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Search Results (1,253)

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23 pages, 3871 KiB  
Article
Direct Distillation: A Novel Approach for Efficient Diffusion Model Inference
by Zilai Li and Rongkai Zhang
J. Imaging 2025, 11(2), 66; https://doi.org/10.3390/jimaging11020066 - 19 Feb 2025
Abstract
Diffusion models are among the most common techniques used for image generation, having achieved state-of-the-art performance by implementing auto-regressive algorithms. However, multi-step inference processes are typically slow and require extensive computational resources. To address this issue, we propose the use of an information [...] Read more.
Diffusion models are among the most common techniques used for image generation, having achieved state-of-the-art performance by implementing auto-regressive algorithms. However, multi-step inference processes are typically slow and require extensive computational resources. To address this issue, we propose the use of an information bottleneck to reschedule inference using a new sampling strategy, which employs a lightweight distilled neural network to map intermediate stages to the final output. This approach reduces the number of iterations and FLOPS required for inference while ensuring the diversity of generated images. A series of validation experiments were conducted involving the COCO dataset as well as the LAION dataset and two proposed distillation models, requiring 57.5 million and 13.5 million parameters, respectively. Results showed that these models were able to bypass 40–50% of the inference steps originally required by a stable U-Net diffusion model, which included 859 million parameters. In the original sampling process, each inference step required 67,749 million multiply–accumulate operations (MACs), while our two distillate models only required 3954 million MACs and 3922 million MACs per inference step. In addition, our distillation algorithm produced a Fréchet inception distance (FID) of 16.75 in eight steps, which was remarkably lower than those of the progressive distillation, adversarial distillation, and DDIM solver algorithms, which produced FID values of 21.0, 30.0, 22.3, and 24.0, respectively. Notably, this process did not require parameters from the original diffusion model to establish a new distillation model prior to training. Information theory was used to further analyze primary bottlenecks in the FID results of existing distillation algorithms, demonstrating that both GANs and typical distillation failed to achieve generative diversity while implicitly studying incorrect posterior probability distributions. Meanwhile, we use information theory to analyze the latest distillation models including LCM-SDXL, SDXL-Turbo, SDXL-Lightning, DMD, and MSD, which reveals the basic reason for the diversity problem confronted by them, and compare those distillation models with our algorithm in the FID and CLIP Score. Full article
(This article belongs to the Section AI in Imaging)
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<p>The time schedule proposed by the improved DDPM.</p>
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<p>A conventional linear time schedule.</p>
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<p>Various time steps in the time schedule developed by Karras and a linear time schedule.</p>
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<p>Variance between the proposed schedule and the Karras schedule.</p>
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<p>The underlying concepts of direct distillation, in which the orange line denotes the proposed distillation process, the blue line represents progressive distillation, and the black line denotes the normal diffusion process. The <math display="inline"><semantics> <mrow> <msub> <mi>p</mi> <mi>θ</mi> </msub> <mrow> <mo>(</mo> </mrow> <msub> <mi>x</mi> <mrow> <mi>t</mi> <mo>−</mo> <mn>1</mn> </mrow> </msub> <mrow> <mo>|</mo> <msub> <mi>x</mi> <mi>t</mi> </msub> <mo>)</mo> </mrow> </mrow> </semantics></math> term models the reverse process, while <math display="inline"><semantics> <mrow> <mi>q</mi> <mo>(</mo> <msub> <mi>x</mi> <mi>t</mi> </msub> <mrow> <mo>|</mo> <msub> <mi>x</mi> <mrow> <mi>t</mi> <mo>−</mo> <mn>1</mn> </mrow> </msub> <mo>)</mo> </mrow> </mrow> </semantics></math> models the forward process.</p>
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<p>Output images from the original stable diffusion and our novel distillation algorithm.</p>
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<p>The comparison between direct distillation and adversarial progressive distillation in the standards of Precision and Recall for distributions.</p>
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<p>Output images from conventional stable diffusion and novel distillation algorithms.</p>
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<p>Output images from the original stable diffusion model and our novel distillation algorithm.</p>
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<p>Output images from the original stable diffusion model and our novel distillation algorithm.</p>
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<p>Output images from the original stable diffusion model and our novel distillation algorithm.</p>
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14 pages, 1607 KiB  
Article
Global NDVI-LST Correlation: Temporal and Spatial Patterns from 2000 to 2024
by Ehsan Rahimi, Pinliang Dong and Chuleui Jung
Environments 2025, 12(2), 67; https://doi.org/10.3390/environments12020067 - 17 Feb 2025
Viewed by 84
Abstract
While numerous studies have investigated the NDVI-LST relationship at local or regional scales, existing global analyses are outdated and fail to incorporate recent environmental changes driven by climate change and human activity. This study aims to address this gap by conducting an extensive [...] Read more.
While numerous studies have investigated the NDVI-LST relationship at local or regional scales, existing global analyses are outdated and fail to incorporate recent environmental changes driven by climate change and human activity. This study aims to address this gap by conducting an extensive global analysis of NDVI-LST correlations from 2000 to 2024, utilizing multi-source satellite data to assess latitudinal and ecosystem-specific variability. The MODIS dataset, which provides global daily LST data at a 1 km resolution from 2000 to 2024, was used alongside MODIS-derived NDVI data, which offers global vegetation indices at a 1 km resolution and 16-day temporal intervals. A correlation analysis was performed by extracting NDVI and LST values for each raster cell. The analysis revealed significant negative correlations in regions such as the western United States, Brazil, southern Africa, and northern Australia, where increased temperatures suppress vegetation activity. A total of 38,281,647 pixels, or 20% of the global map, exhibited statistically significant correlations, with 80.4% showing negative correlations, indicating a reduction in vegetation activity as temperatures rise. The latitudinal distribution of significant correlations revealed two prominent peaks: one in the tropical and subtropical regions of the Southern Hemisphere and another in the temperate zones of the Northern Hemisphere. This study uncovers notable spatial and latitudinal patterns in the LST-NDVI relationship, with most regions exhibiting negative correlations, underscoring the cooling effects of vegetation. These findings emphasize the crucial role of vegetation in regulating surface temperatures, providing valuable insights into ecosystem health, and informing conservation strategies in response to climate change. Full article
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<p>Correlation map of LST-NDVI in six classes (<b>a</b>), and significant and non-significant pixels (<b>b</b>).</p>
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<p>Latitudinal distribution of significant correlations (<b>a</b>), and proportions of positive and negative significant correlations (<b>b</b>).</p>
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28 pages, 12327 KiB  
Article
Global Dynamic Landslide Susceptibility Modeling Based on ResNet18: Revealing Large-Scale Landslide Hazard Evolution Trends in China
by Hui Jiang, Mingtao Ding, Liangzhi Li and Wubiao Huang
Appl. Sci. 2025, 15(4), 2038; https://doi.org/10.3390/app15042038 - 15 Feb 2025
Viewed by 236
Abstract
Large-scale and long-term landslide susceptibility assessments are crucial for revealing the patterns of landslide risk variation and for guiding the formulation of disaster prevention and mitigation policies at the national level. This study, through the establishment of a global dynamic landslide susceptibility model, [...] Read more.
Large-scale and long-term landslide susceptibility assessments are crucial for revealing the patterns of landslide risk variation and for guiding the formulation of disaster prevention and mitigation policies at the national level. This study, through the establishment of a global dynamic landslide susceptibility model, uses the multi-dimensional analysis strategy and studies the development trend of China’s large-scale landslide susceptibility. First, a global landslide dataset consisting of 8023 large-scale landslide events triggered by rainfall and earthquakes between 2001 and 2020 was constructed based on the GEE (Google Earth Engine) platform. Secondly, a global dynamic landslide susceptibility model was developed using the ResNet18 (18-layer residual neural network) DL (deep learning) framework, incorporating both dynamic and static LCFs (landslide conditioning factors). The model was utilized to generate sequential large-scale landslide susceptibility maps for China from 2001 to 2022. Finally, the MK (Mann–Kendall) test was used to investigate the change trends in the large-scale landslide susceptibility of China. The results of the study are as follows. (1) The ResNet18 model outperformed SVMs (support vector machines) and CNNs (convolutional neural networks), with an AUC value of 0.9362. (2) SHAP (Shapley Additive Explanations) analyses revealed that precipitation played an important factor in the occurrence of landslides in China. In addition, profile curvature, NDVI, and distance to faults are thought to have a significant impact on landslide susceptibility. (3) The large-scale landslide susceptibility trends in China are complex and varied. Particular emphasis should be placed on Southwest China, including Chongqing, Guizhou, and Sichuan, which exhibit high landslide susceptibility and notable upward trends, and also consider Northwest China, including Shaanxi and Shanxi, which have high susceptibility but decreasing trends. These results provide valuable insights for disaster prevention and mitigation in China. Full article
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<p>Geomorphological zoning in China.</p>
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<p>Global landslide distribution.</p>
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<p>Dynamic landslide susceptibility evaluation process.</p>
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<p>The network architecture. (<b>a</b>) The CNN network architecture, (<b>b</b>) the residual unit, and (<b>c</b>) the ResNet18 network architecture.</p>
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<p>The <span class="html-italic">PCC</span> calculation results of condition factors. (Areas in the red box represent correlations between static factors, areas in the yellow box represent correlations between dynamic factors, and other areas represent correlations between dynamic and static factors.)</p>
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<p>The <span class="html-italic">MI</span> calculation results of condition factors.</p>
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<p>Spatial distribution of precipitation, NDVI, and land cover types (<b>a</b>,<b>c</b>,<b>e</b>) and their change trends test (<b>b</b>,<b>d</b>,<b>f</b>) during 2001–2022.</p>
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<p>ROC curve and accuracy evaluation of test data.</p>
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<p>Percentage area distribution of landslide susceptibility zones from 2001 to 2022.</p>
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<p>Spatial distribution of LSM (<b>a</b>) and spatial change trend test landslide susceptibility (<b>b</b>) from 2001 to 2022.</p>
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<p>Temporal of landslide susceptibility in typical regions of China, 2001–2022 (red solid line is linear regression, the blue circle is the predicted probability of landslide in the corresponding year).</p>
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<p>Ranking of feature importance based on SHAP method (<b>a</b>) and summary plot (<b>b</b>).</p>
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<p>Test and comparison of local datasets across various models: (<b>a</b>) SVM, (<b>b</b>) CNN, and (<b>c</b>) ResNet18.</p>
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<p>Comparison analysis of landslide susceptibility maps from previous studies. (<b>a</b>) Landslide hazard map developed by Liu [<a href="#B29-applsci-15-02038" class="html-bibr">29</a>]. (<b>b</b>) LSM prepared by Wang [<a href="#B31-applsci-15-02038" class="html-bibr">31</a>]. (<b>c</b>) LSM for 2017 based on the ResNet18 from this study. (<b>d</b>) LSM for 2020 based on the ResNet18 from this study.</p>
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16 pages, 4994 KiB  
Article
High-Resolution Mapping of Shallow Water Bathymetry Based on the Scale-Invariant Effect Using Sentinel-2 and GF-1 Satellite Remote Sensing Data
by Jiada Guan, Huaguo Zhang, Tong Han, Wenting Cao, Juan Wang and Dongling Li
Remote Sens. 2025, 17(4), 640; https://doi.org/10.3390/rs17040640 - 13 Feb 2025
Viewed by 287
Abstract
High-resolution water depth data are of great significance in island research and coastal ecosystem monitoring. However, the acquisition of high-resolution imagery has been a challenge due to the difficulties and high costs associated with obtaining such data. To address this issue, this study [...] Read more.
High-resolution water depth data are of great significance in island research and coastal ecosystem monitoring. However, the acquisition of high-resolution imagery has been a challenge due to the difficulties and high costs associated with obtaining such data. To address this issue, this study proposes a water depth inversion method based on Gaofen-1 (GF-1) satellite data, which integrates multi-source satellite data to obtain high-resolution bathymetric data. Specifically, the research utilizes bathymetric data derived from Sentinel-2 and Ice, Cloud, and Land Elevation Satellite-2 (ICESat-2) as prior information, combined with high-resolution imagery obtained from the GF-1 satellite constellation (GF-1B/C/D). Then, it employs a scale-invariant effect to map bathymetry with a spatial resolution of 2 m, applied to four study areas in the Pacific Islands. The results are further evaluated using ICESat-2 data, which demonstrate that the water depth inversion results from this study possess high accuracy, with R2 values exceeding 0.85, root mean square error (RMSE) ranging from 0.56 to 0.90 m, with an average of 0.7125 m, and mean absolute error (MAE) ranging from 0.43 to 0.76 m, with an average of 0.55 m. Additionally, this paper discusses the applicability of the scale-invariant assumption in this research and the improvements of the quadratic polynomial ratio model (QPRM) method compared to the classical linear ratio model (CLRM) method. The findings indicate that the integration of multi-source satellite remote sensing data based on the scale-invariant effect can effectively obtain high-precision, high-resolution bathymetric data, providing significant reference value for the application of GF-1 satellites in high-resolution bathymetry mapping. Full article
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<p>Distribution map of the four study areas, where the red solid line indicates the orbit of the ICESat-2 satellite.</p>
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<p>Workflow diagram of the bathymetric mapping.</p>
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<p>Complete bathymetric mapping results based on Sentinel-2 and GF-1 inversions for the four study areas (<b>top</b>), detailed bathymetric results for localized areas (<b>middle</b>), and original imagery (<b>bottom</b>); the black boxes indicate the specific location of the localized results on the complete island and the solid black lines indicate the location of the profiles used for analysis in <a href="#remotesensing-17-00640-f004" class="html-fig">Figure 4</a>.</p>
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<p>Scatterplot comparison of profiles in the four study areas: (<b>a</b>) Onotoa Island; (<b>b</b>) Ant Atoll; (<b>c</b>) Emae Island; (<b>d</b>) Vuthovutho Island.</p>
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<p>Comparison results of bathymetric data obtained from inversion with ICESat-2 data in the four islands, where the red dashed line is the 1:1 line, the blue dashed line is the fitted line, and N is the number of data points from ICESat-2 used for validation.</p>
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<p>Comparison of the bathymetric data results obtained from GF-1 data and from Sentinel-2 data, where the red dashed line represents the 1:1 line and the blue dashed line indicates the fitted line.</p>
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<p>The location of profiles selected on each island used for discussing the scale-invariant assumption in <a href="#sec5dot1-remotesensing-17-00640" class="html-sec">Section 5.1</a>, where the interval between each two profiles is 1 km.</p>
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17 pages, 1733 KiB  
Article
A Forest Fire Prediction Framework Based on Multiple Machine Learning Models
by Chen Wang, Hanze Liu, Yiqing Xu and Fuquan Zhang
Forests 2025, 16(2), 329; https://doi.org/10.3390/f16020329 - 13 Feb 2025
Viewed by 383
Abstract
Fire risk prediction is of great importance for fire prevention. Fire risk maps are an effective tool to quantify regional fire risk. Most existing studies on forest fire risk maps mainly use a single machine learning model, but different models have varying degrees [...] Read more.
Fire risk prediction is of great importance for fire prevention. Fire risk maps are an effective tool to quantify regional fire risk. Most existing studies on forest fire risk maps mainly use a single machine learning model, but different models have varying degrees of feature extraction in the same spatial environment, leading to inconsistencies in prediction accuracy. To address this issue, this study proposes a novel integrated machine learning framework that systematically evaluates multiple models and combines their outputs through a weighted ensemble approach, thereby enhancing prediction robustness. During the feature selection stage, factors including socio-economic, climate, terrain, remote sensing data, and human factors were considered. Unlike previous studies that mainly use a single model, eight models were evaluated and compared using performance metrics. Three models were weighted based on Mean Squared Error (MSE) values, and cross-validation results showed an improvement in model performance. The integrated model achieved an accuracy of 0.8602, an area under the curve (AUC) of 0.772, and superior sensitivity (0.9234), outperforming individual models. Finally, the weighted framework was applied to generate a fire risk map. Compared with prior studies, this multi-model ensemble approach not only improves predictive accuracy but also provides a scalable and adaptable framework for fire risk mapping, and provides valuable insights to address future fire sustainability issues. Full article
(This article belongs to the Special Issue Climate-Smart Forestry: Forest Monitoring in a Multi-Sensor Approach)
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<p>The geographic location of the study area.</p>
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<p>The monthly (<b>a</b>) and annual (<b>b</b>) distribution of forest fires.</p>
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<p>Detailed workflow of the method. (<b>a</b>) Factors selection. (<b>b</b>) Data processing. (<b>c</b>) Data check. (<b>d</b>) Models selection. (<b>e</b>) Generate map.</p>
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<p>Factors’ importance.</p>
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<p>Fire risk map of three selected methods and the final fire risk map.</p>
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<p>Proportion of fire-prone areas in the study area.</p>
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25 pages, 12059 KiB  
Article
Albufera Lagoon Ecological State Study Through the Temporal Analysis Tools Developed with PerúSAT-1 Satellite
by Bárbara Alvado, Luis Saldarriaga, Xavier Sòria-Perpinyà, Juan Miguel Soria, Jorge Vicent, Antonio Ruíz-Verdú, Clara García-Martínez, Eduardo Vicente and Jesus Delegido
Sensors 2025, 25(4), 1103; https://doi.org/10.3390/s25041103 - 12 Feb 2025
Viewed by 387
Abstract
The Albufera of Valencia (Spain) is a representative case of pressure on water quality, which caused the hypertrophic state of the lake to completely change the ecosystem that once featured crystal clear waters. PerúSAT-1 is the first Peruvian remote sensing satellite developed for [...] Read more.
The Albufera of Valencia (Spain) is a representative case of pressure on water quality, which caused the hypertrophic state of the lake to completely change the ecosystem that once featured crystal clear waters. PerúSAT-1 is the first Peruvian remote sensing satellite developed for natural disaster monitoring. Its high spatial resolution makes it an ideal sensor for capturing highly detailed products, which are useful for a variety of applications. The ability to change its acquisition geometry allows for an increase in revisit time. The main objective of this study is to assess the potential of PerúSAT-1′s multispectral images to develop multi-parameter algorithms to evaluate the ecological state of the Albufera lagoon. During five field campaigns, samples were taken, and measurements of ecological indicators (chlorophyll-a, Secchi disk depth, total suspended matter, and its organic-inorganic fraction) were made. All possible combinations of two bands were obtained and subsequently correlated with the biophysical variables by fitting a linear regression between the field data and the band combinations. The equations for estimating all the water variables result in the following R2 values: 0.76 for chlorophyll-a (NRMSE: 16%), 0.75 for Secchi disk depth (NRMSE: 15%), 0.84 for total suspended matter (NRMSE: 11%), 0.76 for the inorganic fraction (NRMSE: 15%), and 0.87 for the organic fraction (NRMSE: 9%). Finally, the equations were applied to the Albufera lagoon images to obtain thematic maps for all variables. Full article
(This article belongs to the Special Issue Application of Satellite Remote Sensing in Geospatial Monitoring)
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<p>Study area location <span class="html-italic">L’Albufera de València</span>. Green dots are the sampling points.</p>
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<p>PerúSAT-1 images over the Albufera lagoon. Image TOA (<b>a</b>), without atmospheric correction, and image BOA (<b>b</b>), with atmospheric correction.</p>
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<p>Validation of atmospheric correction data.</p>
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<p>Boxplot of the values range for the water quality parameters. The box bounds the interquartile range (IQR: 25–75 percentile), the horizontal line inside the box indicates the median, and the error bars indicate the 90th above and 10th below percentiles. Dots indicate the outliers.</p>
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<p>Chl-<span class="html-italic">a</span> in situ as a function of ND (B4 − B1)/(B4 + B1).</p>
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<p>SDD in situ as a function of ND (B4 − B1)/(B4 + B1).</p>
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<p>TSM in situ as a function of SR (B1/B4).</p>
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<p>PIM in situ as a function of ND (B3/B1).</p>
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<p>POM in situ as a function of SR (B3/B4).</p>
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<p>Estimation maps of Chl-<span class="html-italic">a</span> (μg/L). From left to right and up to down: winter, spring, summer, and autumn.</p>
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<p>Estimation maps of SDD (m). From left to right and up to down: winter, spring, summer, and autumn.</p>
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<p>Estimation maps of TSM (mg/L). From left to right and up to down: winter, spring, summer, and autumn.</p>
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<p>Estimation maps of PIM (mg/L). From left to right and up to down: winter, spring, summer, and autumn.</p>
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<p>Estimation maps of POM (mg/L). From left to right and up to down: winter, spring, summer, and autumn.</p>
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<p>10 m pixel (<b>left</b>) of S2 image vs. 2.8 m pixel (<b>right</b>) of PerúSAT-1 image.</p>
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<p>Subset of “Obera ditch” area for PerúSAT-1 product (<b>top</b>) and S2 product (<b>bottom</b>).</p>
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<p>Estimation maps of Chl-<span class="html-italic">a</span>. Acquisition data: 20 April 2023. Left: S2 image; right: PerúSAT-1 image.</p>
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<p>Estimation maps of SDD. Acquisition data: 20 April 2023. Left: S2 image; right: PerúSAT-1 image.</p>
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<p>Estimation maps of TSM. Acquisition data: 20 April 2023. Left: S2 image; right: PerúSAT-1 image.</p>
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<p>Estimation maps of PIM. Acquisition data: 20 April 2023. Left: S2 image; right: PerúSAT-1 image.</p>
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<p>Estimation maps of POM. Acquisition data: 20 April 2023. Left: S2 image; right: PerúSAT-1 image.</p>
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<p>Subset of “Obera ditch” area for PerúSAT-1 Chl-<span class="html-italic">a</span> product (<b>top</b>) and S2 Chl-<span class="html-italic">a</span> product (<b>bottom</b>).</p>
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33 pages, 7731 KiB  
Article
Historicizing Natural Hazards and Human-Induced Landscape Transformation in a Tropical Mountainous Environment in Africa: Narratives from Elderly Citizens
by Violet Kanyiginya, Ronald Twongyirwe, David Mubiru, Caroline Michellier, Mercy Gloria Ashepet, Grace Kagoro-Rugunda, Matthieu Kervyn and Olivier Dewitte
Land 2025, 14(2), 346; https://doi.org/10.3390/land14020346 - 8 Feb 2025
Viewed by 520
Abstract
Studying natural hazards in the context of human-induced landscape transformation is complex, especially in regions with limited information. The narratives of the elderly can play a role in filling these knowledge gaps at the multi-decadal timescale. Here, we build upon a citizen-based elderly [...] Read more.
Studying natural hazards in the context of human-induced landscape transformation is complex, especially in regions with limited information. The narratives of the elderly can play a role in filling these knowledge gaps at the multi-decadal timescale. Here, we build upon a citizen-based elderly approach to understanding natural hazard patterns and landscape transformation in a tropical mountainous environment, the Kigezi Highlands (SW Uganda). We engaged 98 elderly citizens (>70 years old) living in eight small watersheds with different characteristics. Through interviews and focus group discussions, we reconstructed historical timelines and used participatory mapping to facilitate the interview process. We cross-checked the information of the elderly citizens with historical aerial photographs, archives, and field visits. Our results show that major land use/cover changes are associated with a high population increase over the last 80 years. We also evidence an increase in reported natural hazard events such as landslides and flash floods from the 1940s until the 1980s. Then, we notice a stabilization in the number of hazard events per decade, although the two most impacted decades (1980s and 2000s) stand out. Despite this new information, an increase in natural hazard frequency due to land use/cover change cannot yet be quantitatively validated, especially when the probable modulator effect of climate variability is considered. Nevertheless, the increase in the exposure of a vulnerable population to natural hazards is clear, and population growth together with poor landscape management practices are the key culprits that explain this evolution. This study demonstrates the added value of historical narratives in terms of understanding natural hazards in the context of environmental changes. This insight is essential for governments and non-governmental organizations for the development of policies and measures for disaster risk reduction that are grounded in the path dependence of local realities. Full article
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<p>The location of the Kigezi Highlands comprising the Kabale, Rubanda, and Kisoro districts and the eight studied watersheds (W1 to W8). The forest cover data are from Google Earth imagery 2021. The map background is a shaded relief with elevation in color extracted from 1 arc sec SRTM DEM (<a href="https//lpdaac.usgs.gov/products/astgtmv003/" target="_blank">https//lpdaac.usgs.gov/products/astgtmv003/</a>, last access: 22 January 2022).</p>
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<p>Field pictures of the eight watersheds (W1 to W8) illustrating dissimilar topographic and land use/cover characteristics. Photos taken by Violet Kanyiginya during fieldwork in September and October 2021.</p>
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<p>The methodological framework of the study illustrating how the multi-decadal inventory of natural hazards and landscape changes was achieved through a combination of historical narratives/approaches (in green text) and empirical methods (in blue text).</p>
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<p>Interviews and participatory mapping with the elderly citizens. (<b>a</b>) One of the maps drawn by the elderly citizens during an FGD in W6, showing past (blue marker) and current (red marker) land use and cover. (<b>b</b>,<b>c</b>) Participatory mapping during FGDs with elderly citizens in W2 and W5, respectively. (<b>d</b>) An individual interview session with an elderly citizen in W8. Photos taken by David Mubiru in September 2022.</p>
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<p>Timeline of events constructed from elderly interviews. The numbers represent watersheds where a particular event happened. “Natural hazard occurrences” includes landslides, floods, and gullies associated with flash flood events. “Deforestation” includes natural tree species that were cut down. “Wetland drainage” refers to the reclamation of wetlands for agricultural and construction purposes. “Road and housing development” includes the roads that were constructed and a change from grass-thatched to iron-roofed houses. “Resettlement schemes” are the measures implemented to depopulate the region. “Population increase” includes the increase in the numbers of both people and livestock, land shortages, and overcultivation. “Land laws enforced” includes the land management regulations that were followed during the colonial period. “Land management practices abandoned” includes the end of practices such as fallowing, the planting of native tree species, contour strip cropping, the avoidance of bush burning, and stabilizing contours with elephant grass. “Public land to private land ownership” refers to the time when land titling began to be given to individual owners and the rights of buying and selling land were established. “Restoration programmes” includes initiatives that have been implemented to rehabilitate the degraded landscapes like afforestation, diversion channels, and the creation of forest buffer zones.</p>
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<p>The temporal trend in natural hazard events recorded for each decade as per the elderly citizens between 1940 and 2010 and the corresponding median ages of the participants calculated for the middle of each decade. Note that the column for 2020 corresponds to only 2020 and 2021.</p>
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<p>(<b>a</b>) Landslide and flash flood events recorded as per the elderly respondents from 1940 to 2021. (<b>b</b>) The watershed settlement density for 2021 expressed as a ratio of the total area covered by settlements and the total area of the watershed (the settlement area was manually extracted from Google Earth imagery 2021). (<b>c</b>) The percentage forest cover change between 1954 (historical aerial photographs) and 2021 (Google Earth). Positive values indicate an increase in forest cover since 1954, while negative values represent a decline in forest cover between 1954 and 2021.</p>
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<p>The proportions of different land use/cover classes for 1954 (circles with a black stippled line) and 2021 (circles with a black contour) in each watershed (yellow polygons) as mapped manually on the 1954 aerial photographs and 2021 Google Earth imagery. The ‘other’ class represents unterraced croplands, wetlands, and other mixed land uses. The map background is a shaded relief with elevations in color extracted from 1 arc sec SRTM DEM (USGS, 2021).</p>
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<p>Land use/cover maps of the eight watersheds for 1954 and 2021. The empty spaces encompass other unmapped land uses such as unterraced croplands, grasslands, and all mixed land uses.</p>
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<p>Examples of quotes from interactions with the elderly citizens.</p>
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<p>Examples of land use and land cover changes in the watersheds. W1 shows a reduction in forest cover, showing that deforestation took place after 1954, and W4 shows an increase in forest cover. The red polygons are the watershed boundaries. The yellow arrows indicate where forest cover change took place.</p>
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28 pages, 23880 KiB  
Article
Inversion of Leaf Chlorophyll Content in Different Growth Periods of Maize Based on Multi-Source Data from “Sky–Space–Ground”
by Wu Nile, Su Rina, Na Mula, Cha Ersi, Yulong Bao, Jiquan Zhang, Zhijun Tong, Xingpeng Liu and Chunli Zhao
Remote Sens. 2025, 17(4), 572; https://doi.org/10.3390/rs17040572 - 8 Feb 2025
Viewed by 325
Abstract
Leaf chlorophyll content (LCC) is a key indicator of crop growth condition. Real-time, non-destructive, rapid, and accurate LCC monitoring is of paramount importance for precision agriculture management. This study proposes an improved method based on multi-source data, combining the Sentinel-2A spectral response function [...] Read more.
Leaf chlorophyll content (LCC) is a key indicator of crop growth condition. Real-time, non-destructive, rapid, and accurate LCC monitoring is of paramount importance for precision agriculture management. This study proposes an improved method based on multi-source data, combining the Sentinel-2A spectral response function (SRF) and computer algorithms, to overcome the limitations of traditional methods. First, the equivalent remote sensing reflectance of Sentinel-2A was simulated by combining UAV hyperspectral images with ground experimental data. Then, using grey relational analysis (GRA) and the maximum information coefficient (MIC) algorithm, we explored the complex relationship between the vegetation indices (VIs) and LCC, and further selected feature variables. Meanwhile, we utilized three spectral indices (DSI, NDSI, RSI) to identify sensitive band combinations for LCC and further analyzed the response relationship of the original bands to LCC. On this basis, we selected three nonlinear machine learning models (XGBoost, RFR, SVR) and one multiple linear regression model (PLSR) to construct the LCC inversion model, and we chose the optimal model to generate spatial distribution maps of maize LCC at the regional scale. The results indicate that there is a significant nonlinear correlation between the VIs and LCC, with the XGBoost, RFR, and SVR models outperforming the PLSR model. Among them, the XGBoost_MIC model achieved the best LCC inversion results during the tasseling stage (VT) of maize growth. In the UAV hyperspectral data, the model achieved an R2 = 0.962 and an RMSE = 5.590 mg/m2 in the training set, and an R2 = 0.582 and an RMSE = 6.019 mg/m2 in the test set. For the Sentinel-2A-simulated spectral data, the training set had an R2 = 0.923 and an RMSE = 8.097 mg/m2, while the test set showed an R2 = 0.837 and an RMSE = 3.250 mg/m2, which indicates an improvement in test set accuracy. On a regional scale, the LCC inversion model also yielded good results (train R2 = 0.76, test R2 = 0.88, RMSE = 18.83 mg/m2). In conclusion, the method proposed in this study not only significantly improves the accuracy of traditional methods but also, with its outstanding versatility, can achieve rapid, non-destructive, and precise crop growth monitoring in different regions and for various crop types, demonstrating broad application prospects and significant practical value in precision agriculture. Full article
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<p>Main flow chart.</p>
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<p>Location of study area. (<b>a</b>) is the geographical location of Inner Mongolia, (<b>b</b>) is land use types in Inner Mongolia, (<b>c</b>) is a DEM map of Hohhot, Inner Mongolia, (<b>d</b>) is flight area, (<b>e</b>) is a RGB plot of the different growth periods of V2–R1.</p>
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<p>Data collection system. (<b>a</b>) The data collection equipment, (<b>b</b>) the UAV hyperspectral data collection site, (<b>c</b>) the UAV flight course.</p>
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<p>Experiment site. (<b>a</b>) Collection of ASD spectral information set, (<b>b</b>) sample site, (<b>c</b>) collection of ground chlorophyll content.</p>
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<p>Verification of the reliability of S185 hyperspectral data. (<b>a</b>) The difference between the spectral curves of S185 and ASD, (<b>b</b>) the correlation of spectral reflectance between S185 and ASD.</p>
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<p>Comparison of spectra and ground spectral curves before and after simulation. (<b>a</b>) The spectral comparison between UAV and Sentinel-2A-simulated data, (<b>b</b>) the Sentinel-2A-simulated spectra versus Sentinel-2A satellite spectra.</p>
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<p>Correlation plots for different growth periods of maize. (<b>A</b>) Three columns show UAV data; (<b>B</b>) three columns show Sentinel-2A simulation data. (<b>a</b>) V2 stage, (<b>b</b>) V4 stage, (<b>c</b>) V6 stage, (<b>d</b>) V10 stage, (<b>e</b>) V12 stage, (<b>f</b>) VT stage, (<b>g</b>) R1 stage.</p>
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<p>Correlation between VI and LCC in different growth periods of maize. (<b>a</b>) UAV_GRA; (<b>b</b>) UAV_MIC, (<b>c</b>) SRF_GRA; (<b>d</b>) SRF_MIC.</p>
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<p>Measured and predicted LCC values based on the best band combined with the best stage of the four ML models. (<b>a</b>) UAV_DSI_XGBoost for VT growth stage, (<b>b</b>) UAV_NDSI_RFR for V12 growth stage, (<b>c</b>) UAV_NDSI_SVR for V12 growth stage, (<b>d</b>) UAV_RSI_PLSR for V6 stage.</p>
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<p>Measured and predicted values of maize in different growth periods for UAV_XGBoost model.</p>
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<p>Measured and predicted values of different growth periods of maize for SRF_XGBoost model.</p>
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<p>RFR and XGBoost models for estimating spatial distribution of LCC in different growth periods of maize in the experimental area.</p>
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<p>Changes in LCC and spectral reflectance in different growth periods of maize. (<b>a</b>) LCC changes, (<b>b</b>) spectral reflectance.</p>
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<p>Accuracy of measured and predicted LCC values of different ML models in different growth periods of maize. (<b>a</b>) Accuracy of measured and predicted LCC values of UAV + spectral index; (<b>b</b>) accuracy of measured and predicted LCC values of Sentinel-2A-simulated spectral data + spectral index; (<b>c</b>) accuracy of measured and predicted LCC values of UAV hyperspectral data + VI; (<b>d</b>) accuracy of measured and predicted LCC values of Sentinel-2A-simulated spectral data + VI.</p>
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<p>Spatial distribution of LCC inversion of maize in different growth periods in Saihan District. (<b>a</b>) is V2; (<b>b</b>) is V4; (<b>c</b>) is V6; (<b>d</b>) is V10; (<b>e</b>) is V12; (<b>f</b>) is VT; (<b>g</b>) is R1.</p>
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26 pages, 13026 KiB  
Article
Unified Spatial-Frequency Modeling and Alignment for Multi-Scale Small Object Detection
by Jing Liu, Ying Wang, Yanyan Cao, Chaoping Guo, Peijun Shi and Pan Li
Symmetry 2025, 17(2), 242; https://doi.org/10.3390/sym17020242 - 6 Feb 2025
Viewed by 422
Abstract
Small object detection in aerial imagery remains challenging due to sparse feature representation, limited spatial resolution, and complex background interference. Current deep learning approaches enhance detection performance through multi-scale feature fusion, leveraging convolutional operations to expand the receptive field or self-attention mechanisms for [...] Read more.
Small object detection in aerial imagery remains challenging due to sparse feature representation, limited spatial resolution, and complex background interference. Current deep learning approaches enhance detection performance through multi-scale feature fusion, leveraging convolutional operations to expand the receptive field or self-attention mechanisms for global context modeling. However, these methods primarily rely on spatial-domain features, while self-attention introduces high computational costs, and conventional fusion strategies (e.g., concatenation or addition) often result in weak feature correlation or boundary misalignment. To address these challenges, we propose a unified spatial-frequency modeling and multi-scale alignment fusion framework, termed USF-DETR, for small object detection. The framework comprises three key modules: the Spatial-Frequency Interaction Backbone (SFIB), the Dual Alignment and Balance Fusion FPN (DABF-FPN), and the Efficient Attention-AIFI (EA-AIFI). The SFIB integrates the Scharr operator for spatial edge and detail extraction and FFT/IFFT for capturing frequency-domain patterns, achieving a balanced fusion of global semantics and local details. The DABF-FPN employs bidirectional geometric alignment and adaptive attention to enhance the significance expression of the target area, suppress background noise, and improve feature asymmetry across scales. The EA-AIFI streamlines the Transformer attention mechanism by removing key-value interactions and encoding query relationships via linear projections, significantly boosting inference speed and contextual modeling. Experiments on the VisDrone and TinyPerson datasets demonstrate the effectiveness of USF-DETR, achieving improvements of 2.3% and 1.4% mAP over baselines, respectively, while balancing accuracy and computational efficiency. The framework outperforms state-of-the-art methods in small object detection. Full article
(This article belongs to the Special Issue Symmetry and Asymmetry Study in Object Detection)
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<p>Comparison between RT-DETR and the proposed USF-DETR method. The feature maps generated by USF-DETR (bottom row) exhibit sharper edges and richer details due to the SFIB and EA-AIFI modules. After multi-scale alignment fusion through the DABF-FPN Encoder, USF-DETR produces more accurate heatmaps, effectively highlighting small objects and improving detection results with fewer missed detections and false positives, as demonstrated by the red bounding boxes.</p>
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<p>Architecture of the proposed USF-DETR, which includes three modules: SFIB, EA-AIFI, and DABF-FPN. The top part illustrates the pipeline of USF-DETR, while the bottom part presents the module flowchart.</p>
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<p>The pipeline of SFIB consists of four stages, with each stage including a Conv layer and a SFI block. The SFI block, shown in the lower left figure, is connected across layers using the CSP concept; As depicted in the lower right image, the SFI extracts spatial and frequency domain features of the image and then fuses them.</p>
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<p>The overall structure of the DABF-FPN integrates bidirectional feature fusion to enhance small object detection and outputs multi-scale features (P2, N3, N4, and N5) for further processing.</p>
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<p>The structure of the DABF module involves high-level semantic features and low-level detailed features being adaptively processed to extract mutual representations. Two DABF blocks facilitate comprehensive information exchange and enhance feature fusion quality.</p>
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<p>EA-AIFI module. (<b>a</b>) Through input embedding and positional encoding, combined with enhanced representation of contextual information, further internal feature interaction and optimization are carried out through a FFN. (<b>b</b>) Efficient Additive Attention eliminates key value interactions and relies solely on linear projections.</p>
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<p>Bounding box distribution. (<b>a</b>) VisDrone2019-DET Dataset. (<b>b</b>) TinyPerson Dataset. The vertical axis represents the categories of annotated bounding boxes, while the horizontal axis depicts the square root of the bounding box area, measured in pixels.</p>
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<p>Visualization of feature maps. (<b>a</b>) Input image. (<b>b</b>) Feature map generated without using the SFI module in the baseline model. (<b>c</b>) Feature map generated with the SFI module in USF-DETR.</p>
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<p>Visualizing the detection results and heatmap on TinyPerson. The highlighted area represents the region of network attention, demonstrating the outstanding performance of USF-DETR in detecting small objects.</p>
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<p>Detection results of the USF-DETR on the VisDrone dataset. Boxes of different colors represent different target categories.</p>
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<p>A comparison of detection results between USF-DETR and the baseline model is presented. Green boxes indicate correct detections, blue boxes represent false positives, and red boxes denote missed detections.</p>
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<p>A comparison of detection performance between the two methods. The first row represents USF-DETR, while the second row shows the baseline method. USF-DETR significantly reduces false positives (blue) and false negatives (red).</p>
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<p>Comparison of detection performance between USF-DETR and popular methods. The yellow circle shows the outstanding detection effect of USF-DETR.</p>
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24 pages, 4060 KiB  
Article
Multi-Unmanned Aerial Vehicle Path Planning Based on Improved Nutcracker Optimization Algorithm
by Chang Xiao, Huiliao Yang and Bo Zhang
Drones 2025, 9(2), 116; https://doi.org/10.3390/drones9020116 - 4 Feb 2025
Viewed by 625
Abstract
For the multi-UAV path planning problem, environmental modeling and an improved swarm intelligence-based optimization algorithm are discussed in this paper. Firstly, to align with reality, specific constraints of UAVs in motions, attitudes and altitudes, real-world threats such as radars and no-fly zones, and [...] Read more.
For the multi-UAV path planning problem, environmental modeling and an improved swarm intelligence-based optimization algorithm are discussed in this paper. Firstly, to align with reality, specific constraints of UAVs in motions, attitudes and altitudes, real-world threats such as radars and no-fly zones, and inter-UAV collisions are considered. Thus, multi-UAV path planning is transformed into a multi-objective constrained optimization problem. Accordingly, an improved nutcracker optimization algorithm is proposed to solve this problem. Through initializing with logistic chaotic mapping and the lens imaging inverse learning strategy, a more fit elite initialization population is produced to increase the efficiency of path planning. Furthermore, by adjusting adaptive parameters and integrating an improved sine-cosine search strategy, a balance between global exploration capability and local exploitation capability during path planning is achieved. Experimental results show that the improved nutcracker optimization algorithm surpasses other algorithms with respect to both convergence speed and convergence value, making it an effective method for multi-UAV path planning. Full article
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<p>The diagram of the flying environment: the sphere represents the radar detection range, the red cuboid indicates the no-fly zone, and the blue undulations represent mountains.</p>
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<p>The diagram of the limitations of yaw and pitch angles along the path points: since the yaw angle <math display="inline"><semantics> <mi>α</mi> </semantics></math> and pitch angle <math display="inline"><semantics> <mi>β</mi> </semantics></math> are within the restricted range, the curvature of the path connecting the previous path point <math display="inline"><semantics> <msub> <mi>P</mi> <mrow> <mi>i</mi> <mo>,</mo> <mi>j</mi> <mo>−</mo> <mn>1</mn> </mrow> </msub> </semantics></math>, the current one <math display="inline"><semantics> <msub> <mi>P</mi> <mrow> <mi>i</mi> <mo>,</mo> <mi>j</mi> </mrow> </msub> </semantics></math>, and the next one <math display="inline"><semantics> <msub> <mi>P</mi> <mrow> <mi>i</mi> <mo>,</mo> <mi>j</mi> <mo>+</mo> <mn>1</mn> </mrow> </msub> </semantics></math> is limited.</p>
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<p>Random initialization adopted in NOA: the initialization sequence is uneven.</p>
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<p>The logistic map initialization employed in INOA: the initialization sequence is more uniform.</p>
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<p>The diagram of the lens imaging inverse learning strategy: if <span class="html-italic">P</span> is the current point within the bounds of <math display="inline"><semantics> <mrow> <mo>[</mo> <mi>l</mi> <mi>b</mi> <mo>,</mo> <mi>u</mi> <mi>b</mi> <mo>]</mo> </mrow> </semantics></math>, then <math display="inline"><semantics> <msup> <mi>P</mi> <mo>′</mo> </msup> </semantics></math> is the inverse solution of <span class="html-italic">P</span> obtained through by the lens imaging inverse learning strategy.</p>
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<p>Parameter adjustment: INOA improves parameters <math display="inline"><semantics> <msub> <mi>P</mi> <mrow> <mi>a</mi> <mn>1</mn> <mi>n</mi> <mi>e</mi> <mi>w</mi> </mrow> </msub> </semantics></math> and <math display="inline"><semantics> <msub> <mi>P</mi> <mrow> <mi>a</mi> <mn>2</mn> <mi>n</mi> <mi>e</mi> <mi>w</mi> </mrow> </msub> </semantics></math> in the foraging/storage and the caching/recovery phases as trigonometric and quadratic functions, respectively, to better balance the exploration and exploitation.</p>
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<p>The flowchat of INOA.</p>
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<p>Simulation based on CEC2020: INOA obtains the best results on all 10 functions.</p>
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<p>Simulation based on CEC2020: INOA obtains the best results on all 10 functions.</p>
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<p>The result of multi-UAV path planning in the first scenario with 6 UAVs, 3 mountains, 2 radars, and 2 no-fly zones.</p>
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<p>Top–down view of multi-UAV path planning in the first scenario with 6 UAVs, 3 mountains, 2 radars, and 2 no-fly zones.</p>
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<p>The result of multi-UAV path planning in the second scenario with 6 UAVs, 6 mountains, 2 radars, and 2 no-fly zones: compared with the first scenario, the number of mountains increases to 6.</p>
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<p>Top–down view of multi-UAV path planning in the second scenario with 6 UAVs, 6 mountains, 2 radars, and 2 no-fly zones: compared with the first scenario, the number of mountains increases to 6.</p>
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<p>The result of multi-UAV path planning in the third scenario with 6 UAVs, 3 mountains, 4 radars, and 2 no-fly zones: compared with the first scenario, the number of radar threats increases to 4.</p>
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<p>Top–down view of multi-UAV path planning in the third scenario with 6 UAVs, 3 mountains, 4 radars, and 2 no-fly zones: compared with the first scenario, the number of radar threats increases to 4.</p>
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<p>The result of multi-UAV path planning in the fourth scenario with 8 UAVs, 6 mountains, 4 radars, and 2 no-fly zones: compared with the first scenario, the numbers of UAVs, mountains, and radars all increased.</p>
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<p>Top–down view of multi-UAV path planning in the fourth scenario with 8 UAVs, 6 mountains, 4 radars, and 2 no-fly zones: compared with the first scenario, the numbers of UAVs, mountains, and radars are all increased.</p>
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<p>Fitness comparison: INOA achieves the best fitness compared with PSO, GWO, and NOA, with the improved search efficiency.</p>
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22 pages, 29748 KiB  
Article
An Integrated Method for Inverting Beach Surface Moisture by Fusing Unmanned Aerial Vehicle Orthophoto Brightness with Terrestrial Laser Scanner Intensity
by Jun Zhu, Kai Tan, Feijian Yin, Peng Song and Faming Huang
Remote Sens. 2025, 17(3), 522; https://doi.org/10.3390/rs17030522 - 3 Feb 2025
Viewed by 528
Abstract
Beach surface moisture (BSM) is crucial to studying coastal aeolian sand transport processes. However, traditional measurement techniques fail to accurately monitor moisture distribution with high spatiotemporal resolution. Remote sensing technologies have garnered widespread attention for providing rapid and non-contact moisture measurements, but a [...] Read more.
Beach surface moisture (BSM) is crucial to studying coastal aeolian sand transport processes. However, traditional measurement techniques fail to accurately monitor moisture distribution with high spatiotemporal resolution. Remote sensing technologies have garnered widespread attention for providing rapid and non-contact moisture measurements, but a single method has inherent limitations. Passive remote sensing is challenged by complex beach illumination and sediment grain size variability. Active remote sensing represented by LiDAR (light detection and ranging) exhibits high sensitivity to moisture, but requires cumbersome intensity correction and may leave data holes in high-moisture areas. Using machine learning, this research proposes a BSM inversion method that fuses UAV (unmanned aerial vehicle) orthophoto brightness with intensity recorded by TLSs (terrestrial laser scanners). First, a back propagation (BP) network rapidly corrects original intensity with in situ scanning data. Second, beach sand grain size is estimated based on the characteristics of the grain size distribution. Then, by applying nearest point matching, intensity and brightness data are fused at the point cloud level. Finally, a new BP network coupled with the fusion data and grain size information enables automatic brightness correction and BSM inversion. A field experiment at Baicheng Beach in Xiamen, China, confirms that this multi-source data fusion strategy effectively integrates key features from diverse sources, enhancing the BP network predictive performance. This method demonstrates robust predictive accuracy in complex beach environments, with an RMSE of 2.63% across 40 samples, efficiently producing high-resolution BSM maps that offer values in studying aeolian sand transport mechanisms. Full article
(This article belongs to the Section Ocean Remote Sensing)
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<p>Field deployment at the Baicheng Beach and the surface moisture sampling points (green). The wind rose was generated based on the average wind frequency for July 2024.</p>
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<p>(<b>a</b>) Samples with different moisture levels with a Spyder standard gray card. (<b>b</b>) Samples with different moisture levels with a Spyder 24-color standard color card (from left to right, the moisture of the samples from top to bottom are 5.87%, 8.27%, 5.39%, 5.28%, 4.36%, 4.35%, 5.94%, 4.21%, 3.09%, 7.17%, 4.61%, and 5.31%).</p>
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<p>The workflow of the proposed method.</p>
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<p>The process of feature parameter extraction: (<b>a</b>) Extraction of sample information; (<b>b</b>) acquisition of feature parameters; (<b>c</b>) Gaussian-fitting the histogram of color parameters and intensity parameters.</p>
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<p>(<b>a</b>) Original intensity distribution. (<b>b</b>) Corrected intensity distribution.</p>
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<p>(<b>a</b>) Characteristics of sediment grain size distribution. (<b>b</b>) Sediment average grain size vs. distance from sampling point to beach berm.</p>
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<p>Correlation coefficient matrix between the feature parameters and moisture content.</p>
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<p>(<b>a</b>) Distribution of beach surface moisture and estimation errors. (<b>b</b>) Measured moisture of the samples vs. estimated moisture of the samples.</p>
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<p>(<b>a</b>) Relationship between original intensity and distance. (<b>b</b>) Relationship between corrected intensity and distance. (<b>c</b>) Relationship between original intensity and incidence angle. (<b>d</b>) Relationship between corrected intensity and incidence angle.</p>
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<p>Relationship between feature parameters and moisture content under different grain size conditions. (<b>a</b>) V (from HSV color space) vs. moisture. (<b>b</b>) Intensity vs. moisture.</p>
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<p>(<b>a</b>) Distribution of beach surface moisture based on intensity. (<b>b</b>) Distribution of beach surface moisture based on brightness.</p>
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34 pages, 7048 KiB  
Article
Research on Mobile Robot Path Planning Based on MSIAR-GWO Algorithm
by Danfeng Chen, Junlang Liu, Tengyun Li, Jun He, Yong Chen and Wenbo Zhu
Sensors 2025, 25(3), 892; https://doi.org/10.3390/s25030892 - 1 Feb 2025
Viewed by 358
Abstract
Path planning is of great research significance as it is key to affecting the efficiency and safety of mobile robot autonomous navigation task execution. The traditional gray wolf optimization algorithm is widely used in the field of path planning due to its simple [...] Read more.
Path planning is of great research significance as it is key to affecting the efficiency and safety of mobile robot autonomous navigation task execution. The traditional gray wolf optimization algorithm is widely used in the field of path planning due to its simple structure, few parameters, and easy implementation, but the algorithm still suffers from the disadvantages of slow convergence, ease of falling into the local optimum, and difficulty in effectively balancing exploration and exploitation in practical applications. For this reason, this paper proposes a multi-strategy improved gray wolf optimization algorithm (MSIAR-GWO) based on reinforcement learning. First, a nonlinear convergence factor is introduced, and intelligent parameter configuration is performed based on reinforcement learning to solve the problem of high randomness and over-reliance on empirical values in the parameter selection process to more effectively coordinate the balance between local and global search capabilities. Secondly, an adaptive position-update strategy based on detour foraging and dynamic weights is introduced to adjust the weights according to changes in the adaptability of the leadership roles, increasing the guiding role of the dominant individual and accelerating the overall convergence speed of the algorithm. Furthermore, an artificial rabbit optimization algorithm bypass foraging strategy, by adding Brownian motion and Levy flight perturbation, improves the convergence accuracy and global optimization-seeking ability of the algorithm when dealing with complex problems. Finally, the elimination and relocation strategy based on stochastic center-of-gravity dynamic reverse learning is introduced for the inferior individuals in the population, which effectively maintains the diversity of the population and improves the convergence speed of the algorithm while avoiding falling into the local optimal solution effectively. In order to verify the effectiveness of the MSIAR-GWO algorithm, it is compared with a variety of commonly used swarm intelligence optimization algorithms in benchmark test functions and raster maps of different complexities in comparison experiments, and the results show that the MSIAR-GWO shows excellent stability, higher solution accuracy, and faster convergence speed in the majority of the benchmark-test-function solving. In the path planning experiments, the MSIAR-GWO algorithm is able to plan shorter and smoother paths, which further proves that the algorithm has excellent optimization-seeking ability and robustness. Full article
(This article belongs to the Section Sensors and Robotics)
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<p>Social hierarchy pyramid of the gray wolf population.</p>
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<p>Schematic diagram of the mechanism for updating the location of the gray wolf population.</p>
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<p>Comparison of the convergence factors for different <math display="inline"><semantics> <msub> <mi>λ</mi> <mn>1</mn> </msub> </semantics></math> and <math display="inline"><semantics> <msub> <mi>λ</mi> <mn>2</mn> </msub> </semantics></math>.</p>
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<p>Trajectory distribution diagram of Levy flight and Brownian motion. (<b>a</b>) Levy flight trajectory distribution diagram; (<b>b</b>) Brownian motion trajectory distribution diagram.</p>
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<p>Flowchart of MSIAR-GWO.</p>
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<p>Convergence curves of different algorithms on a unimodal benchmark test function. (<b>a</b>) The convergence curve of F1; (<b>b</b>) The convergence curve of F2; (<b>c</b>) The convergence curve of F3; (<b>d</b>) The convergence curve of F4; (<b>e</b>) The convergence curve of F5; (<b>f</b>) The convergence curve of F6; (<b>g</b>) The convergence curve of F7.</p>
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<p>Convergence curves of different algorithms on a unimodal benchmark test function. (<b>a</b>) The convergence curve of F1; (<b>b</b>) The convergence curve of F2; (<b>c</b>) The convergence curve of F3; (<b>d</b>) The convergence curve of F4; (<b>e</b>) The convergence curve of F5; (<b>f</b>) The convergence curve of F6; (<b>g</b>) The convergence curve of F7.</p>
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<p>Convergence curves of different algorithms on multi-modal benchmark test functions. (<b>a</b>) The convergence curve of F8; (<b>b</b>) The convergence curve of F9; (<b>c</b>) The convergence curve of F10; (<b>d</b>) The convergence curve of F11; (<b>e</b>) The convergence curve of F12; (<b>f</b>) The convergence curve of F13.</p>
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<p>Convergence curves of different algorithms on multi-modal benchmark test functions. (<b>a</b>) The convergence curve of F8; (<b>b</b>) The convergence curve of F9; (<b>c</b>) The convergence curve of F10; (<b>d</b>) The convergence curve of F11; (<b>e</b>) The convergence curve of F12; (<b>f</b>) The convergence curve of F13.</p>
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<p>Convergence curves of different algorithms on fixed-dimensional multi-modal benchmark test functions. (<b>a</b>) The convergence curve of F14; (<b>b</b>) The convergence curve of F15; (<b>c</b>) The convergence curve of F16; (<b>d</b>) The convergence curve of F17; (<b>e</b>) The convergence curve of F18.</p>
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<p>Convergence curves of different algorithms on fixed-dimensional multi-modal benchmark test functions. (<b>a</b>) The convergence curve of F14; (<b>b</b>) The convergence curve of F15; (<b>c</b>) The convergence curve of F16; (<b>d</b>) The convergence curve of F17; (<b>e</b>) The convergence curve of F18.</p>
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<p>Performance comparison between MSIAR-GWO and other algorithms.</p>
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<p>Comparison of paths before and after de-redundancy optimization. (<b>a</b>) The original path without de-redundancy optimization; (<b>b</b>) The path after the de-redundancy optimization.</p>
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<p>Comparison experiment with the traditional A* algorithm in raster environment. (<b>a</b>) Optimal path of MSIAR-GWO algorithm and A* algorithm under 20 × 20 raster map; (<b>b</b>) Optimal path of MSIAR-GWO algorithm and A* algorithm under 40 × 40 raster map.</p>
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<p>Average path and best path in a 20 × 20 raster environment.</p>
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<p>Average path and best path in a 30 × 30 raster environment.</p>
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<p>Average path and best path in a 40 × 40 raster environment.</p>
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<p>Shortest path planning graph for 8 algorithms in 20 × 20 raster environment. (<b>a</b>) MSIAR-GWO; (<b>b</b>) GWO; (<b>c</b>) ARO; (<b>d</b>) DBO; (<b>e</b>) WOA; (<b>f</b>) IGWO; (<b>g</b>) AGWO; (<b>h</b>) RSMGWO.</p>
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<p>Shortest path planning graph for 8 algorithms in 20 × 20 raster environment. (<b>a</b>) MSIAR-GWO; (<b>b</b>) GWO; (<b>c</b>) ARO; (<b>d</b>) DBO; (<b>e</b>) WOA; (<b>f</b>) IGWO; (<b>g</b>) AGWO; (<b>h</b>) RSMGWO.</p>
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<p>Graph of shortest path planning for 8 algorithms in 30 × 30 raster environment. (<b>a</b>) MSIAR-GWO; (<b>b</b>) GWO; (<b>c</b>) ARO; (<b>d</b>) DBO; (<b>e</b>) WOA; (<b>f</b>) IGWO; (<b>g</b>) AGWO; (<b>h</b>) RSMGWO.</p>
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<p>Graph of shortest path planning for 8 algorithms in 30 × 30 raster environment. (<b>a</b>) MSIAR-GWO; (<b>b</b>) GWO; (<b>c</b>) ARO; (<b>d</b>) DBO; (<b>e</b>) WOA; (<b>f</b>) IGWO; (<b>g</b>) AGWO; (<b>h</b>) RSMGWO.</p>
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<p>Shortest path planning for 8 algorithms in 40 × 40 raster environment. (<b>a</b>) MSIAR-GWO; (<b>b</b>) GWO; (<b>c</b>) ARO; (<b>d</b>) DBO; (<b>e</b>) WOA; (<b>f</b>) IGWO; (<b>g</b>) AGWO; (<b>h</b>) RSMGWO.</p>
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<p>Shortest path planning for 8 algorithms in 40 × 40 raster environment. (<b>a</b>) MSIAR-GWO; (<b>b</b>) GWO; (<b>c</b>) ARO; (<b>d</b>) DBO; (<b>e</b>) WOA; (<b>f</b>) IGWO; (<b>g</b>) AGWO; (<b>h</b>) RSMGWO.</p>
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<p>Average convergence curves in a 20 × 20 grid environment.</p>
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<p>Average convergence curves in a 30 × 30 grid environment.</p>
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<p>Average convergence curves in a 40 × 40 grid environment.</p>
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14 pages, 18673 KiB  
Technical Note
A Machine Learning Algorithm to Convert Geostationary Satellite LST to Air Temperature Using In Situ Measurements: A Case Study in Rome and High-Resolution Spatio-Temporal UHI Analysis
by Andrea Cecilia, Giampietro Casasanta, Igor Petenko and Stefania Argentini
Remote Sens. 2025, 17(3), 468; https://doi.org/10.3390/rs17030468 - 29 Jan 2025
Viewed by 392
Abstract
Air temperature (Ta) measurements are crucial for characterizing phenomena like the urban heat island (UHI), which can create critical conditions in cities during summer. This study aims to develop a machine learning-based model, namely gradient boosting, to estimate Ta [...] Read more.
Air temperature (Ta) measurements are crucial for characterizing phenomena like the urban heat island (UHI), which can create critical conditions in cities during summer. This study aims to develop a machine learning-based model, namely gradient boosting, to estimate Ta from geostationary satellite LST data and to apply these estimates to investigate UHI dynamics. Using Rome, Italy, as a case study, the model was trained with Ta data from 15 weather stations, taking multi-temporal LST values (instantaneous and lagged up to 4 h) and additional predictors. The model achieved an overall RMSE of 0.9 °C. The resulting Ta fields, with a 3 km spatial and hourly temporal resolution, enabled a detailed analysis of UHI intensity and dynamics during the summers of 2019–2020, significantly enhancing the spatial and temporal detail compared to previous studies based solely on in situ data. The results also revealed a slightly higher nocturnal UHI intensity than previously reported, attributed to the inclusion of rural areas with near-zero imperviousness, thanks to the complete mapping of Ta across the domain now accessible. Full article
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<p>(<b>a</b>) Spatial work domain, highlighting the edges of the LST measurement cells (pixels). In light blue are the cells where in situ meteorological stations are present, indicated by orange triangles. (<b>b</b>) Zoom on the domain to better shows the urbanized areas and the parks, the latter highlighted in green with the name in white. The blue lines indicate the main roads, while the light blue color represents the main watercourses. Finally, the green line indicates the A90 Grande Raccordo Anulare motorway, within which we conventionally define the city of Rome.</p>
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<p>Some of the dataset predictors, resampled to LST resolution. (<b>a</b>) Altitude a.s.l. (<b>b</b>) Imperviousness. (<b>c</b>) Land Cover. (<b>d</b>) Tree Cover. (<b>e</b>) Grassland. (<b>f</b>) NDVI (July 2019).</p>
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<p>(<b>a</b>) Diurnal cycle of RMSE; (<b>b</b>) spatial distribution of RMSE, the mean over the entire time period.</p>
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<p>(<b>a</b>) Importance of predictors in percentage. (<b>b</b>) Correlation matrix between predictors. The abbreviations used are as follows: cell, cell ID in the domain; lon, longitude; lat, latitude; lst_C, synchronous LST; dtm, elevation; imp, imperviousness; lst_DX, LST with a lag of X hours backwards.</p>
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<p>Spatial distribution of daily extrema of LST and air temperature, including for the latter maps based only on in situ measurements and on model estimates. (<b>a</b>) Minimum <math display="inline"><semantics> <msub> <mi>T</mi> <mi>a</mi> </msub> </semantics></math> (in situ data). (<b>b</b>) Minimum <math display="inline"><semantics> <msub> <mi>T</mi> <mi>a</mi> </msub> </semantics></math> (model output). (<b>c</b>) Minimum LST. (<b>d</b>) Maximum <math display="inline"><semantics> <msub> <mi>T</mi> <mi>a</mi> </msub> </semantics></math> (in situ data). (<b>e</b>) Maximum <math display="inline"><semantics> <msub> <mi>T</mi> <mi>a</mi> </msub> </semantics></math> (model output). (<b>f</b>) Maximum LST.</p>
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<p>Scatter plots of daily extremes of LST and air temperature (model output data) against IMP (imperviousness), with respective Pearson correlation indices R. (<b>a</b>) Minimum LST. (<b>b</b>) Minimum temperature. (<b>c</b>) Maximum LST. (<b>d</b>) Maximum temperature.</p>
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<p>(<b>a</b>) Diurnal cycle of UHI intensity estimated using air temperature data; (<b>b</b>) diurnal cycle of SUHI intensity estimated using LST and imperviousness data, along with the diurnal cycle of the correlation coefficient between LST and imperviousness.</p>
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<p>(<b>a</b>) Diurnal cycle of UHI intensity estimated using air temperature data output from the machine learning model, and SUHI intensity measured using LST data, compared, (<b>b</b>) and the diurnal cycle of the SUHI and UHI gradients.</p>
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25 pages, 27454 KiB  
Article
Development of an Optimized YOLO-PP-Based Cherry Tomato Detection System for Autonomous Precision Harvesting
by Xiayang Qin, Jingxing Cao, Yonghong Zhang, Tiantian Dong and Haixiao Cao
Processes 2025, 13(2), 353; https://doi.org/10.3390/pr13020353 - 27 Jan 2025
Viewed by 593
Abstract
An accurate and efficient detection method for harvesting is crucial for the development of automated harvesting robots in short-cycle, high-yield facility tomato cultivation environments. This study focuses on cherry tomatoes, which grow in clusters, and addresses the complexity and reduced detection speed associated [...] Read more.
An accurate and efficient detection method for harvesting is crucial for the development of automated harvesting robots in short-cycle, high-yield facility tomato cultivation environments. This study focuses on cherry tomatoes, which grow in clusters, and addresses the complexity and reduced detection speed associated with the current multi-step processes that combine target detection with segmentation and traditional image processing for clustered fruits. We propose YOLO-Picking Point (YOLO-PP), an improved cherry tomato picking point detection network designed to efficiently and accurately identify stem keypoints on embedded devices. YOLO-PP employs a C2FET module with an EfficientViT branch, utilizing parallel dual-path feature extraction to enhance detection performance in dense scenes. Additionally, we designed and implemented a Spatial Pyramid Squeeze Pooling (SPSP) module to extract fine features and capture multi-scale spatial information. Furthermore, a new loss function based on Inner-CIoU was developed specifically for keypoint tasks to further improve detection efficiency.The model was tested on a real greenhouse cherry tomato dataset, achieving an accuracy of 95.81%, a recall rate of 98.86%, and mean Average Precision (mAP) scores of 99.18% and 98.87% for mAP50 and mAP50-95, respectively. Compared to the DEKR, YOLO-Pose, and YOLOv8-Pose models, the mAP value of the YOLO-PP model improved by 16.94%, 10.83%, and 0.81%, respectively. The proposed algorithm has been implemented on NVIDIA Jetson edge computing devices, equipped with a human–computer interaction interface. The results demonstrate that the proposed Improved Picking Point Detection Network exhibits excellent performance and achieves real-time accurate detection of cherry tomato harvesting tasks in facility agriculture. Full article
(This article belongs to the Section Automation Control Systems)
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<p>Research flow of our approach.</p>
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<p>Cherry tomato cultivation and data collection scene. (<b>a</b>) Tomato cultivation environment in facility agriculture, (<b>b</b>) Field data collection of tomatoes.</p>
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<p>Representative sample datasets in different states: (<b>a</b>) Direct light, (<b>b</b>) Backlight, (<b>c</b>) Front view, (<b>d</b>) Side view, (<b>e</b>) and Top-down view.</p>
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<p>Data annotation process.</p>
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<p>The overall network architecture of YOLO-PP.</p>
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<p>The evolution of the architecture of C3, C2F, and C2FET Modules.</p>
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<p>(<b>a</b>) The left path integrates a fundamental convolutional component and a series of bottleneck structures. The primary function of these structures is to refine residual features and integrate the outputs of the two independent branches of the C2FET module at the endpoint. (<b>b</b>) The constructed Transformer branch adopts a three-layer architecture and incorporates a progressive group attention mechanism. (<b>c</b>) The Cascaded Group Attention (CGA) module meticulously deconstructs the computation process of each attention head, customizing feature enhancement for each head to improve the diversity of attention maps.</p>
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<p>The structure of the SPSP module.</p>
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<p>The representation of Inner-IoU and visual explanation.</p>
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<p>Comparison of mAP@50 and mAP@50-95 results for different models.</p>
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<p>Actual detection picking point results of the different network models.</p>
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<p>Performance of YOLO-PP in special cases: (<b>a</b>) Detection results under different lighting conditions; (<b>b</b>) Detection results in multi-target and occlusion scenarios.</p>
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<p>Comparison of ablation results from precision mAP@0.5 and mAP@0.5–0.95: Precision curve; mAP50 curve; mAP50-95 curve.</p>
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<p>Variation curves of loss function for ablation experiments.</p>
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<p>Training loss function value curves: (<b>a</b>) YOLOv8-Pose loss function curve; (<b>b</b>) YOLO-PP loss function curve Abscissa, iteration times, and ordinate, loss value.</p>
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<p>Actual screen of device deployment.</p>
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<p>Hardware platform and software implementation of the automated tomato harvesting robot.</p>
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27 pages, 5483 KiB  
Article
Application of Black-Winged Differential-Variant Whale Optimization Algorithm in the Optimization Scheduling of Cascade Hydropower Stations
by Mi Zhang, Zixuan Liu, Rungang Bao, Shuli Zhu, Li Mo and Yuqi Yang
Sustainability 2025, 17(3), 1018; https://doi.org/10.3390/su17031018 - 26 Jan 2025
Viewed by 616
Abstract
Hydropower is a vital strategic component of China’s clean energy development. Its construction and optimized water resource allocation are crucial for addressing global energy challenges, promoting socio-economic development, and achieving sustainable development. However, the optimization scheduling of cascade hydropower stations is a large-scale, [...] Read more.
Hydropower is a vital strategic component of China’s clean energy development. Its construction and optimized water resource allocation are crucial for addressing global energy challenges, promoting socio-economic development, and achieving sustainable development. However, the optimization scheduling of cascade hydropower stations is a large-scale, multi-constrained, and nonlinear problem. Traditional optimization methods suffer from low computational efficiency, while conventional intelligent algorithms still face issues like premature convergence and local optima, which severely hinder the full utilization of water resources. This study proposed an improved whale optimization algorithm, the Black-winged Differential-variant Whale Optimization Algorithm (BDWOA), which enhanced population diversity through a Logistic-Sine-Cosine combination chaotic map, improved algorithm flexibility with an adaptive adjustment strategy, and introduced the migration mechanism of the black-winged kite algorithm along with a differential mutation strategy to enhance the global search ability and convergence capacity. The BDWOA algorithm was tested using test functions with randomly generated simulated data, with its performance compared against five related optimization algorithms. Results indicate that the BDWOA achieved the optimal value with the fewest iterations, effectively overcoming the limitations of the original whale optimization algorithm. Further validation using actual runoff data for the cascade hydropower station optimization scheduling model showed that the BDWOA effectively enhanced power generation efficiency. In high-flow years, the average power generation increased by 8.3%, 6.5%, 6.8%, 4.1%, and 8.2% compared to the five algorithms while achieving the shortest computation time. Significant improvements in power generation were also observed in normal-flow and low-flow years. The scheduling solutions generated by the BDWOA can adapt to varying inflow conditions, offering an innovative approach to solving complex hydropower station optimization scheduling problems. This contributes to the sustainable utilization of water resources and supports the long-term development of renewable energy. Full article
(This article belongs to the Section Energy Sustainability)
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<p>Population distribution plots for combined chaos and single chaos.</p>
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<p>Population distribution plots for combined chaos and single chaos.</p>
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<p>Convergence process of different algorithms with 10 sets of test functions.</p>
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<p>Flowchart of BDWOA algorithm.</p>
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<p>Topology diagram of the Xiluodu–Xiangjiaba–Three Gorges cascade reservoir system.</p>
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<p>Tukey’s HSD test in high-flow year.</p>
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<p>Tukey’s HSD test in normal-flow year.</p>
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<p>Tukey’s HSD test in low-flow year.</p>
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<p>Boxplots of power generation under typical year scenarios.</p>
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<p>Power generation convergence process under each typical year scenario.</p>
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<p>Output processes of each algorithm under different typical scenarios.</p>
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<p>Inflow and outflow processes solved by the BDWOA algorithm under the high-flow year scenario.</p>
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<p>Inflow and outflow processes solved by the BDWOA algorithm under the normal-flow year scenario.</p>
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<p>Inflow and outflow processes solved by the BDWOA algorithm under the low-flow year scenario.</p>
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<p>Power generation–water level processes of cascade hydropower stations in the high-flow year scenario.</p>
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<p>Power generation–water level processes of cascade hydropower stations in the normal-flow year scenario.</p>
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<p>Power generation–water level processes of cascade hydropower stations in the low-flow year scenario.</p>
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