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Search Results (9,006)

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Keywords = land-cover and land-use

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16 pages, 858 KiB  
Article
E²VRP-CPP: An Energy-Efficient Approach for Multi-UAV Multi-Region Coverage Path Planning Optimization in the Enhanced Vehicle Routing Problem
by Yuechao Zang, Xueqin Huang, Min Lu, Qianzhen Zhang and Xianqiang Zhu
Drones 2025, 9(3), 200; https://doi.org/10.3390/drones9030200 - 11 Mar 2025
Abstract
Unmanned Aerial Vehicles (UAVs) are widely used in applications such as land assessment, surveillance, and rescue operations, where they are often required to cover multiple disjoint regions. Coverage Path Planning (CPP) aims to determine optimal paths for UAVs to cover these areas. While [...] Read more.
Unmanned Aerial Vehicles (UAVs) are widely used in applications such as land assessment, surveillance, and rescue operations, where they are often required to cover multiple disjoint regions. Coverage Path Planning (CPP) aims to determine optimal paths for UAVs to cover these areas. While CPP for single regions has been extensively studied, multi-region CPP with multiple UAVs remains underexplored. Existing methods typically focus on minimizing path length, but often neglect the nonlinear variations in energy consumption during flight, limiting their practical applicability. This paper addresses the multi-UAV, multi-region CPP as a variant of the Vehicle Routing Problem (VRP) with energy estimation. We propose an approach that optimizes UAV flight speeds to minimize energy consumption, supported by an accurate energy estimation algorithm. In addition, a heuristic algorithm is developed to balance the distribution of tasks among UAVs, considering both the scanning and transit times. Experiments using real-world data from the Changsha urban area demonstrate that our approach outperforms state-of-the-art methods in computational efficiency and energy savings, highlighting its potential for practical UAV deployment. Full article
26 pages, 14588 KiB  
Article
Landscape Visual Affordance Evaluation at a Regional Scale in National Parks: A Case Study of the Changhong Area in Qianjiangyuan National Park
by Yuchen Dong, Yuan Kang and Chengzhao Wu
Land 2025, 14(3), 589; https://doi.org/10.3390/land14030589 (registering DOI) - 11 Mar 2025
Abstract
National parks play a vital role in safeguarding natural scenery, maintaining ecological integrity, and preserving cultural heritage, while simultaneously offering valuable opportunities for recreation and education. Among the diverse resources provided by national parks, visual landscape resources hold particular significance due to their [...] Read more.
National parks play a vital role in safeguarding natural scenery, maintaining ecological integrity, and preserving cultural heritage, while simultaneously offering valuable opportunities for recreation and education. Among the diverse resources provided by national parks, visual landscape resources hold particular significance due to their capacity to inspire, educate, and enhance aesthetic appreciation. However, assessing and managing these resources remain challenging, as they span both the physical attributes of the landscape and the human visual perception process. This study aims to develop a theoretical and practical framework for evaluating the “landscape visual affordance” of national parks. Grounded in ecological psychology’s affordance theory, the proposed approach integrates physical affordance and sensory affordance, encompassing both the objective physical attributes of the landscape and the subjective processes of human perception. Drawing on a multi-dimensional set of indicators, the research quantifies physical features—such as topography, land use, vegetation cover, and landscape structure—as well as sensory dimensions, including visibility, visual prominence, and viewing frequency. These elements are synthesized into a landscape visibility assessment model built upon the affordance theory framework. The results demonstrate that landscape visual affordance effectively identifies landscape patches with varying degrees of visual quality and importance within national parks and other protected areas. By providing robust support for management decisions—such as zoned protection, optimizing recreational facilities, and evaluating visitor carrying capacity—this model offers new insights and practical guidance for the sustainable planning and management of landscapes in national parks and other ecologically critical regions. Full article
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<p>Theoretical Framework: Linking Affordance Theory and Visual Landscape Evaluation.</p>
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<p>Study Area Overview.</p>
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<p>Research Framework.</p>
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<p>Landscape Visual Characteristic Types.</p>
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<p>Affordance classification. (<b>a</b>) Physical Landscape Affordance and (<b>b</b>) Visual Sensory Affordance.</p>
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<p>Factors in VSA. (<b>a</b>) Relative Slope Affordance, (<b>b</b>) Visual Prominence, (<b>c</b>) Visual Distance Bands, (<b>d</b>) Visibility, and (<b>e</b>) Viewing Probability.</p>
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<p>Landscape Visual Affordance.</p>
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26 pages, 24249 KiB  
Article
Evaluation of Spectral Indices and Global Thresholding Methods for the Automatic Extraction of Built-Up Areas: An Application to a Semi-Arid Climate Using Landsat 8 Imagery
by Yassine Harrak, Ahmed Rachid and Rahim Aguejdad
Urban Sci. 2025, 9(3), 78; https://doi.org/10.3390/urbansci9030078 - 11 Mar 2025
Viewed by 26
Abstract
The rapid expansion of built-up areas (BUAs) requires effective spatial and temporal monitoring, being a crucial practice for urban land use planning, resource allocation, and environmental studies, and spectral indices (SIs) can provide efficiency and reliability in automating the process of BUAs extraction. [...] Read more.
The rapid expansion of built-up areas (BUAs) requires effective spatial and temporal monitoring, being a crucial practice for urban land use planning, resource allocation, and environmental studies, and spectral indices (SIs) can provide efficiency and reliability in automating the process of BUAs extraction. This paper explores the use of nine spectral indices and sixteen thresholding methods for the automatic mapping of BUAs using Landsat 8 imagery from a semi-arid climate in Morocco during spring and summer. These indices are the Normalized Difference Built-Up Index (NDBI), the Vis-red-NIR Built-Up Index (VrNIR-BI), the Perpendicular Impervious Surface Index (PISI), the Combinational Biophysical Composition Index (CBCI), the Normalized Built-up Area Index (NBAI), the Built-Up Index (BUI), the Enhanced Normalized Difference Impervious Surfaces Index (ENDISI) and the Built-up Land Features Extraction Index (BLFEI). Results show that BLFEI, SWIRED, and BUI maintain high separability between built-up and each of the other land cover types across both seasons, as evaluated via the Spectral Discrimination Index (SDI). The lowest SDI values for all three indices were observed for bare soil against BUAs, with BLFEI recording 1.21 in the wet season and 1.05 in the dry season, SWIRED yielding 1.22 and 1.08, and BUI showing 1.21 and 1.08, demonstrating their robustness in distinguishing BUAs from other land covers under varying phenological and soil moisture conditions. These indices reached overall accuracies of 93.97%, 93.39% and 92.81%, respectively, in wet conditions, and 91.57%, 89.17% and 89.67%, respectively, in dry conditions. The assessment of thresholding methods reveals that the Minimum method resulted in the highest accuracies for these indices in wet conditions, where bimodal medium peaked histograms were observed, whereas the use of Li, Huang, Shanbhag, Otsu, K-means, or IsoData was found to be the most effective under dry conditions, where more peaked histograms were observed. Full article
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<p>Study area. (<b>a</b>) Casablanca-Settat region in Morocco; (<b>b</b>) Settat municipality and the province of Settat; (<b>c</b>) Basic map of Settat.</p>
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<p>Flowchart of the followed methodology.</p>
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<p>SVM classification of LULC in the study area: (<b>a</b>) Collected training data; (<b>b</b>) LULC classification map; (<b>c</b>) Reference points for accuracy assessment.</p>
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<p>Spectral profiles of surface reflectance in the study area: (<b>a</b>) Spring; (<b>b</b>) Summer.</p>
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<p>Index-based maps in spring, plotted with a 2% standard deviation stretching to enhance more subtlety differences.</p>
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<p>Index-based maps in summer, plotted with a 2% standard deviation stretching to enhance more subtlety differences.</p>
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<p>Histograms of pixel values and their respective composition of land cover distributions according to the SVM classification, grouped in 30 bins in (<b>a</b>) Spring; (<b>b</b>) Summer.</p>
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<p>Radar plots of OAs and Kappa coefficients corresponding to thresholding methods and each of the SIs in: (<b>a</b>) Spring, (<b>b</b>) Summer.</p>
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<p>Best performing binary masks for each index in a sample area during spring and Google Earth imagery from February 2021. Refer to <a href="#urbansci-09-00078-t005" class="html-table">Table 5</a> for accuracies and thresholding methods. Red marks represent a sample of: 1. BUAs, 2. Bare land, 3. Agriculture, 4. Trees and 5. Water.</p>
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<p>Best performing binary masks for each index in a sample area during summer and Google Earth imagery from November 2021. Refer to <a href="#urbansci-09-00078-t005" class="html-table">Table 5</a> for accuracies and thresholding methods. Red marks represent a sample of: 1. BUAs, 2. Bare land, 3. Agriculture, 4. Trees and 5. Water.</p>
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20 pages, 42010 KiB  
Article
Coastline and Riverbed Change Detection in the Broader Area of the City of Patras Using Very High-Resolution Multi-Temporal Imagery
by Spiros Papadopoulos, Vassilis Anastassopoulos and Georgia Koukiou
Electronics 2025, 14(6), 1096; https://doi.org/10.3390/electronics14061096 - 11 Mar 2025
Viewed by 16
Abstract
Accurate and robust information on land cover changes in urban and coastal areas is essential for effective urban land management, ecosystem monitoring, and urban planning. This paper details the methodology and results of a pixel-level classification and change detection analysis, leveraging 1945 Royal [...] Read more.
Accurate and robust information on land cover changes in urban and coastal areas is essential for effective urban land management, ecosystem monitoring, and urban planning. This paper details the methodology and results of a pixel-level classification and change detection analysis, leveraging 1945 Royal Air Force (RAF) aerial imagery and 2011 Very High-Resolution (VHR) multispectral WorldView-2 satellite imagery from the broader area of Patras, Greece. Our attention is mainly focused on the changes in the coastline from the city of Patras to the northeast direction and the two major rivers, Charadros and Selemnos. The methodology involves preprocessing steps such as registration, denoising, and resolution adjustments to ensure computational feasibility for both coastal and riverbed change detection procedures while maintaining critical spatial features. For change detection at coastal areas over time, the Normalized Difference Water Index (NDWI) was applied to the new imagery to mask out the sea from the coastline and manually archive imagery from 1945. To determine the differences in the coastline between 1945 and 2011, we perform image differencing by subtracting the 1945 image from the 2011 image. This highlights the areas where changes have occurred over time. To conduct riverbed change detection, feature extraction using the Gray-Level Co-occurrence Matrix (GLCM) was applied to capture spatial characteristics. A Support Vector Machine (SVM) classification model was trained to distinguish river pixels from non-river pixels, enabling the identification of changes in riverbeds and achieving 92.6% and 92.5% accuracy for new and old imagery, respectively. Post-classification processing included classification maps to enhance the visualization of the detected changes. This approach highlights the potential of combining historical and modern imagery with supervised machine learning methods to effectively assess coastal erosion and riverbed alterations. Full article
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<p>Study area: The broader area of the city of Patras. Map data ©2024: Google, SIO, NOAA, U.S Navy, NGA, GEBCO, TerraMetrics, Airbus.</p>
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<p>Tinv matrix is given from cp2tform MATLAB built-in function. This matrix contains the transformation coefficients <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>a</mi> </mrow> <mrow> <mn>11</mn> </mrow> </msub> <msub> <mrow> <mo>,</mo> <mi>a</mi> </mrow> <mrow> <mn>12</mn> </mrow> </msub> <mo>,</mo> <msub> <mrow> <mi>a</mi> </mrow> <mrow> <mn>21</mn> </mrow> </msub> <mo>,</mo> <msub> <mrow> <mi>a</mi> </mrow> <mrow> <mn>22</mn> <mo>,</mo> </mrow> </msub> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>t</mi> </mrow> <mrow> <mn>1</mn> </mrow> </msub> <mo>,</mo> <msub> <mrow> <mi>t</mi> </mrow> <mrow> <mn>2</mn> </mrow> </msub> </mrow> </semantics></math>.</p>
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<p>Registration with affine transformation between the panchromatic image from 2011 and the archive image from 1945 depicting the control points used for determining the affine transformation (<b>a</b>) Fixed VHR panchromatic image; (<b>b</b>) moving archive aerial image; (<b>c</b>) registered archive aerial image.</p>
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<p>The two images after adaptive histogram equalization to enhance the contrast. (<b>a</b>) 1945 archive RAF image; (<b>b</b>) VHR WorldView-2 2011 image.</p>
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<p>The two imageries after thresholding seem to have been “cleared” from noisy pixels near the coastline. (<b>a</b>) 1945 archive RAF image; (<b>b</b>) VHR WorldView-2 2011 image.</p>
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<p>Black- and white-masked (<b>a</b>) archive (1945) and (<b>b</b>) recent (2011) imagery, which is used for coastal change detection. The black and white mask emphasizes the land–water interface and accelerates the identification of shoreline shifts and morphological changes over time.</p>
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<p>RGB map of the differences from 1945 to 2011. In red, we have the recently developed sections of the coastline. Blue represents the coastline areas that existed in 1945 but not now, and green represents the areas with mutual information.</p>
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<p>Precision comparison of the area Plaz, Patras, with our methodology (<b>a</b>) and using Google Earth Pro (<b>b</b>). Map data ©2025: Google, Maxar Technologies. In red, we have the recently developed sections of the coastline. Blue represents the coastline areas that existed in 1945 but not now, and green represents the areas with mutual information.</p>
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<p>Charadros river discharge calculation over the years with our methodology (<b>a</b>,<b>b</b>) using Google Earth Pro. Map data ©2025: Google, Maxar Technologies. In red, we have the recently developed sections of the coastline. Blue represents the coastline areas that existed in 1945 but not now, and green represents the areas with mutual information.</p>
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<p>Original images with the sea masked out and lower resolution for computational efficiency: (<b>a</b>) 1945 RAF aerial image; (<b>b</b>) 2011 Worldview-2 satellite imagery.</p>
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<p>Rivers Charadros and Selemnos from 1945 (<b>a</b>) to 2011 (<b>b</b>).</p>
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<p>Rivers Charadros and Selemnos from 1945 before (<b>a</b>,<b>b</b>) after adaptive histogram equalization.</p>
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<p>Final products after preprocessing the images (1945) (<b>a</b>) and (2011) (<b>b</b>), which were used for feature extraction.</p>
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<p>Training datasets of river (with blue) and non-river (with red) areas in both old (<b>a</b>) and new (<b>b</b>) imageries.</p>
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<p>SVM decision boundaries for the training pixels, for old imagery (<b>a</b>) and new imagery (<b>b</b>), described with two features. Class 1 (river) is represented with blue and class 0 (not river) with red.</p>
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<p>Binary classification maps of Charadros and Selemnos from 1945 (<b>a</b>) and 2011 (<b>b</b>).</p>
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<p>Testing datasets of river (with blue) and non-river (with red) areas in both old (<b>a</b>) and new (<b>b</b>) imageries.</p>
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<p>Confusion matrices of testing pixels for both old (<b>a</b>) and new (<b>b</b>) imageries. Class one represents the non-river pixels, and class two represents pixels that are classified as river.</p>
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<p>ROC curve for testing pixel classification from both old (<b>a</b>) and new (<b>b</b>) imageries.</p>
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<p>Areas of interest that changed drastically over the years. The deltas of Charadros and Selemnos are depicted with the two left parallelograms and two main bodies at the right. The old image (1945) is depicted in (<b>a</b>) and the new image (2011) is depicted in (<b>b</b>).</p>
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18 pages, 3674 KiB  
Article
Detection and Quantification of Vegetation Losses with Sentinel-2 Images Using Bi-Temporal Analysis of Spectral Indices and Transferable Random Forest Model
by Alicja Rynkiewicz, Agata Hościło, Linda Aune-Lundberg, Anne B. Nilsen and Aneta Lewandowska
Remote Sens. 2025, 17(6), 979; https://doi.org/10.3390/rs17060979 (registering DOI) - 11 Mar 2025
Viewed by 67
Abstract
The precise spatially explicit data on land cover and land use changes is one of the essential variables for enhancing the quantification of greenhouse gas emissions and removals, which is relevant for meeting the goal of the European economy and society to become [...] Read more.
The precise spatially explicit data on land cover and land use changes is one of the essential variables for enhancing the quantification of greenhouse gas emissions and removals, which is relevant for meeting the goal of the European economy and society to become climate-neutral by 2050. The accuracy of the machine learning models trained on remote-sensed data suffers from a lack of reliable training datasets and they are often site-specific. Therefore, in this study, we proposed a method that integrates the bi-temporal analysis of the combination of spectral indices that detects the potential changes, which then serve as reference data for the Random Forest classifier. In addition, we examined the transferability of the pre-trained model over time, which is an important aspect from the operational point of view and may significantly reduce the time required for the preparation of reliable and accurate training data. Two types of vegetation losses were identified: woody coverage converted to non-woody vegetation, and vegetated areas converted to sealed surfaces or bare soil. The vegetation losses were detected annually over the period 2018–2021 with an overall accuracy (OA) above 0.97 and a Kappa coefficient of 0.95 for all time intervals in the study regions in Poland and Norway. Additionally, the pre-trained model’s temporal transferability revealed an improvement of the OA by 5 percentage points and the macroF1-Score value by 12 percentage points compared to the original model. Full article
(This article belongs to the Special Issue Women’s Special Issue Series: Remote Sensing 2023-2025)
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<p>The location of the study areas in Poland (Łódź Province) and Norway (Viken County) marked with a red and blue outline, respectively. High-Resolution Image Mosaic 2018—True Colour (10 m) from the Copernicus Land Monitoring Service was used as the base map.</p>
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<p>Scheme of land cover change detection approach divided into two phases based on multi-temporal Sentinel-2 data.</p>
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<p>The size of the change polygons in classes 1 and 2 for Poland and Norway for three time intervals.</p>
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<p>Example of changes detected on an annual basis for the period 2018–2021 in Łódź Province (Poland) using the LCCD method. From left to right: Sentinel-2 mosaic for year n, Sentinel-2 mosaic for year n + 1, LCC for the time interval between year n and year n + 1 (classes: 1, woody coverage converted to non-woody; 2, vegetated surfaces converted to sealed surfaces).</p>
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<p>Example of changes detected on an annual basis for the period 2018–2021 in the study area in Norway using the LCCD method. From left to right: Sentinel-2 mosaic for year n, Sentinel-2 mosaic for year n + 1, LCC for the time interval between year n and year n + 1 (classes: 1, woody coverage converted to non-woody; 2, vegetated surfaces converted to sealed surfaces).</p>
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<p>Confusion matrices calculated for RF models (classes: 0, no change; 1, woody coverage converted to non-woody; 2, vegetated surfaces converted to sealed surfaces) for Poland and Norway.</p>
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<p>Confusion matrices and statistics for the independent verification of LCC products for the period (<b>a</b>) 2020–2021 in Poland, (<b>b</b>) 2020–2021 in Norway, (<b>c</b>) 2019–2020 in Poland, and (<b>d</b>) 2019–2020 in Poland using the pre-trained model.</p>
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23 pages, 14181 KiB  
Article
Time Series Remote Sensing Image Classification with a Data-Driven Active Deep Learning Approach
by Gaoliang Xie, Peng Liu, Zugang Chen, Lajiao Chen, Yan Ma and Lingjun Zhao
Sensors 2025, 25(6), 1718; https://doi.org/10.3390/s25061718 - 10 Mar 2025
Viewed by 119
Abstract
Recently, Time Series Remote Sensing Images (TSRSIs) have been proven to be a significant resource for land use/land cover (LULC) mapping. Deep learning methods perform well in managing and processing temporal dependencies and have shown remarkable advancements within this domain. Although deep learning [...] Read more.
Recently, Time Series Remote Sensing Images (TSRSIs) have been proven to be a significant resource for land use/land cover (LULC) mapping. Deep learning methods perform well in managing and processing temporal dependencies and have shown remarkable advancements within this domain. Although deep learning methods have exhibited outstanding performance in classifying TSRSIs, they rely on enough labeled time series samples for effective training. Labeling data with a wide geographical range and a long time span is highly time-consuming and labor-intensive. Active learning (AL) is a promising method of selecting the most informative data for labeling to save human labeling efforts. It has been widely applied in the remote sensing community, except for the classification of TSRSIs. The main challenge of AL in TSRSI classification is dealing with the internal temporal dependencies within TSRSIs and evaluating the informativeness of unlabeled time series data. In this paper, we propose a data-driven active deep learning framework for TSRSI classification to address the problem of limited labeled time series samples. First, a temporal classifier for TSRSI classification tasks is designed. Next, we propose an effective active learning method to select informative time series samples for labeling, which considers representativeness and uncertainty. For representativeness, we use the K-shape method to cluster time series data. For uncertainty, we construct an auxiliary deep network to evaluate the uncertainty of unlabeled data. The features with rich temporal information in the classifier’s middle-hidden layers will be fed into the auxiliary deep network. Then, we define a new loss function with the aim of improving the deep model’s performance. Finally, the proposed method in this paper was verified on two TSRSI datasets. The results demonstrate a significant advantage of our method over other approaches to TSRSI. On the MUDS dataset, when the initial number of samples was 100 after our method selected and labeled 2000 samples, an accuracy improvement of 4.92% was achieved. On the DynamicEarthNet dataset, when the initial number of samples was 1000 after our method selected and labeled 2000 samples, an accuracy improvement of 7.81% was attained. On the PASTIS dataset, when the initial number of samples was 1000 after our method selected and labeled 2000 samples, an accuracy improvement of 4.89% was achieved. Our code is available in Data Availability Statement. Full article
(This article belongs to the Section Remote Sensors)
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<p>Flowchart of the proposed method. The main flow is divided into two phases: 1. Training phase: this phase involves training the temporal classifier and the Time-series Loss Prediction Module (TLPM). 2. Inference phase: this phase includes the clustering process, loss prediction, and sample selection.</p>
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<p>The situations of samples that different AL methods tend to select. (<b>a</b>) The AL method based on uncertainty. (<b>b</b>) The AL method based on both representativeness and uncertainty.</p>
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<p>One of the network branches of the Time-series Loss Prediction Module (TLPM). This network branch is composed of a self-attention mechanism, a Global Average Pooling (GAP) layer, and a fully connected (FC) layer. The complete TLPM can be seen in <a href="#sensors-25-01718-f001" class="html-fig">Figure 1</a>.</p>
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<p>The sample images of MUDS and their ground-truth classification maps. They are taken from a region of the United States. In their ground-truth classification map, the white areas represent the built-up areas, while the black areas represent the non-built-up areas. We can clearly observe that the construction areas are gradually increasing. (<b>a</b>) An original image of the MUDS dataset in January 2018. (<b>b</b>) An original image of the MUDS dataset in January 2019. (<b>c</b>) An original image of the MUDS dataset in January 2020. (<b>d</b>) The ground-truth classification map from the MUDS dataset in January 2018. (<b>e</b>) The ground-truth classification map from the MUDS dataset in January 2019. (<b>f</b>) The ground-truth classification map from the MUDS dataset in January 2020.</p>
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<p>The sample images of DynamicEarthNet and their ground-truth classification maps. These images were taken from a region in New Zealand, which include land use types such as soil, forest, agricultural land, etc. In the figure, we can see that the forest area initially decreased and then increased. (<b>a</b>) An RGB image of the DynamicEarthNet dataset in January 2018. (<b>b</b>) An RGB image of the DynamicEarthNet dataset in December 2018. (<b>c</b>) An RGB image of the DynamicEarthNet dataset in December 2019. (<b>d</b>) The ground-truth classification map from the DynamicEarthNet dataset in January 2018. (<b>e</b>) The ground-truth classification map from the DynamicEarthNet dataset in December 2018. (<b>f</b>) The ground-truth classification map from the DynamicEarthNet dataset in December 2019.</p>
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<p>The sample images of PASTIS and their ground-truth classification maps. They were taken from a region of France and reflect crop distributions, with a spatial resolution of 10 m. (<b>a</b>) The RGB image from the PASTIS dataset in February 2019. (<b>b</b>) The RGB image from the PASTIS dataset in July 2019. (<b>c</b>) The RGB image from the PASTIS dataset in August 2019. (<b>d</b>) The ground-truth classification map from the PASTIS dataset in February 2019. (<b>e</b>) The ground-truth classification map from the PASTIS dataset in July 2019. (<b>f</b>) The ground-truth classification map from the PASTIS dataset in August 2019.</p>
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<p>The experiment results on three datasets. (<b>a</b>) The experiment results in OA with an initial sample size of 100 and a sample selection increment of 500 on MUDS. (<b>b</b>) The experiment results in OA with an initial sample size of 1000 and a sample selection increment of 1500 on MUDS. (<b>c</b>) The classification accuracy of the building on MUDS. (<b>d</b>) The experiment results in OA with an initial sample size of 1000 and a sample selection increment of 1000 on DynamicEarthNet. (<b>e</b>) The experiment results in OA with an initial sample size of 10,000 and a sample selection increment of 1500 on DynamicEarthNet. (<b>f</b>) The classification accuracy of the Soil on DynamicEarthNet. (<b>g</b>) The experiment results in OA with an initial sample size of 1000 and a sample selection increment of 1000 on PASTIS. (<b>h</b>) The experiment results in OA with an initial sample size of 5000 and a sample selection increment of 1500 on PASTIS. (<b>i</b>) The classification accuracy of the Corn on PASTIS.</p>
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<p>Classification map comparisons of the compared methods for 16,000 labeled samples in the MUDS dataset.</p>
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<p>Classification map comparisons of the compared methods for 17,500 labeled samples in the DynamicEarthNet dataset.</p>
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<p>Classification map comparisons of the compared methods for 40,000 labeled samples in the PASTIS dataset.</p>
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<p>The experiment results with different initial training sets. (<b>a</b>) The experiment results with an initial sample size of 500 and a sample selection increment of 1000 on MUDS. (<b>b</b>) The experiment results with an initial sample size of 2000 and a sample selection increment of 1000 on DynamicEarthNet. (<b>c</b>) The experiment results with an initial sample size of 2000 and a sample selection increment of 1000 on PASTIS. (<b>d</b>) The experiment results with an initial sample size of 2000 and a sample selection increment of 1000 on MUDS. (<b>e</b>) The experiment results with an initial sample size of 4000 and a sample selection increment of 1000 on DynamicEarthNet. (<b>f</b>) The experiment results with an initial sample size of 4000 and a sample selection increment of 1000 on PASTIS. (<b>g</b>) The experiment results with an initial sample size of 4000 and a sample selection increment of 1000 on MUDS. (<b>h</b>) The experiment results with an initial sample size of 8000 and a sample selection increment of 1000 on DynamicEarthNet. (<b>i</b>) The experiment results with an initial sample size of 6000 and a sample selection increment of 1000 on PASTIS.</p>
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<p>Ablation results on analyzing the effect of the K-shape and self-attention. (<b>a</b>) The experiment results with an initial sample size of 500 and a sample selection increment of 500 on MUDS. (<b>b</b>) The experiment results with an initial sample size of 2000 and a sample selection increment of 1500 on DynamicEarthNet. (<b>c</b>) The experiment results with an initial sample size of 2000 and a sample selection increment of 1500 on PASTIS.</p>
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23 pages, 4494 KiB  
Review
Conservation Biodiversity in Arid Areas: A Review
by Voichita Timis-Gansac, Lucian Dinca, Cristinel Constandache, Gabriel Murariu, Gabriel Cheregi and Claudia Simona Cleopatra Timofte
Sustainability 2025, 17(6), 2422; https://doi.org/10.3390/su17062422 - 10 Mar 2025
Viewed by 189
Abstract
Drylands cover a vast area, and biodiversity conservation in these regions represents a major challenge. A bibliometric study of published research highlighted several key aspects, including publication types, research fields, years of publication, contributing countries, institutions, languages, journals, publishers, authors, and frequently used [...] Read more.
Drylands cover a vast area, and biodiversity conservation in these regions represents a major challenge. A bibliometric study of published research highlighted several key aspects, including publication types, research fields, years of publication, contributing countries, institutions, languages, journals, publishers, authors, and frequently used keywords. The analysis also included plants related to biodiversity conservation in arid areas, animals related to biodiversity conservation in arid areas, and causes of biodiversity decline in arid regions, effects of biodiversity loss in these regions, and restoration methods aimed at improving biodiversity conservation in arid areas. A total of 947 publications were identified, starting from 1994, authored by researchers from 99 countries, primarily from Australia, the USA, China, Spain, and South Africa, and published in 345 journals, with the most prominent being Journal of Arid Environments, Biodiversity and Conservation, and Biological Conservation. The most commonly appearing keywords included biodiversity, conservation, diversity, vegetation, and patterns, with recent years showing an increased use of terms related to the causes and effects of aridification: climate change, land use, and ecosystem services. The causes of biodiversity loss in drylands are primarily linked to human activities and climatic changes, while the effects impact the entire ecosystem. Methods to improve biodiversity include traditional agroforestry systems, tree plantations and other plant species, grazing management, and other approaches. Combined actions among stakeholders and ecologically appropriate nature-based solutions are also recommended. Improvements in conservation biodiversity in arid areas are very important also for achieving the sustainability goals in these areas. However, numerous aspects of this topic remain to be studied in greater detail. Full article
(This article belongs to the Special Issue Biodiversity, Biologic Conservation and Ecological Sustainability)
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<p>Used methodology.</p>
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<p>(<b>a</b>) The distribution of the main types of publications concerning conservation of biodiversity in arid areas; (<b>b</b>) the distribution of the main research areas of publications used in the bibliometric analysis; (<b>c</b>) the distribution per year of articles concerning conservation of biodiversity in arid areas; (<b>d</b>) countries with authors who contributed to studies on the subject of biodiversity conservation in arid areas.</p>
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<p>Clusters of nations based on the authorship of studies related to conservation and biodiversity in arid areas.</p>
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<p>The primary journals publishing research on conservation of biodiversity in arid areas.</p>
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<p>The distribution of citations and published articles in the Biodiversity and Conservation Journal; (<b>a</b>) histogram of the number of articles by year of publication; (<b>b</b>) histogram of the distribution by year of the number of citations in the WOS Core database; (<b>c</b>) histogram of the distribution by year of the number of citations in all WOS databases; (<b>d</b>) boxplot of the number of citations by year.</p>
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<p>The distribution of citations and published articles in the Journal of Arid Environments; (<b>a</b>) histogram of the number of articles by year of publication; (<b>b</b>) histogram of the distribution by year of the number of citations in the WOS Core database; (<b>c</b>) histogram of the distribution by year of the number of citations in all WOS databases; (<b>d</b>) boxplot of the number of citations by year.</p>
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<p>Authors’ keywords concerning conservation of biodiversity in arid areas.</p>
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<p>Annual distribution of keywords related to conservation of biodiversity in arid areas.</p>
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28 pages, 3732 KiB  
Article
Urban Green Infrastructure Planning in Jaipur, India: A GIS-Based Suitability Model for Semi-Arid Cities
by Ritu Nathawat, Saurabh Kumar Gupta, Shruti Kanga, Suraj Kumar Singh, Shamik Chakraborty, Asif Marazi, Bhartendu Sajan, Mohamed Yehia Abouleish, Gowhar Meraj, Tarig Ali and Pankaj Kumar
Sustainability 2025, 17(6), 2420; https://doi.org/10.3390/su17062420 - 10 Mar 2025
Viewed by 231
Abstract
Urbanization in Jaipur, India, has led to a 42% decline in green cover over the past two decades, exacerbating urban heat, air pollution, groundwater depletion, and reduced livability. Green Infrastructure (GI) offers a sustainable solution, but effective implementation requires robust, data-driven strategies. This [...] Read more.
Urbanization in Jaipur, India, has led to a 42% decline in green cover over the past two decades, exacerbating urban heat, air pollution, groundwater depletion, and reduced livability. Green Infrastructure (GI) offers a sustainable solution, but effective implementation requires robust, data-driven strategies. This study employs geospatial technologies—GIS, remote sensing, and Multi-Criteria Decision Analysis (MCDA)—to develop a suitability model for Urban Green Infrastructure (UGI) planning. Using an entropy-based weighting approach, the model integrates environmental factors, including the Normalized Difference Vegetation Index (NDVI), which fell by 18% between 2000 and 2020; Land Surface Temperature (LST), which increased by 1.8 °C; soil moisture; precipitation; slope; and land use/land cover (LULC). Proximity to water bodies was found to be a critical determinant of suitability, whereas land surface temperature and soil moisture played significant roles in determining UGI feasibility. The results were validated using NDVI trends and comparative analysis with prior studies so as to ensure accuracy and robustness. The suitability analysis reveals that 35% of Jaipur’s urban area, particularly peri-urban regions and river corridors, is highly suitable for UGI interventions, thereby presenting significant opportunities for urban cooling, flood mitigation, and enhanced ecosystem services. These findings align with India’s National Urban Policy Framework (2018) and the UN Sustainable Development Goal 11, supporting climate resilience and sustainable urban development. This geospatial approach provides a scalable methodology for integrating green spaces into urban planning frameworks across rapidly urbanizing cities. Full article
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<p>Location Map of Study Area. Upper left inset shows the location of the Rajasthan state with respect to the Union of India. Left bottom inset shows the location of the Jaipur city with respect to the state of Rajasthan. The right inset shows the boundaries of Jaipur city.</p>
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<p>Flowchart of the complete methodology used in this study.</p>
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<p>Suitability score maps all the input svariables used in this study.</p>
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<p>UGI suitability map of the study area generated used the MCDA framework.</p>
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<p>Relationship between UGI Suitability Index and Soil Moisture.</p>
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<p>Relationship between UGI Suitability Index and LST.</p>
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<p>Graph showing the relation between UGI Suitability Index and Precipitation (R<sup>2</sup> = 11.54%).</p>
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<p>Graph showing the relation between UGI Suitability Index and Air Temperature (R<sup>2</sup> = 23.12%).</p>
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<p>Graph showing the relation between UGI Suitability Index and Water Proximity Score.</p>
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26 pages, 5980 KiB  
Article
Spatiotemporal Analysis of Habitat Quality and Connectivity in Response to Land Use/Cover Change: A Case Study of İzmir
by Nurdan Erdoğan
Sustainability 2025, 17(6), 2407; https://doi.org/10.3390/su17062407 - 10 Mar 2025
Viewed by 152
Abstract
Understanding the impacts of land use/land cover (LULC) changes on ecological processes is essential for addressing biodiversity loss, habitat fragmentation, and climate change. This study analyzes the effects of LULC changes on habitat quality and landscape connectivity in İzmir, Turkey’s third-largest city, using [...] Read more.
Understanding the impacts of land use/land cover (LULC) changes on ecological processes is essential for addressing biodiversity loss, habitat fragmentation, and climate change. This study analyzes the effects of LULC changes on habitat quality and landscape connectivity in İzmir, Turkey’s third-largest city, using the Integrated Valuation of Ecosystem Services and Trade-offs Habitat Quality (InVEST HQ) model, Conefor 2.6 connectivity analysis, and Circuitscape 4.0 resistance-based modeling. This study relies on Coordination of Information on the Environment (CORINE) Land Cover data from 1990 to 2018. Findings indicate that artificial surfaces increased by 82.5% (from 19,418 ha in 1990 to 35,443 ha in 2018), primarily replacing agricultural land (11,721 ha converted). Despite this expansion, high quality habitat areas remained relatively stable, though habitat fragmentation intensified, with the number of patches rising from 469 in 1990 to 606 in 2018, and the average patch size decreasing from 394.31 ha to 297.39 ha. Connectivity analysis highlighted Mount Nif and the Urla–Çeşme–Karaburun Peninsula as critical ecological corridors. However, resistance to movement increased, reducing the likelihood of connectivity-supporting corridors. These findings emphasize the importance of integrating spatial modeling approaches into urban planning and conservation strategies to mitigate future habitat loss and fragmentation. Full article
(This article belongs to the Special Issue Biodiversity Management in Sustainable Landscapes)
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<p>Location of the study area.</p>
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<p>LULC maps of the study area for 1990, 2000, 2006, 2012, and 2018.</p>
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<p>Spatial distribution of habitat quality.</p>
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<p>Graph of Change in Total Area of High-Quality Habitat Patches with Trend Line.</p>
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<p>Spatial distribution of the importance of habitats according to the dIIC index.</p>
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<p>Spatial distribution of the importance of habitats according to the dPC index.</p>
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<p>Current maps generated in Circuitscape 4.0 showing connectivity in 1990 and 2018.</p>
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24 pages, 20633 KiB  
Article
From Conservation to Development: A Study of Land Use and Ecological Changes to Vegetation Around the Hainan Tropical Rainforest National Park
by Huimei Xia, Wei Wang and Zijian Zhang
Sustainability 2025, 17(6), 2403; https://doi.org/10.3390/su17062403 - 10 Mar 2025
Viewed by 201
Abstract
Global ecosystems, particularly in biodiversity-rich tropical rainforests, are increasingly under pressure from human activities. As socio-economic development continues and populations steadily grow, the effective planning of areas surrounding national parks has become a global challenge. This study, based on remote sensing data and [...] Read more.
Global ecosystems, particularly in biodiversity-rich tropical rainforests, are increasingly under pressure from human activities. As socio-economic development continues and populations steadily grow, the effective planning of areas surrounding national parks has become a global challenge. This study, based on remote sensing data and utilizing landscape ecology tools, such as ArcGIS 10.8, GeoDa 1.20, and Fragstats 4.2, combines spatial statistical methods, trend analysis, and the Hurst index to conduct a long-term analysis and forecast future trends in vegetation ecological quality indicators (VEQI) and landscape pattern changes within and around the Hainan Tropical Rainforest National Park. VEQI changes across various buffer zones were also assessed. Our results show that both arable and built-up land increased, especially from 2002 to 2022. Arable land decreased from 5566.8 km2 to 4796.8 km2, then increased to 5904.6 km2; built-up land expanded from 163.97 km2 to 314.59 km2, reflecting urbanization. Spatiotemporal analysis revealed that 42.54% of the study area experienced significant VEQI changes, with a 24.05% increase (mainly in the northwest) and an 18.49% decrease (mainly in the southeast). The VEQI improvements were consistent across all buffer zones, with the most significant growth in the 7.5 km zone. Landscape indices indicated high fragmentation in coastal areas, while inland areas remained stable, reflecting the tension between conservation and urbanization. These findings provide a theoretical basis for future ecological development and buffer zone policies in the park. Full article
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<p>Visualization of the buffer zone of Hainan Tropical Rainforest National Park.</p>
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<p>Research Roadmap.</p>
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<p>Land Use Transition.</p>
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<p>Trend of VEQI changes in the vicinity of Hainan Tropical Rainforest National Park from 2002 to 2022. (<b>a</b>) Spatial distribution of VEQI in the area surrounding Hainan Tropical Rainforest National Park from 2002 to 2022. (<b>b</b>) Spatial distribution of VEQI change trends in the area surrounding Hainan Tropical Rainforest National Park from 2002 to 2022.</p>
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<p>Line plots and bar charts of VEQI changes in the 2.5 km, 5 km, 7.5 km, and 10 km buffer zones around Hainan Tropical Rainforest National Park between 2002 and 2022. (<b>a</b>) Line plots showing VEQI trends, and (<b>b</b>) Bar charts depicting the magnitude of VEQI changes in each buffer zone.</p>
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<p>Spatial distribution patterns and trends of landscape pattern indices around Hainan Tropical Rainforest National Park from 2002 to 2022. (<b>a</b>) Spatial distribution patterns of the Largest Patch Index (LPI) and its trends in the area surrounding Hainan Tropical Rainforest National Park from 2002 to 2022; (<b>b</b>) Spatial distribution patterns of the Contagion Index (CONTAG) and its trends in the area surrounding Hainan Tropical Rainforest National Park from 2002 to 2022; (<b>c</b>) Spatial distribution patterns of Shannon’s Evenness Index (SHEI) and its trends in the area surrounding Hainan Tropical Rainforest National Park from 2002 to 2022; (<b>d</b>) Spatial distribution patterns of Patch Density (PD) and its trends in the area surrounding Hainan Tropical Rainforest National Park from 2002 to 2022; (<b>e</b>) Spatial distribution patterns of the Landscape Shape Index (LSI) and its trends in the area surrounding Hainan Tropical Rainforest National Park from 2002 to 2022.</p>
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<p>Trends in landscape pattern indices within four buffer zones of Hainan Tropical Rainforest National Park from 2002 to 2022. (<b>a</b>) Trend in the Landscape Shape Index (LSI) within the four buffer zones of Hainan Tropical Rainforest National Park from 2002 to 2022; (<b>b</b>) Trend in the Patch Density (PD) within the four buffer zones of Hainan Tropical Rainforest National Park from 2002 to 2022; (<b>c</b>) Trend in the Largest Patch Index (LPI) within the four buffer zones of Hainan Tropical Rainforest National Park from 2002 to 2022; (<b>d</b>) Trend in Shannon’s Evenness Index (SHEI) within the four buffer zones of Hainan Tropical Rainforest National Park from 2002 to 2022; (<b>e</b>) Trend in the Contagion Index (CONTAG) within the four buffer zones of Hainan Tropical Rainforest National Park from 2002 to 2022.</p>
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<p>LISA cluster map of vegetation ecological quality and landscape pattern indices from 2002 to 2022.</p>
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<p>Spatial distribution of VEQI within the buffer zone of Hainan Tropical Rainforest National Park predicted using the Hurst Index model. “Up → Up” indicates that the trend will continue to rise; “Up → Down” indicates that the trend will shift from rising to declining; “Down → Down” indicates that the trend will continue to decline; “Down → Up” indicates that the trend will shift from declining to rising; “<span class="html-italic">p</span> &gt; 0.05” indicates that the change in trend is not statistically significant.</p>
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21 pages, 7896 KiB  
Article
Analyzing Long-Term Land Use/Cover Change (LUCC) and PM10 Levels in Coastal Urbanization: The Crucial Influence of Policy Interventions
by Xue Li, Haihong He, Lizhen Wu, Junfang Chang, Yichen Qin, Chunli Liu, Rui Liu, Mingxin Yao and Wenli Qiao
Sustainability 2025, 17(6), 2393; https://doi.org/10.3390/su17062393 - 9 Mar 2025
Viewed by 235
Abstract
With the rapid acceleration of global urbanization, the impact of land use/cover change (LUCC) on the environment and ecosystems has become increasingly prominent, particularly in terms of air quality, which has emerged as a significant issue demanding attention. Focusing on the coastal city [...] Read more.
With the rapid acceleration of global urbanization, the impact of land use/cover change (LUCC) on the environment and ecosystems has become increasingly prominent, particularly in terms of air quality, which has emerged as a significant issue demanding attention. Focusing on the coastal city of Lianyungang, the spatiotemporal dynamics of land use/cover changes were explored by utilizing land use dynamic degree and land use transfer matrix methods. By integrating a comprehensive historical dataset, multiple linear regression analysis was used to analyze the driving mechanism of land use conversion and to explore the effect of LUCC on the variations in PM10 levels. The results showed an overall decreasing trend in PM10 levels over the 24-year period from 2000 to 2023, with distinct seasonal fluctuations, showing higher concentrations in winter and lower concentrations in summer. The impact of land use on PM10 variations can be categorized into three stages: initial (2000–2006), transitional (2007–2013), and deepening development (2014–2022). Notably, during the third stage, with the involvement of policy interventions and industrial upgrading, a strong negative correlation of −0.97 was identified between urban land expansion and the decrease in PM10 levels. The correlation between LUCC and PM10 levels was insignificant over shorter periods, but the analysis of data from 2000 to 2022 revealed a significant positive correlation of 0.77, emphasizing the importance of adopting a long-term perspective to accurately assess the impact of LUCC on air quality. This research provides valuable insights into the implications of LUCC on air quality during urbanization and establishes a scientific foundation for developing air pollution management strategies in Lianyungang and similar regions. Full article
(This article belongs to the Section Environmental Sustainability and Applications)
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<p>(<b>a</b>) Study area map of Lianyungang City. Terrain elevation (H, unit: meters) is shown in green, with arrows marking Gangcheng Road, Yuntai Mountain, and Mount Huaguoshan; (<b>b</b>) Lianyungang’s location in Jiangsu Province (dark red); (<b>c</b>) Jiangsu Province’s location in China (light red).</p>
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<p>Classification results of land use for Lianyungang in (<b>a</b>) 2000; (<b>b</b>) 2007; (<b>c</b>) 2014; and (<b>d</b>) 2022.</p>
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<p>Variation in land use in Lianyungang from 2000 to 2022. (<b>a</b>) Farmland; (<b>b</b>) forest; (<b>c</b>) grass; (<b>d</b>) water; (<b>e</b>) unused land; (<b>f</b>) urban land.</p>
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<p>Climatological monthly mean variation of PM<sub>10</sub> in Lianyungang City from 2000 to 2023. Gray shadow is the standard deviation.</p>
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<p>Climatological monthly mean spatiotemporal distribution of PM<sub>10</sub> in Lianyungang City from 2000 to 2023 (Unit: μg/m<sup>3</sup>). (<b>a</b>–<b>c</b>) Spring (March, April, May); (<b>d</b>–<b>f</b>) summer (June, July, August); (<b>g</b>–<b>i</b>) autumn (September, October, November); (<b>j</b>–<b>l</b>) winter (December, January, February).</p>
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<p>Analysis of the trend of PM<sub>10</sub> in Lianyungang from 2000 to 2023: (<b>a</b>) time series of monthly average PM<sub>10</sub>; (<b>b</b>) trend (green line) and detected abrupt changepoint (blue line) with the highest probability derived from the BEAST, with the green envelope around the fitted trend signals representing the 95% credible intervals.</p>
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<p>The correlations between land use and PM<sub>10</sub> in the three stages. (<b>a</b>) Farmland; (<b>b</b>) forest; (<b>c</b>) grass; (<b>d</b>) water; (<b>e</b>) unused land; (<b>f</b>) urban land. (Black color for 2000–2006/2000-2013, red color for 2007–2013, blue color for 2014–2022.).</p>
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<p>Sankey diagram of LUCC based on the land use transfer matrix method in different periods.</p>
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<p>The distribution of LUCC in Lianyungang during (<b>a</b>) 2000–2006; (<b>b</b>) 2007–2013; (<b>c</b>) 2017–2022; and (<b>d</b>) 2000–2022.</p>
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<p>Land use dynamic degrees in Lianyungang in different periods. (<b>a</b>) Single dynamic degree; (<b>b</b>) integrated dynamic degree.</p>
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18 pages, 10973 KiB  
Article
Assessing Forest Carbon Sequestration in China Under Multiple Climate Change Mitigation Scenarios
by Mingli Qiu, Yuxin Zhao and Dianfeng Liu
Land 2025, 14(3), 571; https://doi.org/10.3390/land14030571 - 8 Mar 2025
Viewed by 182
Abstract
Understanding how climate policies impact forest carbon sequestration is crucial for optimizing mitigation strategies. This study evaluated forest carbon sequestration in China from 2020 to 2060 under three climate scenarios: SSP1-2.6 (high mitigation), SSP3-7.0 (limited mitigation), and SSP5-8.5 (no mitigation). We integrated the [...] Read more.
Understanding how climate policies impact forest carbon sequestration is crucial for optimizing mitigation strategies. This study evaluated forest carbon sequestration in China from 2020 to 2060 under three climate scenarios: SSP1-2.6 (high mitigation), SSP3-7.0 (limited mitigation), and SSP5-8.5 (no mitigation). We integrated the land-use harmonization (LUH2) and patch-generating land-use simulation (PLUS) models to project forest cover change, and the Lund–Potsdam–Jena managed land (LPJmL) model to simulate carbon dynamics. The results showed stronger mitigation efforts led to higher sequestration, with annual rates of 0.49, 0.48, and 0.20 Pg yr−1 across the scenarios. SSP1-2.6 achieved the highest carbon density (17.75 kg m−2) and sequestration (56.95 Pg), driven by the greatest increases in the carbon density of existing forests (+41.56%) and soil carbon (+39.94%). SSP3-7.0, despite the highest forest cover (34.74%), had a lower carbon density (17.19 kg m−2) and sequestration (56.84 Pg). SSP5-8.5 recorded the lowest forest cover (27.12%) and sequestration (45.62 Pg). Increasing carbon density, rather than expanding forest area, could be more effective for carbon sequestration in China. The carbon density and annual sequestration in existing forests were 2.36 and 2.89 times higher than in new forests. We recommend prioritizing SSP1-2.6 to maximize sequestration, focusing on protecting southwest forests and soil carbon. Full article
(This article belongs to the Section Land, Biodiversity, and Human Wellbeing)
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<p>Analytical framework of forest carbon sequestration assessment under climate change mitigation scenarios.</p>
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<p>Change in forest area (FA) from 2020 to 2060. (<b>a</b>) FA in China from 2020 to 2060; (<b>b</b>) FA change in China from 2020 to 2060; and (<b>c</b>) FA in the areas with forest cover change under different scenarios.</p>
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<p>Change in carbon density (CD) from 2020 to 2060. (<b>a</b>) CD in China’s forest from 2020 to 2060; (<b>b</b>) CD change in China’s forest from 2020 to 2060; and (<b>c</b>) CD in the areas with forest cover change under different scenarios.</p>
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<p>Change in carbon sequestration (CS) from 2020 to 2060. (<b>a</b>) CS in China’s forest from 2020 to 2060; (<b>b</b>) CS change in China’s forest from 2020 to 2060; and (<b>c</b>) CS change in the areas with forest cover change under different scenarios.</p>
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<p>Spatial patterns of forest cover change in China from 2020 to 2060 under different scenarios: (<b>a</b>) SSP1-2.6; (<b>b</b>) SSP3-7.0; and (<b>c</b>) SSP5-8.5 (① = northeastern China, ② = northern China, ③ = eastern China, ④ = southern China, ⑤ = northwestern China, and ⑥ = southwestern China).</p>
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<p>Forest carbon density in 2060 under different scenarios: (<b>a</b>) SSP1-2.6; (<b>b</b>) SSP3-7.0; and (<b>c</b>) SSP5-8.5 (① = northeastern China, ② = northern China, ③ = eastern China, ④ = southern China, ⑤ = northwestern China, and ⑥ = southwestern China).</p>
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<p>Annual sequestration rate of China’s forest from 2020 to 2060 under different scenarios: (<b>a</b>) SSP1-2.6; (<b>b</b>) SSP3-7.0; and (<b>c</b>) SSP5-8.5 (① = northeastern China, ② = northern China, ③ = eastern China, ④ = southern China, ⑤ = northwestern China, and ⑥ = southwestern China).</p>
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17 pages, 7122 KiB  
Article
Multi-Temporal and Multi-Resolution RGB UAV Surveys for Cost-Efficient Tree Species Mapping in an Afforestation Project
by Saif Ullah, Osman Ilniyaz, Anwar Eziz, Sami Ullah, Gift Donu Fidelis, Madeeha Kiran, Hossein Azadi, Toqeer Ahmed, Mohammed S. Elfleet and Alishir Kurban
Remote Sens. 2025, 17(6), 949; https://doi.org/10.3390/rs17060949 - 7 Mar 2025
Viewed by 467
Abstract
Accurate, cost-efficient vegetation mapping is critical for managing afforestation projects, particularly in resource-limited areas. This study used a consumer-grade RGB unmanned aerial vehicle (UAV) to evaluate the optimal spatial and temporal resolutions (leaf-off and leaf-on) for precise, economically viable tree species mapping. This [...] Read more.
Accurate, cost-efficient vegetation mapping is critical for managing afforestation projects, particularly in resource-limited areas. This study used a consumer-grade RGB unmanned aerial vehicle (UAV) to evaluate the optimal spatial and temporal resolutions (leaf-off and leaf-on) for precise, economically viable tree species mapping. This study conducted in 2024 in Kasho, Bannu district, Pakistan, using UAV missions at multiple altitudes captured high-resolution RGB imagery (2, 4, and 6 cm) across three sampling plots. A Support Vector Machine (SVM) classifier with 5-fold cross-validation was assessed using accuracy, Shannon entropy, and cost–benefit analyses. The results showed that the 6 cm resolution achieved a reliable accuracy (R2 = 0.92–0.98) with broader coverage (12.3–22.2 hectares), while the 2 cm and 4 cm resolutions offered higher accuracy (R2 = 0.96–0.99) but limited coverage (4.8–14.2 hectares). The 6 cm resolution also yielded the highest benefit–cost ratio (BCR: 0.011–0.015), balancing cost-efficiency and accuracy. This study demonstrates the potential of consumer-grade UAVs for affordable, high-precision tree species mapping, while also accounting for other land cover types such as bare earth and water, supporting budget-constrained afforestation efforts. Full article
(This article belongs to the Section Forest Remote Sensing)
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<p>The map shows the geographical location of the study area in the Kasho region. RGB UAV images at three resolutions have been captured for a selected sample plot—yellow, which is one of three distinct sample plots for this study—with black rectangles marking the targeted vegetation area used for comparative analysis.</p>
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<p>Comparison of leaf-off and leaf-on orthoimages for three sample plots (1–3), highlighting seasonal transitions in vegetation classes—from exposed soil and understory in leaf-off to dense canopy coverage in leaf-on images, where red outlines the study area boundary, yellow marks all sample plots, and light blue highlights the selected sample plots for this study.</p>
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<p>Workflow for precise vegetation mapping and benefit–cost ratio (BCR) analysis.</p>
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<p>Total time and area coverage efficiency across different resolutions, with median, and standard deviation indicated via error bars.</p>
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<p>Bar graphs showing the area distribution of vegetation classes across different resolutions (2, 4, and 6 cm) in leaf-on and leaf-off conditions.</p>
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<p>Precise mapping of vegetation and non-vegetation classes where W = water, BL = barren land, EC = <span class="html-italic">Eucalyptus camaldulensis</span>, PJ = <span class="html-italic">Prosopis juliflora</span>, AA = <span class="html-italic">Ammophila arenaria</span>, and JA = <span class="html-italic">Juncus acutus</span>.</p>
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<p>Pearson correlation between accuracy, class coverage, and entropy gain/loss across resolutions, where the shape of the points denotes the sample plot number, and the color of the crosses indicates the resolution of the corresponding sample plot.</p>
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<p>SHAP summary plot of feature contributions to BCR in UAV-based vegetation mapping.</p>
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<p>Effect of resolution and seasonal condition on BCR, analyzed by two-way ANOVA, highlighting a significant impact of resolution compared to the effect of condition. (α = 0.005).</p>
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29 pages, 6438 KiB  
Article
Potato Cultivation Under Zero Tillage and Straw Mulching: Option for Land and Cropping System Intensification for Indian Sundarbans
by Saikat Dey, Sukamal Sarkar, Anannya Dhar, Koushik Brahmachari, Argha Ghosh, Rupak Goswami and Mohammed Mainuddin
Land 2025, 14(3), 563; https://doi.org/10.3390/land14030563 - 7 Mar 2025
Viewed by 148
Abstract
Agriculture in the Indian Sundarbans deltaic region primarily depends on a rice-based monocropping system during the rainy season, with the subsequent season often remaining fallow. To mitigate this issue, a series of experiments using zero tillage and straw mulching (ZTSM) potato cultivation were [...] Read more.
Agriculture in the Indian Sundarbans deltaic region primarily depends on a rice-based monocropping system during the rainy season, with the subsequent season often remaining fallow. To mitigate this issue, a series of experiments using zero tillage and straw mulching (ZTSM) potato cultivation were conducted over eight consecutive years (2017–2024) across various islands in the Sundarbans Delta, West Bengal, aimed to intensify the cropping system and ensure the betterment of the land use pattern using climate-smart agricultural practices. In the initial two years, the experiments concentrated on assessing different potato cultivars and nutrient dosages under zero tillage and paddy straw mulching conditions. During the subsequent years, the focus shifted to field demonstrations under diverse climatic conditions. The research included the application of different macronutrients and growth regulators, in combination with different depths of straw mulching. In the final years of the study, the intervention was dedicated solely to the horizontal expansion of cultivated land. These initiatives aimed to enhance agricultural productivity and sustainable land use in the polders, promoting climate-resilient farming practices. From the sets of experiments, we standardized the sustainable nutrient management strategies and selection of appropriate potato cultivars vis-à-vis depth of straw mulching and, finally, the overall best agronomic practices for the region. The adoption of the ZTSM potato cultivation system demonstrated considerable success, as evidenced by the remarkable increase in the number of farmers employing this sustainable agricultural practice. The number of farmers practicing zero tillage potato cultivation surged from 23 in the initial year to over 1100, covering an area of more than 15 ha, highlighting the effectiveness of the technology. The analysis of the estimated adoption also showed that more than 90% adoption is likely to be achieved within a decade. This potential expansion underscores the benefits of the ZTSM potato cultivation system in improving soil health, conserving water, and reducing labour and costs. As more farmers recognize the advantages of zero tillage potato mulching, this approach is poised to play a pivotal role in sustainable agriculture, enhancing productivity while promoting environmental stewardship. Full article
(This article belongs to the Special Issue Tillage Methods on Soil Properties and Crop Growth)
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<p>Working principle of zero-tillage potato cultivation with paddy straw mulching (image created with <a href="https://BioRender.com" target="_blank">https://BioRender.com</a>; license no: BE27A0036T, accessed on 7 September 2024).</p>
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<p>(<b>a</b>) Plant height (cm); (<b>b</b>) the number of main branches/plants; (<b>c</b>) plant dry weight/plant, and (<b>d</b>) tuber dry weights/plants of different varieties of potatoes under ZTSM condition (where V1 = <span class="html-italic">K. chandramukhi</span>, V2 = <span class="html-italic">K. jyoti</span>, V3 = <span class="html-italic">S-52</span>, V4 = S6, and V5 = local).</p>
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<p>Effect of foliar nutrient management on (<b>a</b>) plant height, (<b>b</b>) number of compound leaves/plant, (<b>c</b>) leaf area index, and (<b>d</b>) total biomass per plant of ZTSM system of potato (T1: Control; T2: RDF<sub>NPK</sub> fb Urea 2% fs <sub>30 DAP</sub>; T3: RDF<sub>NPK</sub> fb Urea 2% fs <sub>30 &amp; 50 DAP</sub>; T4: RDF<sub>NPK</sub> fb MOP 2% fs <sub>30 DAP</sub>; T5: RDF<sub>NPK</sub> fb Urea 2% fs <sub>30 &amp; 50 DAP</sub> + MOP 2% fs <sub>30 DAP</sub>; T6: RDF<sub>NPK</sub> fb Boron 0.1% fs <sub>30 DAP</sub>; T7: RDF<sub>NPK</sub> fb Urea 2% fs <sub>30 &amp; 50 DAP</sub> + Boron 0.1% fs <sub>30 DAP</sub>; T8: RDF<sub>NPK</sub> fb Zinc 0.5% fs <sub>30 DAP</sub>; T9: RDF<sub>NPK</sub> fb Urea 2% fs <sub>30 &amp; 50 DAP</sub> + Zinc 0.5% fs <sub>30 DAP</sub>).</p>
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<p>Effects of biostimulants on (<b>a</b>) plant height; (<b>b</b>) number of compound leaves/plant; (<b>c</b>) leaf area index; and (<b>d</b>) total biomass/plant of ZTSM potato (where T1: Control, T2: RDF<sub>NPK</sub> fb <span class="html-italic">Sargassum</span> 5% fs <sub>30 DAP</sub>; T3: RDF<sub>NPK</sub> fb Sargassum 5% fs <sub>30 DAP &amp; 50 DAP</sub>; T4: RDF<sub>NPK</sub> fb Sargassum + humic acid 5% fs <sub>30 DAP</sub>; T5: RDF<sub>NPK</sub> fb Sargassum + humic acid 5% fs <sub>30 DAP &amp; 50 DAP</sub>; T6: RDF<sub>NPK</sub> fb Triacontanol 0.05% fs <sub>30 DAP</sub>; T7: RDF<sub>NPK</sub> fb Triacontanol 0.05% fs <sub>30 DAP &amp; 50 DAP</sub>; T8: Water).</p>
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<p>Effects of foliar nutrient and growth regulators on (<b>a</b>) plant height; (<b>b</b>) the number of compound leaves; (<b>c</b>) leaf area index; and (<b>d</b>) total biomass/plant (where T1: Water Spray; T2: 2% DAP at 30 DAP; T3: 2% DAP at 30 And 50 DAP; T4: 2% MOP at 30 DAP; T5: 2% MOP at 30 and 50 DAP; T6: 2% DAP and 2% MOP at 30 DAP; T7: 2% DAP and 2% MOP At 30 and 50 DAP; T8: 2% DAP + 2% MOP + 0.1% Triacontanol 0.05% EC (Miraculan) at 30 and 50 DAP).</p>
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<p>Effect of foliar nutrient management on (<b>a</b>) tuber hardness; (<b>b</b>) specific gravity; (<b>c</b>) pH; (<b>d</b>) vitamin C; (<b>e</b>) TSS; and (<b>f</b>) acidity of potatoes. T1: Control; T2: RDF<sub>NPK</sub> fb Urea 2% fs <sub>30 DAP</sub>; T3: RDF<sub>NPK</sub> fb Urea 2% fs <sub>30 &amp; 50 DAP</sub>; T4: RDF<sub>NPK</sub> fb MOP 2% fs <sub>30 DAP</sub>; T5: RDF<sub>NPK</sub> fb Urea 2% fs <sub>30 &amp; 50 DAP</sub> + MOP 2% fs <sub>30 DAP</sub>; T6: RDF<sub>NPK</sub> fb Boron 0.1% fs <sub>30 DAP</sub>; T7: RDF<sub>NPK</sub> fb Urea 2% fs <sub>30 &amp; 50 DAP</sub> + Boron 0.1% fs <sub>30 DAP</sub>; T8: RDF<sub>NPK</sub> fb Zinc 0.5% fs <sub>30 DAP</sub>; T9: RDF<sub>NPK</sub> fb Urea 2% fs <sub>30 &amp; 50 DAP</sub> + Zinc 0.5% fs <sub>30 DAP</sub>.</p>
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<p>Effect of biostimulants on (<b>a</b>) acidity; (<b>b</b>) tuber hardness; (<b>c</b>) specific gravity; (<b>d</b>) pH; (<b>e</b>) vitamin C; (<b>f</b>) TSS of potatoes (where T1: Control, T2: RDF<sub>NPK</sub> fb Sargassum 5% fs <sub>30 DAP</sub>; T3: RDF<sub>NPK</sub> fb Sargassum 5% fs <sub>30 DAP &amp; 50 DAP</sub>; T4: RDF<sub>NPK</sub> fb Sargassum + humic acid 5% fs <sub>30 DAP</sub>; T5: RDF<sub>NPK</sub> fb Sargassum + humic acid 5% fs <sub>30 DAP &amp; 50 DAP</sub>; T6: RDF<sub>NPK</sub> fb Triacontanol 0.05% fs <sub>30 DAP</sub>; T7: RDF<sub>NPK</sub> fb Triacontanol 0.05% fs <sub>30 DAP &amp; 50 DAP</sub>; T8: Water).</p>
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<p>Effect of foliar nutrient and growth regulators on (<b>a</b>) tuber hardness; (<b>b</b>) specific gravity; (<b>c</b>) pH (<b>d</b>) vitamin C; (<b>e</b>) TSS; (<b>f</b>) pH of potatoes (where, T1: Water Spray; T2: 2% DAP at 30 DAP; T3: 2% DAP at 30 And 50 DAP; T4: 2% MOP at 30 DAP; T5: 2% MOP at 30 and 50 DAP; T6: 2% DAP and 2% MOP at 30 DAP; T7: 2% DAP and 2% MOP At 30 and 50 DAP; T8: 2% DAP + 2% MOP + 0.1% Triacontanol 0.05% EC (Miraculan) at 30 and 50 DAP).</p>
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<p>Comparison of soil moisture (%) between (<b>a</b>) zero-tilled–mulched potato fields and adjacent (<b>b</b>) fallow rice fields (vertical bars indicate the standard deviation of the mean).</p>
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<p>Comparison of soil salinity between (<b>a</b>) zero-tilled–mulched potato fields and adjacent (<b>b</b>) fallow rice fields (vertical bars indicate the standard deviation of the mean).</p>
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<p>Location and spatial distribution of ZTSM potato field across the various experimental sites of Indian Sundarbans (Site-I: Rangabelia, Site-II: Choto Mollakhali, and Site-III: Satjelia).</p>
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<p>Probability of exceedance (0–1) of potato tuber yield (kg/ha) across different locations in (<b>a</b>) <span class="html-italic">Rabi</span>, 2022, and (<b>b</b>) <span class="html-italic">Rabi</span>, 2023.</p>
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<p>Peak adoption level (%) and peak time to adoption (year) for zero tillage and straw mulching (ZTSM) potato cultivation for three scenarios. Scenarios are defined by the perceived “step-up” and “step-down” options of the ADOPT model. The figures on the right of the dotted vertical line suggest the likely rate of adoption in the first five years.</p>
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23 pages, 7629 KiB  
Article
Humans, Climate Change, or Both Causing Land-Use Change? An Assessment with NASA’s SEDAC Datasets, GIS, and Remote Sensing Techniques
by Alen Raad and Joseph D. White
Urban Sci. 2025, 9(3), 76; https://doi.org/10.3390/urbansci9030076 - 7 Mar 2025
Viewed by 174
Abstract
Land-Cover and Land-Use Change (LCLUC) is a dynamic process affected by the combination and mutual interaction of climatic and socioeconomic drivers. Field studies and surveys, which are typically time- and resource-consuming, have been employed by researchers to better understand LCLUC drivers. However, remotely [...] Read more.
Land-Cover and Land-Use Change (LCLUC) is a dynamic process affected by the combination and mutual interaction of climatic and socioeconomic drivers. Field studies and surveys, which are typically time- and resource-consuming, have been employed by researchers to better understand LCLUC drivers. However, remotely sensed data may provide the same trustworthy outcomes with less time and expense. This study aimed to assess the relationship between LCLUC and changes in socioeconomic and climatic factors in the Dallas-Fort Worth (DFW) metropolitan area, Texas, USA, between 2000 and 2020. The LCLU, socioeconomic, and climatic data were obtained from the National Land Cover Database of Multi-Resolution Land Characteristics Consortium, NASA’s Socioeconomic Data and Applications Center (SEDAC), and the global climate and weather data website (WorldClim), respectively. Change detection calculated from these data was used to analyze spatial and statistical relationships between LCLUC and changes in socioeconomic and climatic factors. Results showed that LCLUC was significantly predicted by population change, housing and transportation, household and disability change, socioeconomic status change, monthly average minimum temperature change, and monthly mean precipitation change. While socioeconomic factors played a predominant role in driving LCLUC in this study, the influence of climatic factors should not be overlooked, particularly in regions where climate sensitivity is more pronounced, such as arid or transitional zones. These findings highlight the importance of considering regional variability when assessing LCLUC drivers. Full article
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<p>Location of the study area.</p>
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<p>Maps of NLCD LCLU classes for the DFW metroplex in 2001 and 2019.</p>
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<p>Mapped distribution of NLCD LCLUC (gain) by LULC class within the DFW metroplex study area from 2001 to 2019.</p>
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<p>Mapped distribution of NLCD LCLUC (loss) by LULC class within the DFW metroplex study area from 2001 to 2019.</p>
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<p>Population count (number of persons per km<sup>2</sup>) for the DFW metroplex study area in 2000 (<b>left</b>) and 2020 (<b>right</b>) derived from SEDAC datasets.</p>
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<p>Housing and transportation index values for the DFW metroplex study area in 2000 (<b>left</b>) and 2018 (<b>right</b>), derived from SEDAC datasets.</p>
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<p>Mapped household and disability index values for the DFW metroplex study area in 2000 (<b>left</b>) and 2018 (<b>right</b>) derived from SEDAC datasets.</p>
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<p>Mapped socioeconomic status index values for the DFW metroplex study area in 2000 (<b>left</b>) and 2018 (<b>right</b>) derived from SEDAC datasets.</p>
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<p>Mapped overall SVI values for the DFW metroplex study area in 2000 (<b>left</b>) and 2018 (<b>right</b>) derived from SEDAC datasets.</p>
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<p>Mapped monthly mean precipitation (mm) values for the DFW metroplex study area in 2001 (<b>left</b>) and 2018 (<b>right</b>) derived from WorldClim datasets.</p>
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<p>Mapped monthly average maximum temperature (°C) values for the DFW metroplex study area in 2001 (<b>left</b>) and 2018 (<b>right</b>) derived from WorldClim datasets.</p>
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<p>Mapped monthly average minimum temperature (°C) values for the DFW metroplex study area in 2001 (<b>left</b>) and 2018 (<b>right</b>) derived from WorldClim datasets.</p>
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