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Search Results (3,142)

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18 pages, 9898 KiB  
Article
Land Cover Mapping in East China for Enhancing High-Resolution Weather Simulation Models
by Bingxin Ma, Yang Shao, Hequn Yang, Yiwen Lu, Yanqing Gao, Xinyao Wang, Ying Xie and Xiaofeng Wang
Remote Sens. 2024, 16(20), 3759; https://doi.org/10.3390/rs16203759 - 10 Oct 2024
Abstract
This study was designed to develop a 30 m resolution land cover dataset to improve the performance of regional weather forecasting models in East China. A 10-class land cover mapping scheme was established, reflecting East China’s diverse landscape characteristics and incorporating a new [...] Read more.
This study was designed to develop a 30 m resolution land cover dataset to improve the performance of regional weather forecasting models in East China. A 10-class land cover mapping scheme was established, reflecting East China’s diverse landscape characteristics and incorporating a new category for plastic greenhouses (totaling 8687.9 km2 with 6340.5 km2 in Shanghai specifically). Plastic greenhouses are key to understanding surface heterogeneity in agricultural regions, as they can significantly impact local climate conditions, such as heat flux and evapotranspiration, yet they are often not represented in conventional land cover classifications. This is mainly due to the lack of high-resolution datasets capable of detecting these small yet impactful features. For the six-province study area, we selected and processed Landsat 8 imagery from 2015–2018, filtering for cloud cover. Complementary datasets, such as digital elevation models (DEM) and nighttime lighting data, were integrated to enrich the inputs for the Random Forest classification. A comprehensive training dataset was compiled to support Random Forest training and classification accuracy. We developed an automated workflow to manage the data processing, including satellite image selection, preprocessing, classification, and image mosaicking, thereby ensuring the system’s practicality and facilitating future updates. We included three Weather Research and Forecasting (WRF) model experiments in this study to highlight the impact of our land cover maps on daytime and nighttime temperature predictions. The resulting regional land cover dataset achieved an overall accuracy of 83.2% and a Kappa coefficient of 0.81. These accuracy statistics are higher than existing national and global datasets. The model results suggest that the newly developed land cover, combined with a mosaic option in the Unified Noah scheme in WRF, provided the best overall performance for both daytime and nighttime temperature predictions. In addition to supporting the WRF model, our land cover map products, with a planned 3–5-year update schedule, could serve as a valuable data source for ecological assessments in the East China region, informing environmental policy and promoting sustainability. Full article
(This article belongs to the Topic Computer Vision and Image Processing, 2nd Edition)
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<p>Location map of the six provinces in East China as the study area.</p>
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<p>The flowchart of Land cover mapping in East China and experiment for WRF Simulation.</p>
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<p>Landsat scenes utilized in this study, including row and path IDs.</p>
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<p>Some typical data used in Random Forest. (<b>a</b>) 30 m DEM dataset; (<b>b</b>) high-resolution imagery (0.6 m); with specific identification on the imagery (<b>b</b>) as follows: (<b>c</b>) Grasslands and Forest lands (marked by green dot); (<b>d</b>) Water bodies (marked by blue dot); (<b>e</b>) Urban (marked by red dot); (<b>f</b>) Croplands and Plastic greenhouses (marked by orange dot).</p>
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<p>The distribution of the training dataset and the testing dataset.</p>
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<p>30 m Land cover map product for East China.</p>
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<p>Distribution of major land cover types across six study provinces.</p>
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<p>Comparison of landcover types across different datasets.</p>
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<p>Difference between simulated and observed 2 m temperatures. (<b>a</b>–<b>c</b>) at 16:00 on 13 August 2020, and (<b>d</b>–<b>f</b>) at 02:00 on 14 August 2020 (shading, units: °C). (<b>a</b>,<b>d</b>) Original surface data, (<b>b</b>,<b>e</b>) New surface data, (<b>c</b>,<b>f</b>) New surface data + mosaic.</p>
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<p>Time series of (<b>a</b>) the error and (<b>b</b>) the root mean square error of 2 m temperature.</p>
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18 pages, 3599 KiB  
Article
Rapid Appraisal of Wildlife Corridor Viability with Geospatial Modelling and Field Data: Lessons from Makuyuni, Tanzania
by Emmanuel H. Lyimo, Gabriel Mayengo, Kwaslema M. Hariohay, Joseph Holler, Alex Kisingo, David J. Castico, Niwaeli E. Kimambo, Justin Lucas, Emanuel H. Martin and Damian Nguma
Land 2024, 13(10), 1647; https://doi.org/10.3390/land13101647 - 9 Oct 2024
Abstract
Connectivity between protected areas is necessary to prevent habitat fragmentation. Biodiverse countries like Tanzania craft legislation to promote habitat connectivity via the creation of ecological corridors, but their viability for wildlife often remains unknown. We therefore develop a scalable and replicable approach to [...] Read more.
Connectivity between protected areas is necessary to prevent habitat fragmentation. Biodiverse countries like Tanzania craft legislation to promote habitat connectivity via the creation of ecological corridors, but their viability for wildlife often remains unknown. We therefore develop a scalable and replicable approach to assess and monitor multispecies corridor viability using geospatial modeling and field data. We apply and test the approach in the Makuyuni study area: an unprotected ecological corridor connecting Tarangire National Park to Essmingor mountain, Makuyuni Wildlife Park and Mto Wa Mbu Game Controlled Area. We analyzed the viability of Makuyuni as an ecological corridor by creating and validating a geospatial least-cost corridor model with field observations of wildlife and livestock. We created the model from publicly available spatial datasets augmented with manual digitization of pastoral homesteads (bomas). The least-cost corridor model identified two likely pathways for wildlife, confirmed and validated with field observations. Locations with low least-cost values were significantly correlated with more wildlife observations (Spearman’s rho = −0.448, p = 0.002). Our findings suggest that Makuyuni is a viable ecological corridor threatened by development and land use change. Our methodology presents a replicable approach for both monitoring Makuyuni and assessing corridor viability more generally. The incorporation of manually digitized homesteads (bomas) and field-based livestock observations makes corridor assessment more robust by taking into account pastoral land uses that are often missing in land cover maps. Integration of geospatial analysis and field observations is key for the robust identification of corridors for habitat connectivity. Full article
(This article belongs to the Section Landscape Ecology)
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<p>Makuyuni study site, survey transects (lines numbered with transect ID), and nearby conservation areas [<a href="#B43-land-13-01647" class="html-bibr">43</a>].</p>
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<p>Conceptual workflow for least-cost corridor model and validation. <a href="#sec2dot2dot1-land-13-01647" class="html-sec">Section 2.2.1</a>, <a href="#sec2dot2dot2-land-13-01647" class="html-sec">Section 2.2.2</a>, <a href="#sec2dot3dot1-land-13-01647" class="html-sec">Section 2.3.1</a> and <a href="#sec2dot3dot2-land-13-01647" class="html-sec">Section 2.3.2</a>.</p>
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<p>Map of the Makuyuni study area showing inputs for the least-cost corridor model, as listed in <a href="#land-13-01647-t001" class="html-table">Table 1</a>.</p>
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<p>Modeled least-cost corridors that are locations with low cost of movement (blue) relative to the rest of the study area. Overlaid are “observed corridors,” generated by digitizing regions with high wildlife counts in field surveys. The most western “observed corridor” measures 7065 ha, while the most eastern one measures 7552 ha.</p>
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<p>Wildlife density based on total count of individuals of all wildlife species encountered during the field transect survey (kernel diameter = 300 m). Numbered lines indicate survey transects.</p>
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<p>Livestock density based on total count of individual livestock (sheep, goats, cows, donkeys) encountered during the field transect survey (kernel diameter = 300 m). Numbered lines indicate survey transects.</p>
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<p>QGIS graphic model for the least-cost wildlife corridor analysis.</p>
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<p>Sample land cover types across the Tarangire–Manyara ecosystem. Photographs are illustrative of flora and fauna of the ecosystem and do not all originate from the Makuyuni study area. Credit: Salum Mpapa.</p>
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14 pages, 12026 KiB  
Article
Satellite Reveals a Coupling between Forest Displacement and Landscape Fragmentation across the Economic Corridor of the Eurasia Continent
by Ying Wang, Li’nan Dong, Longhao Wang and Jiaxin Jin
Forests 2024, 15(10), 1768; https://doi.org/10.3390/f15101768 - 8 Oct 2024
Abstract
Jointly building the Economic Corridor of the Eurasia Continent (ECEC), which is one of the most important parts of the Silk Road Economic Belt, is a pivotal initiative for fostering regional development. Forests, which serve as a green foundation of economic resilience, underpin [...] Read more.
Jointly building the Economic Corridor of the Eurasia Continent (ECEC), which is one of the most important parts of the Silk Road Economic Belt, is a pivotal initiative for fostering regional development. Forests, which serve as a green foundation of economic resilience, underpin this effort. However, there is an imbalance in ecological status due to differences in natural resources and the social economy along the economic corridor. This imbalance has led to alterations in landscapes, yet the specific changes and their underlying relationships are still much less understood. Here, we quantitatively detected changes in the forest landscape and its ecological efforts over the ECEC via widespread, satellite-based and long-term land cover maps released by the European Space Agency (ESA) Climate Change Initiative (CCI). Specifically, the coupling between changes in forest coverage and landscape patterns, e.g., diversity, was further examined. The results revealed that forest coverage fluctuated and declined over the ECEC from 1992 to 2018, with an overall reduction of approximately 9784.8 km2 (i.e., 0.25%). Conversions between forests and other land cover types were widely observed. The main displacements occurred between forests and grasslands/croplands (approximately 48%/21%). Moreover, the landscape diversity in the study area increased, as measured by the effective diversity index (EDI), during the study period, despite obvious spatial heterogeneity. Notably, this pattern of landscape diversity was strongly associated with forest displacement and local urban development through coupling analysis, consequently indicating increasing fragmentation rather than biological diversity. This study highlights the coupled relationship between quantitative and qualitative changes in landscapes, facilitating our understanding of environmental protection and policy management. Full article
(This article belongs to the Section Forest Inventory, Modeling and Remote Sensing)
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<p>Spatial distribution of forests across the Economic Corridor of the Eurasia Continent and Silk Road Economic Belt. Panel (<b>a</b>) shows the spatial distribution of deciduous and evergreen forests. The lines with the black and blue dots represent the Silk Road Economic Belt. The dark and light green lines on the right indicate the means of coverages of deciduous and evergreen forests, respectively, along the latitudinal and longitudinal gradients. Panel (<b>b</b>) presents a conceptual diagram of the Silk Road and Economic Belt. Three routes are shown: the China–Mongolia–Russia Economic Corridor, the New Eurasian Land Bridge, and the China–Central Asia–West Asia Economic Corridor. The arrows indicate the direction of these corridors.</p>
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<p>Technique flow chart for this study. Panels showing (<b>a</b>) the technique flow chart and (<b>b</b>,<b>c</b>) scientific issues of this study.</p>
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<p>Spatial variability in forests across the Economic Corridor of the Eurasia Continent from 1992 to 2018. The lines with the black and blue dots line represent the Silk Road Economic Belt.</p>
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<p>Time series variabilities in forests across the Economic Corridor of the Eurasia Continent from 1992 to 2018. Panels (<b>a</b>–<b>d</b>) show the forest coverage changes in evergreen needle-leaved forest (ENF), deciduous broad-leaved forest (DBF), evergreen broad-leaved forest (EBF) and deciduous needle-leaved forest (DNF), respectively. Panel (<b>e</b>) shows the interannual variation in the total amount of ENF, DBF, EBF, and DNF.</p>
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<p>Spatial distributions of the effective diversity index (EDI) trends across the Economic Corridor of the Eurasia Continent from 1992 to 2018. The lines with the black and blue dots represent the Silk Road Economic Belt.</p>
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<p>Transitions between forests and other land cover types across the entire study area from 1992 to 2018. Other types of land cover include barren land and cities.</p>
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<p>Spatiotemporal variabilities in the transitions between forests and other land cover types across the Economic Corridor of the Eurasia Continent from 1992 to 2018. Panels (<b>a</b>) and (<b>b</b>) show the spatial patterns of net forest gain and net forest loss, respectively. The lines with the black and blue dots represent the Silk Road Economic Belt.</p>
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<p>Spatial distribution of the coupling between land cover and landscape diversity changes across the Economic Corridor of the Eurasia Continent from 1992 to 2018. (<b>a</b>) The colors indicate the coupled intervals of changes in forest coverage and the effective diversity index (EDI). The purple pixels represent the worst-case pattern, where significant forest loss was accompanied by increased landscape fragmentation, while the green areas represent the best-case pattern, with minimal forest loss and reduced fragmentation. The lines with the black and blue dots represent the Silk Road Economic Belt. (<b>b</b>) The bars indicate the percentages of the coupled patterns.</p>
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22 pages, 11903 KiB  
Article
Remote Sensing Mapping and Analysis of Spatiotemporal Patterns of Land Use and Cover Change in the Helong Region of the Loess Plateau Region (1986–2020)
by Jingyu Li, Yangbo Chen, Yu Gu, Meiying Wang and Yanjun Zhao
Remote Sens. 2024, 16(19), 3738; https://doi.org/10.3390/rs16193738 - 8 Oct 2024
Abstract
Land use and cover change (LUCC) is directly linked to the sustainability of ecosystems and the long-term well-being of human society. The Helong Region in the Loess Plateau has become one of the areas most severely affected by soil and water erosion in [...] Read more.
Land use and cover change (LUCC) is directly linked to the sustainability of ecosystems and the long-term well-being of human society. The Helong Region in the Loess Plateau has become one of the areas most severely affected by soil and water erosion in China due to its unique geographical location and ecological environment. The long-term construction of terraces and orchards is one of the important measures for this region to combat soil erosion. Despite the important role that terraces and orchards play in this region, current studies on their extraction and understanding remain limited. For this reason, this study designed a land use classification system, including terraces and orchards, to reveal the patterns of LUCC and the effectiveness of ecological restoration projects in the area. Based on this system, this study utilized the Random Forest classification algorithm to create an annual land use and cover (LUC) dataset for the Helong Region that covers eight periods from 1986 to 2020, with a spatial resolution of 30 m. The validation results showed that the maps achieved an average overall accuracy of 87.54% and an average Kappa coefficient of 76.94%. This demonstrates the feasibility of the proposed design and land coverage mapping method in the study area. This study found that, from 1986 to 2020, there was a continuous increase in forest and grassland areas, a significant reduction in cropland and bare land areas, and a notable rise in impervious surface areas. We emphasized that the continuous growth of terraces and orchards was an important LUCC trend in the region. This growth was primarily attributed to the conversion of grasslands, croplands, and forests. This transformation not only reduced soil erosion but also enhanced economic efficiency. The products and insights provided in this study help us better understand the complexities of ecological recovery and land management. Full article
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<p>Location of Helong Region.</p>
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<p>Workflow of this study.</p>
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<p>Number of Landsat scenes used in the GEE image synthesis.</p>
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<p>Anomaly screening and repair of Landsat data (<b>a</b>) filling missing data (<b>b</b>) repairing Landsat 7 image gaps.</p>
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<p>Distribution of the training sample polygons at different times and in different categories.</p>
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<p>Validation of the spatial distribution of the sample set.</p>
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<p>Temporal distribution of area changes for various LUC types in the Helong Region (the proportion of change on the right axis is relative to the area change ratio with respect to the base year (1986)).</p>
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<p>Spatial distribution of LUC change rates in the Helong Region. (Through linear regression, we calculated the area ratio change rates for each category within each grid (0.1°) from 1986 to 2020, and the spatial distributions of the area ratio changes that were found to be significant (<span class="html-italic">p</span> &lt; 0.05) are displayed. In the figure, gray grids represent results with insignificant changes or changes below 0.1% per year (−0.1 to 0.1)).</p>
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<p>Spatial and temporal distributions of forests, grasslands, and croplands transformed into terraces and orchards.</p>
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<p>Heat map of the transitions of LUC types in two adjacent periods.</p>
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<p>Comparison of the accuracy of HL-LUC, FROM-GLC, CLC-FCS30, and ESA CCI-LC.</p>
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<p>Comparison of HL-LUC-2015 with the three other datasets.</p>
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17 pages, 2422 KiB  
Article
A “Region-Specific Model Adaptation (RSMA)”-Based Training Data Method for Large-Scale Land Cover Mapping
by Congcong Li, George Xian and Suming Jin
Remote Sens. 2024, 16(19), 3717; https://doi.org/10.3390/rs16193717 - 6 Oct 2024
Abstract
An accurate and historical land cover monitoring dataset for Alaska could provide fundamental information for a range of studies, such as conservation habitats, biogeochemical cycles, and climate systems, in this distinctive region. This research addresses challenges associated with the extraction of training data [...] Read more.
An accurate and historical land cover monitoring dataset for Alaska could provide fundamental information for a range of studies, such as conservation habitats, biogeochemical cycles, and climate systems, in this distinctive region. This research addresses challenges associated with the extraction of training data for timely and accurate land cover classifications in Alaska over longer time periods (e.g., greater than 10 years). Specifically, we designed the “Region-Specific Model Adaptation (RSMA)” method for training data. The method integrates land cover information from the National Land Cover Database (NLCD), LANDFIRE’s Existing Vegetation Type (EVT), and the National Wetlands Inventory (NWI) and machine learning techniques to generate robust training samples based on the Anderson Level II classification legend. The assumption of the method is that spectral signatures vary across regions because of diverse land surface compositions; however, despite these variations, there are consistent, collective land cover characteristics that span the entire region. Building upon this assumption, this research utilized the classification power of deep learning algorithms and the generalization ability of RSMA to construct a model for the RSMA method. Additionally, we interpreted existing vegetation plot information for land cover labels as validation data to reduce inconsistency in the human interpretation. Our validation results indicate that the RSMA method improved the quality of the training data derived solely from the NLCD by approximately 30% for the overall accuracy. The validation assessment also demonstrates that the RSMA method can generate reliable training data on large scales in regions that lack sufficient reliable data. Full article
(This article belongs to the Special Issue Advances of Remote Sensing in Land Cover and Land Use Mapping)
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<p>The framework of the “Region-Specific Model Adaptation (RSMA)”-based training data method. The land cover images are NLCD land cover maps. The different colored lines represent various input features.</p>
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<p>Temporal trends (<b>A</b>) and semi-monthly NIR composition (<b>B</b>) of the NIR reflectance values (2009–2012). The reflectance values were scaled by a factor of 10,000.</p>
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<p>Diagram of the convolution along the time dimension.</p>
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<p>Interpreted validation sample units from plots in the North Slope Land Cover and USFWS. The background images are NLCD land cover maps.</p>
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23 pages, 15900 KiB  
Article
Predicting Fractional Shrub Cover in Heterogeneous Mediterranean Landscapes Using Machine Learning and Sentinel-2 Imagery
by El Khalil Cherif, Ricardo Lucas, Taha Ait Tchakoucht, Ivo Gama, Inês Ribeiro, Tiago Domingos and Vânia Proença
Forests 2024, 15(10), 1739; https://doi.org/10.3390/f15101739 - 1 Oct 2024
Abstract
Wildfires pose a growing threat to Mediterranean ecosystems. This study employs advanced classification techniques for shrub fractional cover mapping from satellite imagery in a fire-prone landscape in Quinta da França (QF), Portugal. The study area is characterized by fine-grained heterogeneous land cover and [...] Read more.
Wildfires pose a growing threat to Mediterranean ecosystems. This study employs advanced classification techniques for shrub fractional cover mapping from satellite imagery in a fire-prone landscape in Quinta da França (QF), Portugal. The study area is characterized by fine-grained heterogeneous land cover and a Mediterranean climate. In this type of landscape, shrub encroachment after land abandonment and wildfires constitutes a threat to ecosystem resilience—in particular, by increasing the susceptibility to more frequent and large fires. High-resolution mapping of shrub cover is, therefore, an important contribution to landscape management for fire prevention. Here, a 20 cm resolution land cover map was used to label 10 m Sentinel-2 pixels according to their shrub cover percentage (three categories: 0%, >0%–50%, and >50%) for training and testing. Three distinct algorithms, namely Support Vector Machine (SVM), Artificial Neural Networks (ANNs), and Random Forest (RF), were tested for this purpose. RF excelled, achieving the highest precision (82%–88%), recall (77%–92%), and F1 score (83%–88%) across all categories (test and validation sets) compared to SVM and ANN, demonstrating its superior ability to accurately predict shrub fractional cover. Analysis of confusion matrices revealed RF’s superior ability to accurately predict shrub fractional cover (higher true positives) with fewer misclassifications (lower false positives and false negatives). McNemar’s test indicated statistically significant differences (p value < 0.05) between all models, consolidating RF’s dominance. The development of shrub fractional cover maps and derived map products is anticipated to leverage key information to support landscape management, such as for the assessment of fire hazard and the more effective planning of preventive actions. Full article
(This article belongs to the Section Forest Inventory, Modeling and Remote Sensing)
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<p>The study area within Quinta da França farm (white dashed line), Portugal (top left). The solid blue line outlines the study area in detail. A zoomed-in view in the bottom-right corner highlights the land cover within the study area, as captured by drone imagery.</p>
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<p>Methodology employed by this study for shrub cover assessment using Sentinel-2 imagery and a high-resolution land cover map. The process encompasses the following chain of steps: (1) Sentinel-2 images from August 2020 are acquired and aligned with a high-resolution land cover map; (2) Sentinel-2 pixels are labeled according to their shrub cover percentage category using a high-resolution land cover map; (3) labeled Sentinel-2 pixels and their spectral information are used to train three machine learning models (RF, SVM, and ANN); (4) models are validated using an independent dataset. Solid lines depict training and testing steps, and dashed lines represent the validation step.</p>
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<p>Fractional shrub coverage in Quinta da Franca. Full dataset obtained from the intersection of the high-resolution land cover map and the Sentinel-2 pixel grid. This figure shows the spatial distribution of shrub cover across the study area, not the number of samples for each category.</p>
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<p>(<b>a</b>) Actual shrub cover in the testing subset of pixels retrieved from the full dataset (<a href="#forests-15-01739-f003" class="html-fig">Figure 3</a>) to test the machine learning algorithms. (<b>b</b>) Shrub cover predicted by the random forest algorithm for the subset of pixels in the testing dataset.</p>
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<p>(<b>a</b>) Validation dataset showing the subset of pixels retrieved from the full dataset (<a href="#forests-15-01739-f003" class="html-fig">Figure 3</a>) to test the machine learning algorithms. (<b>b</b>) Shrub coverage predicted by the random forest algorithm for the subset of pixels in the validation dataset.</p>
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<p>Confusion Matrices for shrub cover classification on the test set and validation set.</p>
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25 pages, 5094 KiB  
Article
Evaluating Flood Damage to Paddy Rice Fields Using PlanetScope and Sentinel-1 Data in North-Western Nigeria: Towards Potential Climate Adaptation Strategies
by Sa’ad Ibrahim and Heiko Balzter
Remote Sens. 2024, 16(19), 3657; https://doi.org/10.3390/rs16193657 - 30 Sep 2024
Abstract
Floods are significant global disasters, but their impact in developing countries is greater due to the lower shock tolerance, many subsistence farmers, land fragmentation, poor adaptation strategies, and low technical capacity, which worsen food security and livelihoods. Therefore, accurate and timely monitoring of [...] Read more.
Floods are significant global disasters, but their impact in developing countries is greater due to the lower shock tolerance, many subsistence farmers, land fragmentation, poor adaptation strategies, and low technical capacity, which worsen food security and livelihoods. Therefore, accurate and timely monitoring of flooded crop areas is crucial for both disaster impact assessments and adaptation strategies. However, most existing methods for monitoring flooded crops using remote sensing focus solely on estimating the flood damage, neglecting the need for adaptation decisions. To address these issues, we have developed an approach to mapping flooded rice fields using Earth observation and machine learning. This approach integrates high-resolution multispectral satellite images with Sentinel-1 data. We have demonstrated the reliability and applicability of this approach by using a manually labelled dataset related to a devastating flood event in north-western Nigeria. Additionally, we have developed a land suitability model to evaluate potential areas for paddy rice cultivation. Our crop extent and land use/land cover classifications achieved an overall accuracy of between 93% and 95%, while our flood mapping achieved an overall accuracy of 99%. Our findings indicate that the flood event caused damage to almost 60% of the paddy rice fields. Based on the land suitability assessment, our results indicate that more land is suitable for cultivation during natural floods than is currently being used. We propose several recommendations as adaptation measures for stakeholders to improve livelihoods and mitigate flood disasters. This study highlights the importance of integrating multispectral and synthetic aperture radar (SAR) data for flood crop mapping using machine learning. Decision-makers will benefit from the flood crop mapping framework developed in this study in a number of spatial planning applications. Full article
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<p>Study area location showing digital elevation and showing three sites that were used in the subsequent sections as extracts of the LULC/crop and flood extents from pre- and post-flood imagery, respectively, (<b>a</b>) and study area overlay on Nigeria (<b>b</b>).</p>
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<p>(<b>a</b>–<b>f</b>) depict the RGB composites for three sites within the study area, along with their corresponding. RF LULC maps from PlanetScope four bands, SAR and NDWI. (<b>a</b>) PlanetScope RGB for site I, (<b>b</b>) PlanetScope RGB for site II, (<b>c</b>) PlanetScope RGB for site III, (<b>d</b>) RF LULC map for site I, (<b>e</b>) RF LULC map for site II, and (<b>f</b>) RF LULC map for site III.</p>
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<p>Histogram distribution of the flood and non-flood points extracted based on the training data used for the flooded/non-flooded classification using the (<b>a</b>) NDWI (PlanetScope), (<b>b</b>) Sentinel-1 VV backscatter, and (<b>c</b>) Sentinel-1 VH backscatter.</p>
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<p>(<b>a</b>–<b>i</b>) RF flooded and non-flooded layers overlaid by water bodies, affected and unaffected rice fields, from the subsets of the full scenes (zoom in from the three sites shown on the study area map).</p>
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<p>Sentinel-1 VV signals of the paddy rice fields of flooded/non-flooded rice fields and their corresponding rainfall anomalies (2016–2023). (<b>a</b>) Flooded/non-flooded rice fields and rainfall anomalies for the three locations shown on the graph. (<b>b</b>) Flooded/non-flooded rice fields and rainfall anomalies for the three locations shown on the graph.</p>
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<p>Area in hectares and percentages for each LULC/crop extent, flooded/non-flooded area and the damaged PR.</p>
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<p>Potential cultivable area estimated based on the weighted overlay approach for different scenarios: (<b>a</b>) for rainfed (RF) agriculture, (<b>b</b>) for rainfed under natural flood (RFNF) and (<b>c</b>) for Irrigation (IR) paddy rice farming.</p>
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29 pages, 13171 KiB  
Article
Enhancing Coffee Agroforestry Systems Suitability Using Geospatial Analysis and Sentinel Satellite Data in Gedeo Zone, Ethiopia
by Wondifraw Nigussie, Husam Al-Najjar, Wanchang Zhang, Eshetu Yirsaw, Worku Nega, Zhijie Zhang and Bahareh Kalantar
Sensors 2024, 24(19), 6287; https://doi.org/10.3390/s24196287 - 28 Sep 2024
Abstract
The Gedeo zone agroforestry systems are the main source of Ethiopia’s coffee beans. However, land-use and suitability analyses are not well documented due to complex topography, heterogeneous agroforestry, and lack of information. This research aimed to map the coffee coverage and identify land [...] Read more.
The Gedeo zone agroforestry systems are the main source of Ethiopia’s coffee beans. However, land-use and suitability analyses are not well documented due to complex topography, heterogeneous agroforestry, and lack of information. This research aimed to map the coffee coverage and identify land suitability for coffee plantations using remote sensing, Geographic Information Systems (GIS), and the Analytical Hierarchy Process (AHP) in the Gedeo zone, Southern Ethiopia. Remote sensing classifiers often confuse agroforestry and plantations like coffee cover with forest cover because of their similar spectral signatures. Mapping shaded coffee in Gedeo agroforestry using optical or multispectral remote sensing is challenging. To address this, the study identified and mapped coffee coverage from Sentinel-1 data with a decibel (dB) value matched to actual coffee coverage. The actual field data were overlaid on Sentinel-1, which was used to extract the raster value. Pre-processing, classification, standardization, and reclassification of thematic layers were performed to find potential areas for coffee plantation. Hierarchy levels of the main criteria were formed based on climatological, edaphological, physiographic, and socioeconomic factors. These criteria were divided into 14 sub-criteria, reclassified based on their impact on coffee growing, with their relative weights derived using AHP. From the total study area of 1356.2 km2, the mapped coffee coverage is 583 km2. The outcome of the final computed factor weight indicated that average annual temperature and mean annual rainfall are the primary factors, followed by annual mean maximum temperature, elevation, annual mean minimum temperature, soil pH, Land Use/Land Cover (LULC), soil texture, Cation Exchange Capacity (CEC), slope, Soil Organic Matter (SOM), aspect, distance to roads, and distance to water, respectively. The identified coffee plantation potential land suitability reveals unsuitable (413 km2), sub-suitable (596.1 km2), and suitable (347.1 km2) areas. This study provides comprehensive spatial details for Ethiopian cultivators, government officials, and agricultural extension specialists to select optimal coffee farming locations, enhancing food security and economic prosperity. Full article
(This article belongs to the Special Issue Remote Sensing Technology for Agricultural and Land Management)
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<p>Location of the study area.</p>
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<p>Methodological flowchart of the research.</p>
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<p>Pre-processed images (<b>a</b>) sentinel-1 (SAR), and (<b>b</b>) sentinel-2 (MSI).</p>
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<p>Agro-ecological classification, (<b>a</b>) sample field data of coffee coverage, and (<b>b</b>) processed sentinel-1.</p>
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<p>Maps of physiographic thematic layers (<b>a</b>) Elevation, (<b>b</b>) Slope, (<b>c</b>) Aspect, (<b>d</b>) Reclassified elevation, (<b>e</b>) Reclassified slope, (<b>f</b>) Reclassified aspect.</p>
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<p>Maps of edaphological thematic layers. (<b>a</b>) Soil texture, (<b>b</b>) Reclassified soil texture, (<b>c</b>) Soil organic matter, (<b>d</b>) Reclassified soil organic matter, (<b>e</b>) Soil pH, (<b>f</b>) Reclassified soil pH, (<b>g</b>) CEC, (<b>h</b>) Reclassified CEC.</p>
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<p>Maps of climatological thematic layers, (<b>a</b>) Mean annual rainfall, (<b>b</b>) Reclassified mean annual rainfall, (<b>c</b>) Annual mean maximum temperature, (<b>d</b>) Reclassified maximum temperature, (<b>e</b>) Average annual temperature, (<b>f</b>) Reclassified average annual temperature, (<b>g</b>) Annual mean minimum temperature, (<b>h</b>) Reclassified mean minimum temperature.</p>
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<p>Maps of socioeconomic thematic layers, (<b>a</b>) LULC in 2021, (<b>b</b>) Distance to road network, (<b>c</b>) Distance to river network, (<b>d</b>) Reclassified LULC, (<b>e</b>) Reclassified distance to road, (<b>f</b>) Reclassified distance to river.</p>
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<p>Current potential coffee coverage areas in Gedeo zone.</p>
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<p>Identified potential areas for coffee plantation.</p>
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<p>Area coverage of identified potential coffee plantation.</p>
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21 pages, 9403 KiB  
Article
Link Aggregation for Skip Connection–Mamba: Remote Sensing Image Segmentation Network Based on Link Aggregation Mamba
by Qi Zhang, Guohua Geng, Pengbo Zhou, Qinglin Liu, Yong Wang and Kang Li
Remote Sens. 2024, 16(19), 3622; https://doi.org/10.3390/rs16193622 - 28 Sep 2024
Abstract
The semantic segmentation of satellite and UAV remote sensing imagery is pivotal for address exploration, change detection, quantitative analysis and urban planning. Recent advancements have seen an influx of segmentation networks utilizing convolutional neural networks and transformers. However, the intricate geographical features and [...] Read more.
The semantic segmentation of satellite and UAV remote sensing imagery is pivotal for address exploration, change detection, quantitative analysis and urban planning. Recent advancements have seen an influx of segmentation networks utilizing convolutional neural networks and transformers. However, the intricate geographical features and varied land cover boundary interferences in remote sensing imagery still challenge conventional segmentation networks’ spatial representation and long-range dependency capabilities. This paper introduces a novel U-Net-like network for UAV image segmentation. We developed a link aggregation Mamba at the critical skip connection stage of UNetFormer. This approach maps and aggregates multi-scale features from different stages into a unified linear dimension through four Mamba branches containing state-space models (SSMs), ultimately decoupling and fusing these features to restore the contextual relationships in the mask. Moreover, the Mix-Mamba module is incorporated, leveraging a parallel self-attention mechanism with SSMs to merge the advantages of a global receptive field and reduce modeling complexity. This module facilitates nonlinear modeling across different channels and spaces through multipath activation, catering to international and local long-range dependencies. Evaluations on public remote sensing datasets like LovaDA, UAVid and Vaihingen underscore the state-of-the-art performance of our approach. Full article
(This article belongs to the Special Issue Deep Learning for Satellite Image Segmentation)
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<p>Overall architecture of the proposed network. The network consists of three main components: a CNN encoder, an LASC-Mamba skip connection structure and a Mix-Mamba decoder.</p>
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<p>The structure of LASC-Mamba. LASC-Mamba transforms two-dimensional features across four different scales and aggregates the one-dimensional outputs through link aggregation, ultimately restoring feature dimensions and utilizing skip connections at the terminal stage.</p>
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<p>The structure of Mix-Mamba. Comprises a local feature extraction module on the left, a global self-attention mechanism in the middle and a Mamba module on the right.</p>
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<p>Visualization of results on the LoveDA validation set.</p>
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<p>Visualization of results on the UAVid validation set.</p>
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<p>Visualization of results on the Vaihaigen test set.</p>
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<p>Visualization of results on the UAVid validation set.</p>
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<p>Visualization of results on the LoveDA validation set.</p>
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<p>Failure cases on the Vaihingen dataset.</p>
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15 pages, 17891 KiB  
Article
Effects of Land Cover Changes on Shallow Landslide Susceptibility Using SlideforMAP Software (Mt. Nerone, Italy)
by Ilenia Murgia, Alessandro Vitali, Filippo Giadrossich, Enrico Tonelli, Lorena Baglioni, Denis Cohen, Massimiliano Schwarz and Carlo Urbinati
Land 2024, 13(10), 1575; https://doi.org/10.3390/land13101575 - 27 Sep 2024
Abstract
Land cover changes in mountainous areas due to silvo-pastoral abandonment can affect soil stability, especially on steep slopes. In addition, the increase in rainfall intensity in recent decades requires re-assessing landslide susceptibility and vegetation management for soil protection. This study was carried out [...] Read more.
Land cover changes in mountainous areas due to silvo-pastoral abandonment can affect soil stability, especially on steep slopes. In addition, the increase in rainfall intensity in recent decades requires re-assessing landslide susceptibility and vegetation management for soil protection. This study was carried out using the software SlideforMAP in the Mt. Nerone massif (central Italy) to assess (i) the effects of land cover changes on slope stability over the past 70 years (1954–2021) and (ii) the role of actual vegetation cover during intense rainfall events. The study area has undergone a significant change in vegetation cover over the years, with a reduction in mainly pastures (−80%) and croplands (−22%) land cover classes in favor of broadleaf forests (+64%). We simulated twelve scenarios, combining land cover conditions and rainfall intensities, and analyzed the landslide failure probability results. Vegetation cover significantly increased the slope stability, up to three to four times compared to the unvegetated areas (29%, 68%, and 89%, respectively, in the no cover, 1954, and 2021 scenarios). The current land cover provided protection against landslide susceptibility, even during extreme rainfall events, for different return periods. The 30-year return period was a critical condition for a significant stability reduction. In addition, forest species provide different mitigation effects due to their root system features. The results showed that species with deep root systems, such as oaks, provide more effective slope stability than other species, such as pines. This study helps to quantify the mitigation effects of vegetation cover and suggests that physically based probabilistic models can be used at the regional scale to detect the areas prone to failure and the triggering of rainfall-induced shallow landslides. This approach can be important in land planning and management to mitigate risks in mountainous regions. Full article
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<p>Location of the Mt. Nerone study area (yellow boundaries) in the Central Apennines (red dot).</p>
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<p>Workflow diagram. Boxes with dashed edges relate to the preliminary step for determining land cover changes. The flowchart elements are color-coded and shaped differently to highlight various workflow stages. Boxes with solid edges indicate the process of slope stability analysis. Data sources (gray cylinder), source data for stability assessment (light blue boxes), software (yellow box shapes), and outputs (dark blue boxes) for the different scenarios (0 = no vegetation cover; 54 = vegetation cover in 1954; 21 = vegetation cover in 2021; 21* = vegetation cover 2021 with detailed forest categories). The bulleted list to the right lists the analyses and comparisons carried out in this research.</p>
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<p>Land cover in the Mt. Nerone area in 1954 (<b>a</b>) and 2021 (<b>b</b>).</p>
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<p>Failure probabilities estimated using SlideforMAP for the 200-year return period rainfall with (<b>a</b>) no vegetation cover, (<b>b</b>) 1954 land cover, and (<b>c</b>) 2021 land cover. In the legend, <span class="html-italic">Fn</span> represents the failure probability class, where n is the maximum value of each class. In (<b>d</b>), the sum of the relative areas is less than 100% because urban areas (ua) and roads and paths (rt) were not included.</p>
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<p>Surface areas with different failure probability classes and different return periods in the 2021* scenario.</p>
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<p>Area extent (in hectares) of each failure probability class, referring to each forest category (rows) and return period (columns) and comparing no-cover (red bars) and 2021* (blue bars) scenarios. Holm oak (ho), downy oak (do), hop hornbeam–manna ash (hm), beech (be), and turkey oak (to), black pine (bp).</p>
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<p>ROC curves for predictive model performance at various random point distances. The curves show the area under the curve (AUC) for random point minimum distances of 1, 5, 10, 15, and 20 m. The diagonal dotted line is the reference line that defines the ROC curve as a random classification.</p>
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25 pages, 5983 KiB  
Article
Quality Evaluation of Multi-Source Cropland Data in Alpine Agricultural Areas of the Qinghai-Tibet Plateau
by Shenghui Lv, Xingsheng Xia, Qiong Chen and Yaozhong Pan
Remote Sens. 2024, 16(19), 3611; https://doi.org/10.3390/rs16193611 - 27 Sep 2024
Abstract
Accurate cropland distribution data are essential for efficiently planning production layouts, optimizing farmland use, and improving crop planting efficiency and yield. Although reliable cropland data are crucial for supporting modern regional agricultural monitoring and management, cropland data extracted directly from existing global land [...] Read more.
Accurate cropland distribution data are essential for efficiently planning production layouts, optimizing farmland use, and improving crop planting efficiency and yield. Although reliable cropland data are crucial for supporting modern regional agricultural monitoring and management, cropland data extracted directly from existing global land use/cover products present uncertainties in local regions. This study evaluated the area consistency, spatial pattern overlap, and positional accuracy of cropland distribution data from six high-resolution land use/cover products from approximately 2020 in the alpine agricultural regions of the Hehuang Valley and middle basin of the Yarlung Zangbo River (YZR) and its tributaries (Lhasa and Nianchu Rivers) area on the Qinghai-Tibet Plateau. The results indicated that (1) in terms of area consistency analysis, European Space Agency (ESA) WorldCover cropland distribution data exhibited the best performance among the 10 m resolution products, while GlobeLand30 cropland distribution data performed the best among the 30 m resolution products, despite a significant overestimation of the cropland area. (2) In terms of spatial pattern overlap analysis, AI Earth 10-Meter Land Cover Classification Dataset (AIEC) cropland distribution data performed the best among the 10 m resolution products, followed closely by ESA WorldCover, while the China Land Cover Dataset (CLCD) performed the best for the Hehuang Valley and GlobeLand30 performed the best for the YZR area among the 30 m resolution products. (3) In terms of positional accuracy analysis, the ESA WorldCover cropland distribution data performed the best among the 10 m resolution products, while GlobeLand30 data performed the best among the 30 m resolution products. Considering the area consistency, spatial pattern overlap, and positional accuracy, GlobeLand30 and ESA WorldCover cropland distribution data performed best at 30 m and 10 m resolutions, respectively. These findings provide a valuable reference for selecting cropland products and can promote refined cropland mapping of the Hehuang Valley and YZR area. Full article
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<p>Overview of the study area: (<b>a</b>) study area location, (<b>b</b>) YZR area, and (<b>c</b>) Hehuang Valley. Note: elevation and slope may also vary on Earth due to its geological activity.</p>
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<p>Verification sample points: (<b>a</b>) sample points in the Hehuang Valley and (<b>b</b>) sample points in the YZR area.</p>
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<p>Illustration of the relative area difference (%) between the cropland distribution data products and statistical data in the Hehuang Valley. Note that the overestimation proportions exceeding 100% were truncated at 100% to maintain the balance of the color bar. The issue of severe overestimation was common in GL and GLC. (<b>a</b>) WC (10 m), (<b>b</b>) LC (10 m), (<b>c</b>) AIEC (10 m), (<b>d</b>) GL (30 m), (<b>e</b>) GLC (30 m), and (<b>f</b>) CLCD (30 m).</p>
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<p>Illustration of the relative area difference (%) between the cropland distribution data products and statistical data in the YZR area. (<b>a</b>) WC (10 m), (<b>b</b>) LC (10 m), (<b>c</b>) AIEC (10 m), (<b>d</b>) GL (30 m), (<b>e</b>) GLC (30 m), and (<b>f</b>) CLCD (30 m).</p>
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<p>Spatial consistency among overlay results: (<b>a</b>) 10 m cropland distribution data in the Hehuang Valley area, (<b>b</b>) 10 m cropland distribution data in the YZR area, (<b>c</b>) 30 m cropland distribution data in the Hehuang Valley area, and (<b>d</b>) 30 m cropland distribution data in the YZR area.</p>
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<p>Details of cultivated land data in the Hehuang Valley. (<b>a</b>) Slope cropland, (<b>b</b>) areas with concentrated cropland distribution, (<b>c</b>) urban green spaces, and (<b>d</b>) areas with a mixture of cropland and other land types. WC (10 m), LC (10 m), AIEC (10 m), GL (30 m), GLC (30 m), and CLCD (30 m). Note: The process of manual visual interpretation primarily relies on sub-meter resolution remote sensing imagery, supplemented by auxiliary data, such as DEM data, ground survey samples, and other cropland distribution data. In this context, the primary focus is on the misclassification of cropland. Therefore, forest, grassland, and urban green spaces were categorized as a single class, while built-up areas and bare areas were grouped into another class.</p>
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<p>Details of cultivated land data in the YZR area. (<b>a1</b>,<b>a2</b>) WC (10 m), (<b>b1</b>,<b>b2</b>) LC (10 m), (<b>c1</b>,<b>c2</b>) AIEC (10 m), (<b>d1</b>,<b>d2</b>) GL (30 m), (<b>e1</b>,<b>e2</b>) GLC (30 m), and (<b>f1</b>,<b>f2</b>) CLCD (30 m). Note: The process of manual visual interpretation primarily relies on sub-meter resolution remote sensing imagery, supplemented by auxiliary data, such as DEM data, ground survey samples, and other cropland distribution data. In this case, the focus is on the omission of cultivated land. Consequently, only the cropland category was interpreted.</p>
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<p>Pixel distribution of cropland distribution data in the Hehuang Valley. (<b>a</b>) WC (10 m), (<b>b</b>) LC (10 m), (<b>c</b>) AIEC (10 m), (<b>d</b>) GL (30 m), (<b>e</b>) GLC (30 m), and (<b>f</b>) CLCD (30 m).</p>
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<p>Pixel distribution of cropland distribution data in the YZR area. (<b>a</b>) WC (10 m), (<b>b</b>) LC (10 m), (<b>c</b>) AIEC (10 m), (<b>d</b>) GL (30 m), (<b>e</b>) GLC (30 m), and (<b>f</b>) CLCD (30 m).</p>
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<p>Area proportion of pixels with different consistencies in different terrain factor ranges in the Hehuang Valley region. (<b>a</b>) Proportion of consistent pixels among the 10 m cropland distribution data products at different slope ranges. (<b>b</b>) Proportion of consistent pixels among the 30 m cropland distribution data products at different slope ranges. (<b>c</b>) Proportion of consistent pixels among the 10 m cropland distribution data products at different elevation ranges. (<b>d</b>) Proportion of consistent pixels among the 30 m cropland distribution data products at different elevation ranges.</p>
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<p>Area proportion of pixels with different consistencies among the different terrain factor ranges in the YZR area. (<b>a</b>) Proportion of consistent pixels among the 10 m cropland distribution data products at different slope ranges. (<b>b</b>) Proportion of consistent pixels among the 30 m cropland distribution data products at different slope ranges. (<b>c</b>) Proportion of consistent pixels among the 10 m cropland distribution data products at different elevation ranges. (<b>d</b>) Proportion of consistent pixels among the 30 m cropland distribution data products at different elevation ranges.</p>
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<p>Forage fields with cultivated grain at high elevations.</p>
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27 pages, 13823 KiB  
Article
Application of Remote Sensing and Explainable Artificial Intelligence (XAI) for Wildfire Occurrence Mapping in the Mountainous Region of Southwest China
by Jia Liu, Yukuan Wang, Yafeng Lu, Pengguo Zhao, Shunjiu Wang, Yu Sun and Yu Luo
Remote Sens. 2024, 16(19), 3602; https://doi.org/10.3390/rs16193602 - 27 Sep 2024
Abstract
The ecosystems in the mountainous region of Southwest China are exceptionally fragile and constitute one of the global hotspots for wildfire occurrences. Understanding the complex interactions between wildfires and their environmental and anthropogenic factors is crucial for effective wildfire modeling and management. Despite [...] Read more.
The ecosystems in the mountainous region of Southwest China are exceptionally fragile and constitute one of the global hotspots for wildfire occurrences. Understanding the complex interactions between wildfires and their environmental and anthropogenic factors is crucial for effective wildfire modeling and management. Despite significant advancements in wildfire modeling using machine learning (ML) methods, their limited explainability remains a barrier to utilizing them for in-depth wildfire analysis. This paper employs Logistic Regression (LR), Random Forest (RF), and Extreme Gradient Boosting (XGBoost) models along with the MODIS global fire atlas dataset (2004–2020) to study the influence of meteorological, topographic, vegetation, and human factors on wildfire occurrences in the mountainous region of Southwest China. It also utilizes Shapley Additive exPlanations (SHAP) values, a method within explainable artificial intelligence (XAI), to demonstrate the influence of key controlling factors on the frequency of fire occurrences. The results indicate that wildfires in this region are primarily influenced by meteorological conditions, particularly sunshine duration, relative humidity (seasonal and daily), seasonal precipitation, and daily land surface temperature. Among local variables, altitude, proximity to roads, railways, residential areas, and population density are significant factors. All models demonstrate strong predictive capabilities with AUC values over 0.8 and prediction accuracies ranging from 76.0% to 95.0%. XGBoost outperforms LR and RF in predictive accuracy across all factor groups (climatic, local, and combinations thereof). The inclusion of topographic factors and human activities enhances model optimization to some extent. SHAP results reveal critical features that significantly influence wildfire occurrences, and the thresholds of positive or negative changes, highlighting that relative humidity, rain-free days, and land use land cover changes (LULC) are primary contributors to frequent wildfires in this region. Based on regional differences in wildfire drivers, a wildfire-risk zoning map for the mountainous region of Southwest China is created. Areas identified as high risk are predominantly located in the Northwestern and Southern parts of the study area, particularly in Yanyuan and Miyi, while areas assessed as low risk are mainly distributed in the Northeastern region. Full article
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<p>Location of the research region and the distribution of MODIS active fire incidents from 2004 to 2020. Maps at a national scale represent the kernel density of local wildfires for the same time frame.</p>
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<p>Hierarchical importance of climatic variables.</p>
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<p>Hierarchical importance of local factors.</p>
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<p>The SHAP summary plot ranks the top 20 variables affecting model predictions by their mean absolute SHAP values, shown on the <span class="html-italic">y</span>-axis. Subfigure (<b>a</b>) showcases the importance of these features, while subfigure (<b>b</b>) illustrates their positive or negative effects on wildfire predictions through scatter points.</p>
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<p>The SHAP dependence plots (<b>a</b>) between SHAP values and Da_minRH, with a fitted trend line (red line); (<b>b</b>) between SHAP values and Norainday_avg, with a fitted trend line (red line); (<b>c</b>) between SHAP values and Da_minRH, showing the interaction with Tmax_avg (color scale); (<b>d</b>) between SHAP values and Norainday_avg, showing the interaction with Tmax_avg (color scale). Da_minRH, daily minimum relative humidity; Noraindy_avg, average number of rainless days of fire season.</p>
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<p>SHAP interaction plot (<b>a</b>) and heatmap analysis (<b>b</b>).</p>
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<p>SHAP interaction plot (<b>a</b>) and heatmap analysis (<b>b</b>).</p>
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<p>Fire-occurrence probability: analysis using LR, RF, and XGB based on meteorological factors.</p>
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<p>Fire-occurrence probability: analysis using LR, RF, and XGB based on local factors.</p>
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<p>Fire-occurrence probability: combined meteorological and local factors analysis with LR, RF, and XGB.</p>
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<p>ROC curves of the success rate of three models.</p>
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<p>Comparison of error metrics for different models.</p>
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<p>Risk-assessment mapping results of XGB model.</p>
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25 pages, 10835 KiB  
Article
Sustainable Groundwater Management Using Machine Learning-Based DRASTIC Model in Rurbanizing Riverine Region: A Case Study of Kerman Province, Iran
by Mortaza Tavakoli, Zeynab Karimzadeh Motlagh, Mohammad Hossein Sayadi, Ismael M. Ibraheem and Youssef M. Youssef
Water 2024, 16(19), 2748; https://doi.org/10.3390/w16192748 - 27 Sep 2024
Abstract
Groundwater salinization poses a critical threat to sustainable development in arid and semi-arid rurbanizing regions, exemplified by Kerman Province, Iran. This region experiences groundwater ecosystem degradation as a result of the rapid conversion of rural agricultural land to urban areas under chronic drought [...] Read more.
Groundwater salinization poses a critical threat to sustainable development in arid and semi-arid rurbanizing regions, exemplified by Kerman Province, Iran. This region experiences groundwater ecosystem degradation as a result of the rapid conversion of rural agricultural land to urban areas under chronic drought conditions. This study aims to enhance Groundwater Pollution Risk (GwPR) mapping by integrating the DRASTIC index with machine learning (ML) models, including Random Forest (RF), Boosted Regression Trees (BRT), Generalized Linear Model (GLM), Support Vector Machine (SVM), and Multivariate Adaptive Regression Splines (MARS), alongside hydrogeochemical investigations, to promote sustainable water management in Kerman Province. The RF model achieved the highest accuracy with an Area Under the Curve (AUC) of 0.995 in predicting GwPR, outperforming BRT (0.988), SVM (0.977), MARS (0.951), and GLM (0.887). The RF-based map identified new high-vulnerability zones in the northeast and northwest and showed an expanded moderate vulnerability zone, covering 48.46% of the study area. Analysis revealed exceedances of WHO standards for total hardness (TH), sodium, sulfates, chlorides, and electrical conductivity (EC) in these high-vulnerability areas, indicating contamination from mineralized aquifers and unsustainable agricultural practices. The findings underscore the RF model’s effectiveness in groundwater prediction and highlight the need for stricter monitoring and management, including regulating groundwater extraction and improving water use efficiency in riverine aquifers. Full article
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<p>Location of the study region in Kerman Province highlighted by the red polygon in southern Iran.</p>
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<p>Location of sampling points in in Kerman Province, highlighted by the red polygon in southern Iran.</p>
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<p>General procedure followed in the research.</p>
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<p>The spatial arrangement of parameters indicating groundwater vulnerability and the creation of maps illustrating the factors influencing groundwater vulnerability: (<b>a</b>) depth to water table, (<b>b</b>) net recharge, (<b>c</b>) aquifer media, (<b>d</b>) slope, (<b>e</b>) soil media, (<b>f</b>) impact of vadose zone, and (<b>g</b>) hydraulic conductivity.</p>
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<p>Groundwater vulnerability map based on DRASTIC index in Kerman Province, highlighted by the red polygon in southern Iran.</p>
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<p>GwPR maps of the Kerman Province, highlighted by the red polygon in southern Iran, using (<b>a</b>) RF, (<b>b</b>) MARS, (<b>c</b>) SVM, (<b>d</b>) GLM, and (<b>e</b>) BRT.</p>
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<p>The validation outcomes of the suggested frameworks by the ROC curves for RF, MARS, SVM, GLM, and BRT.</p>
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<p>The spatial variability of (<b>a</b>) TDS, (<b>b</b>) EC, (<b>c</b>) Th, (<b>d</b>) CL<sup>−</sup>, (<b>e</b>) SO4<sup>2−</sup>, (<b>f</b>) HCO<sup>3−</sup>, (<b>g</b>) pH, (<b>h</b>) Mg<sup>2+</sup>, and (<b>i</b>) Ca<sup>2+</sup> concentrations in the water samples collected from the research site.</p>
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23 pages, 36997 KiB  
Article
Enhanced Monitoring of Sub-Seasonal Land Use Dynamics in Vietnam’s Mekong Delta through Quantile Mapping and Harmonic Regression
by Nick Kupfer, Tuan Quoc Vo, Felix Bachofer, Juliane Huth, Harry Vereecken, Lutz Weihermüller and Carsten Montzka
Remote Sens. 2024, 16(19), 3569; https://doi.org/10.3390/rs16193569 - 25 Sep 2024
Abstract
In response to economic and environmental challenges like sea-level rise, salinity intrusion, groundwater extraction, sand mining, and sinking delta phenomena, the demand for solutions to adapt to changing conditions in riverine environments has increased significantly. High-quality analyses of land use and land cover [...] Read more.
In response to economic and environmental challenges like sea-level rise, salinity intrusion, groundwater extraction, sand mining, and sinking delta phenomena, the demand for solutions to adapt to changing conditions in riverine environments has increased significantly. High-quality analyses of land use and land cover (LULC) dynamics play a critical role in addressing these challenges. This study introduces a novel high-spatial resolution satellite-based approach to identify sub-seasonal LULC dynamics in the Mekong River Delta (MRD), employing a three-year (2021–2023) Sentinel-1 and Sentinel-2 satellite data time series. The primary obstacle is discerning detailed vegetation dynamics, particularly the seasonality of rice crops, answered through quantile mapping, harmonic regression with Fourier transform, and phenological metrics as inputs to a random forest machine learning classifier. Due to the substantial data volume, Google’s cloud computing platform Earth Engine was utilized for the analysis. Furthermore, the study evaluated the relative significance of various input features. The overall accuracy of the classification is 82.6% with a kappa statistic of 0.81, determined using comprehensive reference data collected in Vietnam. While the purely pixel-based approach has limitations, it proves to be a viable method for high-spatial resolution satellite image time series classification of the MRD. Full article
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<p>The Mekong River Delta (marked green in the overview) in Vietnam (red), its provincial division, and the location of collected reference data points.</p>
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<p>Workflow of the LULC analysis with data collection, input features used for classification, and final uncertainty analysis.</p>
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<p>(<b>a</b>) Harmonic curve representative of the first harmonic term and (<b>b</b>) curves for the first, second, and third harmonic terms (after [<a href="#B84-remotesensing-16-03569" class="html-bibr">84</a>]).</p>
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<p>LULC classification based on Sentinel-2 and -1 time series (2021–2023) of the Mekong River Delta with detailed sub-figures of An Giang/Dong Thap (<b>left</b>) and Ben Tre/Tra Vinh (<b>right</b>).</p>
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<p>LULC distribution of the Mekong River Delta 2021–2023. The three small boxes belong to the minor classes <span class="html-italic">Pineapple/Coconut mixed</span> (0.4%), <span class="html-italic">Water Melon</span> (0.1%), and <span class="html-italic">Casuarina Forest</span> (0.1%).</p>
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<p>F1 score for the 18 classes of the time series analysis.</p>
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<p>Exemplary illustrations of vegetation metrics that support the differentiation of different land use types.</p>
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<p>Time−dependent spectral progression of two exemplary rice and aquaculture classes derived from NDVI signals including harmonic fitting.</p>
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<p>Time−dependent spectral progression of two exemplary rice and aquaculture classes derived from NDVI signals including harmonic fitting.</p>
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<p>Pair-wise Pearson correlation matrix of each training image. “Bx_py” refers to the calculated quantile band (Band x; quantile y). “HMx_y” refers to the calculated harmonic regression (Harmonic Model term x; Band y).</p>
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<p>Validation error matrix showing the user’s, producer’s and overall accuracy of the classification.</p>
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<p>Analysis of the accuracy deviation for the user’s accuracy.</p>
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<p>Analysis of the accuracy deviation for the producer’s accuracy.</p>
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26 pages, 28717 KiB  
Article
Assessing Land-Cover Change Trends, Patterns, and Transitions in Coalfield Counties of Eastern Kentucky, USA
by Suraj K C, Buddhi R. Gyawali, Shawn Lucas, George F. Antonious, Anuj Chiluwal and Demetrio Zourarakis
Land 2024, 13(9), 1541; https://doi.org/10.3390/land13091541 - 23 Sep 2024
Abstract
Surface coal mining and reclamation have greatly reshaped eastern Kentucky’s landscape affecting its socioeconomic, environmental and climatic aspects. This study examined the land-cover changes, trends and patterns in Floyd, Knott, Letcher, Magoffin, Martin, Perry, and Pike counties from 2004 to 2019. Using a [...] Read more.
Surface coal mining and reclamation have greatly reshaped eastern Kentucky’s landscape affecting its socioeconomic, environmental and climatic aspects. This study examined the land-cover changes, trends and patterns in Floyd, Knott, Letcher, Magoffin, Martin, Perry, and Pike counties from 2004 to 2019. Using a random forest classifier, land cover was categorized into seven major classes, i.e., water, barren land, developed land, forest, shrubland, herbaceous, and planted/cultivated, majorly based on Landsat images. The Kappa accuracy ranged from 75 to 89%. The results showed a notable increase in forest area from 5052 sq km to 5305 sq km accompanied by a substantial decrease in barren land from 179 sq km to 91 sq km from 2004 to 2019. These findings demonstrated that reclamation activities positively impacted the forest expansion and reduced the barren land of the study area. Key land-cover transitions included barren land to shrubland/herbaceous, forest to shrubland, and shrubland to forest, indicating vegetation growth from 2004 to 2019. An autocorrelation analysis indicated similar land-cover types clustered together, showing effective forest restoration efforts. As surface coal mining and reclamation significantly influenced the landscapes of the coalfield counties in eastern Kentucky, this study provides a holistic perspective for understanding the repercussions of these transformations, including their effects on humans, society, and environmental health. Full article
Show Figures

Figure 1

Figure 1
<p>Map of study area: (<b>a</b>) contiguous USA showing KY, (<b>b</b>) Map of KY showing study area counties within blue border, (<b>c</b>) DEM of study area, (<b>d</b>) coalfield counties of study area.</p>
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<p>Study workflow.</p>
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<p>Topographic layers: (<b>a</b>) elevation, (<b>b</b>) slope, (<b>c</b>) aspect, (<b>d</b>) land capability classes of the study area.</p>
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<p>Land-cover maps of the study area for 2004 and 2019.</p>
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<p>Map showing land-cover change in the study area from 2004 to 2019.</p>
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<p>(<b>a</b>) Land-cover change trends in the study area from 2004 to 2019. (<b>b</b>) Land-cover change trends in the study area from 2004 to 2019.</p>
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<p>Graphical representation of percentage change in land-cover classes between the years 2004 and 2019 in the study area.</p>
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<p>Hot spot and cold spot mapping of herbaceous and developed land-cover change using Gi* Statistic between 2004 and 2019 in eastern Kentucky.</p>
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<p>Hot spot and cold spot mapping of forest and barren land-cover change using Gi* Statistic between 2004 and 2019 in eastern Kentucky.</p>
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<p>Hot spot and cold spot mapping of shrubland land-cover change using Gi* Statistic between 2004 and 2019 in eastern Kentucky.</p>
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<p>Validation points and training samples shown in a map of the study area for 2004 and 2019.</p>
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