classes were reformatted to be consistent with the GlobCover designations used for AfriPop [20] (link), reclassifying and resampling the data to 8.33×10−4 degrees spatial resolution (approximately 100 meters at the equator). For areas that were classified as cloud, shadow, or “No Data” we filled the data using the nearest neighbour algorithm to create a complete, void-filled land cover dataset for each country.
Additional country-specific datasets were used where available to refine the mapping of settlements and land cover. For Cambodia, land cover was refined using detailed water bodies and built area extent datasets from the Ministry of Land Management, Urban Planning, and Construction. For the Philippines and Myanmar, land cover was refined using detailed built area datasets from the Pacific Disaster Center, Global Hazards Information Network [29] . Building and residential data classes from OpenStreetMap (OSM) (http://download-int.geofabrik.de/osm/asia/) [30] , [31] , an open source product that provides free world-wide geographic datasets, were used to refine urban and rural settlement extents for all countries where it was available. Lastly, the GeoCover data does not differentiate large high density urban areas from smaller rural settlements so, for all countries, we applied a conditional statement that used the urban designations set by the GRUMP urban extents dataset to identify which built areas were ‘urban’ while all other built areas were classified as rural [13] . The inclusion of these additional steps to refine the original GeoCover land cover dataset provide a final product with the most updated ancillary information available on settlement and built landscape features included in the land cover input layer for modelling human population distribution at regional to continental scales. The final land cover datasets were comprised of nine land cover types. Analyses were conducted principally in ArcGIS 10.0 [32] and ERDAS Imagine 2011 [33] .
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Publication 2013
Disasters Homo sapiens Imagery, Guided Satellite Imagery Urination Water, Body

Most recents protocols related to «Satellite Imagery»

Defining urban agglomerations is challenging and often depends on considerations and parameters (18 (link)–20 (no link found, link), 50 ). Africapolis applies the same definition for an urban agglomeration at a continental level (i.e., an agglomeration of at least 10,000 inhabitants and buildings less than 200 m apart), enabling it to analyze and compare cities between different countries (31 ). Buildings’ locations were extracted from the recently launched Google Open Buildings dataset, https://sites.research.google/open-buildings/. The buildings’ footprints were obtained using a deep learning model with high-resolution satellite imagery (50 cm pixel size) (27 ). We extract the buildings’ footprints located within Africapolis polygons and keep the attributes of the building’s center location (latitude and longitude), the confidence score, and the building footprint area. We assign each building the unique identifier of the Africapolis urban agglomeration to which it belongs. This way, we obtained the location and attributes of the buildings’ footprint of 6,849 African urban agglomerations (Fig. 4). We computed street network metrics (29 , 51 ) and terrain metrics (30 ), such as the difference in elevation between the highest and lowest point, the average slope, and the average height within each Africapolis urban agglomeration polygon (SI Appendix, Appendix A).
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Publication 2023
M-200 Negroid Races Satellite Imagery
We followed the suggestion of Arnold et al to use baseline (preintervention) data at the community level to match intervention to control communities when randomisation is not possible.23 (link) To characterise sub-neighbourhoods for further matching and restriction, we performed a population-based community survey in November–December 2020 of approximately 1700 households; this provided approximately a 5% proportional sample of our potential study sub-neighbourhoods. We used a random grid sampling approach to estimate household density, using Google Earth satellite imagery, where a grid was placed over an area, and a random selection of squares were selected and counted independently in duplicate, and the number of houses per unit was extrapolated across unsampled squares. The survey contained modules regarding household demographics, water access and practices, sanitation access and practices, household assets and wealth indicators, as well as questions related to COVID-19. A socioeconomic status (SES) score was constructed using the ‘simple poverty scorecard’78 developed specifically for Mozambique, and scores were aggregated at the sub-neighbourhood level, and categorised into tertiles.
We matched intervention sub-neighbourhoods to control sub-neighbourhoods, using coarsened exact matching,79 80 (link) with intervention sub-neighbourhoods being matched to control sub-neighbourhoods within the same tertile of both SES and population density. Four neighbourhoods (encompassing nine sub-neighbourhoods) were found to be outliers in terms of their sub-neighbourhood-level SES or sanitation, and were excluded from the study sampling frame. Ultimately, we designated 36 intervention sub-neighbourhoods, with an estimated 16 800 households, and 26 control sub-neighbourhoods, with an estimated 9500 households.
Publication 2023
COVID 19 Households Reading Frames Satellite Imagery
Our study is a natural experiment, where the investigators had no control over the selection or timing of the intervention implementation. The study flow diagram is shown in figure 4. We worked with FIPAG to determine which neighbourhoods in Beira were to receive water distribution system upgrades prior to initiation of enrolment (2020) and before the end of the study (2023). FIPAG provided maps and timelines for construction works related to the upgrades, and the specific areas participating in the water loss reduction project. We also worked with FIPAG and through satellite imagery to identify similarly dense low-income areas in Beira that were not slated to receive water network upgrades. A total of 17 potential neighbourhoods were considered for inclusion in the study, and neighbourhoods were divided into 80 sub-neighbourhoods, delineated along natural boundaries such as roads or waterways. ‘Intervention’ sub-neighbourhoods include areas with the upgraded water distribution system. ‘Control’ sub-neighbourhoods include areas not receiving these improvements during the time period of the study. Within both intervention and control sub-neighbourhoods, some households have a connection to the water system and others do not. We excluded nine control sub-neighbourhoods that were in close proximity to intervention sub-neighbourhoods or that were scheduled to receive the interventions within the timetable of our project; some control sub-neighbourhoods are slated to receive the intervention after completion of our study.
Publication 2023
Households Microtubule-Associated Proteins Satellite Imagery TimeLine

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Publication 2023
Droughts Plant Roots Satellite Imagery
Nièna is a rural commune in Mali, located in the Sikasso Circle along a national road (Highway RN7) connecting Bamako, Sikasso, and its neighboring country of Côte d’Ivoire24 . The commune has an area of 1040 square kilometers, includes 45 villages, and a population of 51,086 (population density = 51,086/1040 = 49.1 people per square kilometer). This part of Mali is known for its subsistence agriculture in corn and rice25 . Nièna is illustrated in terms of its proximity to Bamako in Fig. 1.

Geographical location of the study site in Niéna, Mali. Nièna is situated west of the Sikasso Region and southeast of the capital city of Bamako. The geographic coordinates for the locations shown are Bamako (12.6392° N, 8.0029° W), Sikasso (11.3224° N, 5.6984° W), and Nièna (11.4277° N, 6.3492° W). The map was generated using the ArcGIS application basemaps (Professonal version, ESRI, Redlands, CA). Source and service layer credits for satellite imagery: Esri, DigitalGlobe, GeoEye, i-cubed, USDA FSA, USGS, AEX, Getmapping, Aerogrid, IGN, IGP, swisstopo, and the GIS User Community.

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Publication 2023
Satellite Imagery Zea mays

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More about "Satellite Imagery"

Satellite Imaging, Remote Sensing, Earth Observation, Geospatial Analysis, Aerial Imagery, Geospatial Information Systems (GIS), Landsat, Sentinel, MODIS, GOES, IKONOS, QuickBird, WorldView, GeoEye, DigitalGlobe, Maxar, Planet Labs, NOAA, NASA, ESA, JAXA, Photogrammetry, Image Processing, Image Analysis, Cartography, Geovisualization, Climate Change Monitoring, Land Use/Land Cover Change, Deforestation, Urbanization, Natural Disaster Response, Precision Agriculture, Environmental Monitoring, Infrastructure Mapping, Illustrator CS3, SteREO Discovery V20, Handheld meter, eTrex 10, EOS 5D Mark III, SPSS v16.0, PhotoScan, Metashape Professional, EndNote, Developer Software.
Typo: Satelite Imagery.