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Search Results (3,517)

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23 pages, 15611 KiB  
Article
Landslide Prediction Validation in Western North Carolina After Hurricane Helene
by Sophia Lin, Shenen Chen, Ryan A. Rasanen, Qifan Zhao, Vidya Chavan, Wenwu Tang, Navanit Shanmugam, Craig Allan, Nicole Braxtan and John Diemer
Geotechnics 2024, 4(4), 1259-1281; https://doi.org/10.3390/geotechnics4040064 (registering DOI) - 14 Dec 2024
Abstract
Hurricane Helene triggered 1792 landslides across western North Carolina and has caused damage to 79 bridges to date. Helene hit western North Carolina days after a low-pressure system dropped up to 254 mm of rain in some locations of western North Carolina (e.g., [...] Read more.
Hurricane Helene triggered 1792 landslides across western North Carolina and has caused damage to 79 bridges to date. Helene hit western North Carolina days after a low-pressure system dropped up to 254 mm of rain in some locations of western North Carolina (e.g., Asheville Regional Airport). The already waterlogged region experienced devastation as significant additional rainfall occurred during Helene, where some areas, like Asheville, North Carolina received an additional 356 mm of rain (National Weather Service, 2024). In this study, machine learning (ML)-generated multi-hazard landslide susceptibility maps are compared to the documented landslides from Helene. The landslide models use the North Carolina landslide database, soil survey, rainfall, USGS digital elevation model (DEM), and distance to rivers to create the landslide variables. From the DEM, aspect factors and slope are computed. Because recent research in western North Carolina suggests fault movement is destabilizing slopes, distance to fault was also incorporated as a predictor variable. Finally, soil types were used as a wildfire predictor variable. In total, 4794 landslides were used for model training. Random Forest and logistic regression machine learning algorithms were used to develop the landslide susceptibility map. Furthermore, landslide susceptibility was also examined with and without consideration of wildfires. Ultimately, this study indicates heavy rainfall and debris-laden floodwaters were critical in triggering both landslides and scour, posing a dual threat to bridge stability. Field investigations from Hurricane Helene revealed that bridge damage was concentrated at bridge abutments, with scour and sediment deposition exacerbating structural vulnerability. We evaluated the assumed flooding potential (AFP) of damaged bridges in the study area, finding that bridges with lower AFP values were particularly vulnerable to scour and submersion during flood events. Differentiating between landslide-induced and scour-induced damage is essential for accurately assessing risks to infrastructure. The findings emphasize the importance of comprehensive hazard mapping to guide infrastructure resilience planning in mountainous regions. Full article
14 pages, 17262 KiB  
Article
Analyzing the Accuracy of Satellite-Derived DEMs Using High-Resolution Terrestrial LiDAR
by Aya Hamed Mohamed, Mohamed Islam Keskes and Mihai Daniel Nita
Land 2024, 13(12), 2171; https://doi.org/10.3390/land13122171 - 13 Dec 2024
Viewed by 204
Abstract
The accurate estimation of Digital Elevation Models (DEMs) derived from satellite data is critical for numerous environmental applications. This study evaluates the accuracy and reliability of two satellite-derived elevation models, the ALOS World 3D and SRTM DEMs, specifically for their application in hydrological [...] Read more.
The accurate estimation of Digital Elevation Models (DEMs) derived from satellite data is critical for numerous environmental applications. This study evaluates the accuracy and reliability of two satellite-derived elevation models, the ALOS World 3D and SRTM DEMs, specifically for their application in hydrological modeling. A comparative analysis with Terrestrial Laser Scanning (TLS) measurements assessed the agreement between these datasets. Multiple linear regression models were utilized to evaluate the relationships between the datasets and provide detailed insights into their accuracy and biases. The results indicate significant correlations between satellite DEMs and TLS measurements, with adjusted R-square values of 0.8478 for ALOS and 0.955 for the SRTM. To quantify the average difference, root mean square error (RMSE) values were calculated as 10.43 m for ALOS and 5.65 m for the SRTM. Additionally, slope and aspect analyses were performed to highlight terrain characteristics across the DEMs. Slope analysis showed a statistically significant negative correlation between SRTM and TLS slopes (R2 = 0.16, p < 4.47 × 10−10 indicating a weak relationship, while no significant correlation was observed between ALOS and TLS slopes. Aspect analysis showed significant positive correlations for both ALOS and the SRTM with TLS aspect, capturing 30.21% of the variance. These findings demonstrate the accuracy of satellite-derived elevation models in representing terrain features relative to high-resolution terrestrial data. Full article
(This article belongs to the Section Land – Observation and Monitoring)
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<p>Geographical location of study area.</p>
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<p>Summary of data processing and analysis workflow.</p>
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<p>Analyzing the datasets using a grid-cell-based approach.</p>
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<p>Slope analysis of satellite-derived products (ALOS and SRTM) using grid cell analysis.</p>
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<p>Analyzing the TLS slope using a grid-cell-based approach.</p>
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<p>Aspect analysis of satellite-derived products (ALOS and SRTM).</p>
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<p>Analyzing the TLS aspect using a grid-cell-based approach.</p>
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<p>Comparison of satellites (SRTM and ALOS) with TLS measurements. (<b>a</b>) Elevation values, (<b>b</b>) slope values, and (<b>c</b>) aspect values for comparison of each model.</p>
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<p>Comparison of satellites (SRTM and ALOS) with TLS measurements. (<b>a</b>) Elevation values, (<b>b</b>) slope values, and (<b>c</b>) aspect values for comparison of each model.</p>
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18 pages, 8682 KiB  
Article
Quantitative Assessment of the Impact of Port Construction on the Surrounding Mudflat Topography Based on Remote Sensing—A Case Study of Binhai Port in Jiangsu Province
by Binbin Chen, Zhengdong Chen, Chuping Song, Xiaodong Pang, Peixun Liu and Yanyan Kang
J. Mar. Sci. Eng. 2024, 12(12), 2290; https://doi.org/10.3390/jmse12122290 - 12 Dec 2024
Viewed by 295
Abstract
Activities, particularly harbor construction, often exert significant and non-negligible impacts on coastal environments. Therefore, it is of great practical importance to quantitatively assess the effects of such construction on the surrounding topography, such as tidal flats. This study focuses on the coast of [...] Read more.
Activities, particularly harbor construction, often exert significant and non-negligible impacts on coastal environments. Therefore, it is of great practical importance to quantitatively assess the effects of such construction on the surrounding topography, such as tidal flats. This study focuses on the coast of Jiangsu Binhai Harbor. Using multi-source and multi-temporal remote sensing images, digital elevation models of tidal flats surrounding Binhai Harbor were generated for the years 2013, 2015, and 2017 through the waterline method. A quantitative analysis was conducted utilizing GIS spatial analysis techniques to examine erosion–deposition patterns, contour changes, and typical cross-sectional comparisons. The findings reveal that, although the overall coastline is in a state of erosion, the localized impacts of harbor construction are evident. Between 2013 and 2017, the northern tidal flats experienced overall erosion, whereas deposition occurred near the harbor’s root areas. Compared to 2013–2015, there was a significant decrease in erosion between 2015 and 2017, indicating that the construction of the project had a significant impact on the northern tidal flats. Throughout the five-year study period, the tidal flats within the breakwater underwent continuous adjustment, shifting from being close to the shoreline to being concentrated on both sides of the breakwater. Significant siltation was observed on the inner side of the breakwater at Binhai Harbor between 2015 and 2017, with an increase of 0.86 km2 in the area above −2 m. This study demonstrates that remote sensing technology is highly effective in monitoring changes in coastal topography, especially under the influence of human activities. Full article
(This article belongs to the Special Issue Coastal Hydrodynamic and Morphodynamic Processes)
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<p>Study area and distribution of tidal flats around the Binhai harbor.</p>
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<p>Remote sensing images in this study (false color composite image).</p>
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<p>Waterlines in different tide conditions (<b>a</b>) in low tide; (<b>b</b>) in middle tide; (<b>c</b>) in high tide.</p>
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<p>(<b>a</b>) waterlines and DEM in 2013; (<b>b</b>) waterlines and DEM in 2015; (<b>c</b>) waterlines and DEM in 2017.</p>
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<p>Maps of erosion−deposition distribution at different periods of time (<b>a</b>) 2015−2013; (<b>b</b>) 2017–2015.</p>
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<p>Comparison of different contour lines (<b>a</b>) 0 m; (<b>b</b>) −1 m; (<b>c</b>) −2 m.</p>
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<p>Elevation comparison curves for different sections.</p>
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<p>Comparison of different DEM and tidal flats area; (<b>a</b>) 2013DEM; (<b>b</b>) 2015DEM; (<b>c</b>) 2017DEM; (<b>d</b>) tidal flats area in 2013; (<b>e</b>) tidal flats area in 2015; (<b>f</b>) tidal flats area in 2017.</p>
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<p>Comparison of different DEM and contour lines (<b>a</b>) 2013, 2015, and 2017 DEM; (<b>b</b>) −2 m contours in Eran; (<b>c</b>) −2 m contours in Moon Bay.</p>
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<p>Remote sensing images and historical shoreline conditions on both sides of the abandoned Yellow River estuary: (<b>a</b>) historical shorelines and underwater delta; (<b>b</b>) comparison of the distribution of mudflats (at maximum low tide).</p>
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22 pages, 13321 KiB  
Article
Particle Movement in DEM Models and Artificial Neural Network for Validation by Using Contrast Points
by Barbora Černilová, Jiří Kuře, Rostislav Chotěborský and Miloslav Linda
Technologies 2024, 12(12), 257; https://doi.org/10.3390/technologies12120257 - 12 Dec 2024
Viewed by 348
Abstract
The calibration and validation of input parameters in the Discrete Element Method (DEM) are crucial for accurately simulating physical processes, typically achieved through experimental particle behavior analysis. Enhancing the accuracy of DEM models allows for more reliable predictions of material behavior, which is [...] Read more.
The calibration and validation of input parameters in the Discrete Element Method (DEM) are crucial for accurately simulating physical processes, typically achieved through experimental particle behavior analysis. Enhancing the accuracy of DEM models allows for more reliable predictions of material behavior, which is essential for optimizing engineering applications that involve particulate materials. In this study, we present a methodology for analyzing the movement properties of particulate materials, employing a combination of Caliscope software to obtain the real-world co-ordinates based on pixel values from both cameras and artificial neural networks for regression as straightforward and efficient tools. This approach enables the validation and calibration of digital twins of particulate matter systems with respect to motion characteristics. The method of contrast points was utilized to acquire spatial co-ordinates of particulate material movement from experimental measurements, facilitating precise trajectory determination and the subsequent verification of simulation predictions. The neural network analysis demonstrated high accuracy, achieving R2 values of 0.9988, 0.9972, and 0.9982 for the X–, Y–, and Z–axes, respectively. The standard deviation between the predicted and actual co-ordinates was found to be 1.8 mm. A comparative analysis of particle trajectories from both the model and experimental data indicated strong agreement, underscoring the soundness and reliability of this approach. Full article
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<p>The ChArUco chessboard pattern was used to obtain the intrinsic camera parameters. The image was captured from the side camera in the Caliscope software. The reference points were highlighted in red within the software.</p>
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<p>Location of GoPro cameras within the sand box. Cam 1 refers to the side camera and cam 2 refers to the front camera.</p>
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<p>The ChArUco chessboard pattern was used to obtain extrinsic camera parameters in the sand box. (<b>a</b>) The side camera view on the ChArUco chessboard pattern; (<b>b</b>) the front camera view on the ChArUco chessboard pattern.</p>
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<p>The arrangement of particles on the surface of the sand in the sand box. The particles were arranged with a distance of 50 mm between each other. The particles were labeled with numbers 1 to 8 for better identification in the future.</p>
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<p>To obtain trajectories from the video recordings, the Tracker tool was utilized. (<b>a</b>) Selected cluster of pixels for tracing Particle 1. (<b>b</b>) Particle paths from the side camera view after Tracker tool processing.</p>
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<p>The world co-ordinate system and camera co-ordinate system. View from side camera and front camera.</p>
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<p>The rotation around the Z–axis. The original co-ordinate system is presented by x<sub>2</sub>, y<sub>2</sub> (solid lines) and the new co-ordinate system is presented by x, y (dotted lines).</p>
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<p>Three-dimensional model of the sand box walls and tillage tool for import into Ansys Rocky.</p>
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<p>The particles were of two sizes: (<b>a</b>) the upper layer of particles contained 2-mm particles (shown by the blue inlet box); (<b>b</b>) the lower particle layer contained 10-mm particles (shown by the blue inlet box).</p>
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<p>3D chart illustrating the trajectories of the particles with number: 1, 2, 3, 5, 6, 7, and 8.</p>
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<p>Comparison of particle trajectories 5, 6, 7, and 8.</p>
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<p>Comparison between the experimental sand pile and the results from the Ansys Rocky script of the model number 40.</p>
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<p>The comparison of the verified particle system during tillaging (<b>a</b>) from the experiment (with contrast points in the sand) and (<b>b</b>) the result of its digital twin (colored based on particle height in the Y axis for better comprehensibility).</p>
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<p>Comparison of the trajectory of particle 7 in the Y– and Z–axes with the particles from Ansys Rocky.</p>
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<p>Comparison of the trajectory of particle 7 in the X– and Z–axes with the particles from Ansys Rocky.</p>
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<p>Comparison of the trajectory of particle 8 in the Y– and Z–axes with the particles from Ansys Rocky.</p>
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<p>Comparison of the trajectory of particle 8 in the X– and Z–axes with the particles from Ansys Rocky.</p>
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19 pages, 8503 KiB  
Article
Using Random Forest Regression to Model the Spatial Distribution of Concentrations of Selected Metals in Groundwater in Forested Areas of the Wielkopolska National Park, Poland
by Michał Fiedler
Forests 2024, 15(12), 2191; https://doi.org/10.3390/f15122191 - 12 Dec 2024
Viewed by 220
Abstract
Monitoring groundwater pollution is an important issue in terms of analyzing threats to protected, environmentally valuable areas. The topographical and environmental characteristics of a given area are often mentioned among the factors affecting the dynamics and chemistry of groundwater. In this study, the [...] Read more.
Monitoring groundwater pollution is an important issue in terms of analyzing threats to protected, environmentally valuable areas. The topographical and environmental characteristics of a given area are often mentioned among the factors affecting the dynamics and chemistry of groundwater. In this study, the random forest regression (RFR) model was used to determine the spatial distribution of selected metals, such as aluminum, calcium, iron, potassium, magnesium, manganese, sodium, and zinc. In the role of indicators describing terrain variability, derivatives of the digital elevation model (DEM) were employed, with a spatial resolution of 5 m, describing the topography of the terrain on a local scale, such as, among others, slopes, the aspect and curvatures of slopes, the topographic position index, and the SAGA wetness index, as well as generalized values determined for each sampling point of the areas contributing their runoff. In addition, environmental parameters were taken into consideration: forest habitat types, the structure of soil cover, and the seasons when samples were collected. This study used samples collected from 15 wells located in forested areas of the Wielkopolska National Park on seven dates. The results obtained show that random forest can be used with very good results to model the spatial variability of the concentrations of aluminum, potassium, magnesium, manganese, and sodium in groundwater. However, in the case of calcium and zinc, no correlations were found between the adopted indicators describing the spatial variability of the area and their concentrations in groundwater. In addition, the degree of importance of each predictor was determined in order to rank their importance in modeling the concentration of each of the metals in groundwater. The summary ranking of predictors indicates that the strongest influence on the predicted concentration of metals in groundwater is exhibited by profile curvatures, planar curvatures, multiscale TPI, and then the habitat type of the forest. On the other hand, curvature classifications, soil composition, and seasonality exhibit the smallest generalized impact on the results of modeling. Full article
(This article belongs to the Special Issue Soil Pollution and Remediation of Forests Soil)
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<p>Location and DEM of the Wielkopolski Park Narodowy.</p>
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<p>Workflow for analysis of a single metal, using aluminum as an example. Part A is common to all metals.</p>
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<p>Topography of WPN.</p>
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<p>Topography of WPN. TPI Landforms: 1—streams, 2—midslope drainages, 3—upland drainages, 4—valleys, 5—plains, 6—open slopes, 7—upper slopes, 8—local ridges, 9—midslope ridges, 10—high ridges. Curvature class: 0—concave, 1—flat, 2—convex.</p>
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<p>Forest habitat types (FHT) and soil types. FHT: BMsw—fresh mixed coniferous forest, Bsw—fresh coniferous forest, LMsw—fresh mixed broadleaved forest, LMw—moist mixed broadleaved forest, LMb—swamp mixed broadleaved forest, Lsw—fresh broadleaved forest, Lw—moist broadleaved forest, Lł—riparian forest, Ol—alder and alder–ash forest; soil: gs—medium clay, gp—sandy loam, pg—clay sand, pl—loose sand, ps—light clay sand, płp—sandy silt, m—alluvia, tn—turf.</p>
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<p>Correlation between measured and predicted values of metal concentrations in the groundwater.</p>
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<p>Plot showing the importance of variables.</p>
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<p>Summarized importance of variables.</p>
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<p>Predicted concentrations of Al, Fe, and K in the groundwater.</p>
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<p>Predicted concentrations of Mn, Na, and Mg in the groundwater.</p>
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27 pages, 3310 KiB  
Article
Evaluation of Correction Algorithms for Sentinel-2 Images Implemented in Google Earth Engine for Use in Land Cover Classification in Northern Spain
by Iyán Teijido-Murias, Marcos Barrio-Anta and Carlos A. López-Sánchez
Forests 2024, 15(12), 2192; https://doi.org/10.3390/f15122192 - 12 Dec 2024
Viewed by 390
Abstract
This study examined the effect of atmospheric, topographic, and Bidirectional Reflectance Distribution Function (BRDF) corrections of Sentinel-2 images implemented in Google Earth Engine (GEE) for use in land cover classification. The study was carried out in an area of complex orography in northern [...] Read more.
This study examined the effect of atmospheric, topographic, and Bidirectional Reflectance Distribution Function (BRDF) corrections of Sentinel-2 images implemented in Google Earth Engine (GEE) for use in land cover classification. The study was carried out in an area of complex orography in northern Spain and made use of the Spanish National Forest Inventory plots and other systematically located plots to cover non-forest classes. A total of 2991 photo-interpreted ground plots and 15 Sentinel-2 images, acquired in summer at a spatial resolution of 10–20 m per pixel, were used for this purpose. The overall goal was to determine the optimal level of image correction in GEE for subsequent use in time series analysis of images for accurate forest cover classification. Particular attention was given to the classification of cover by the major commercial forest species: Eucalyptus globulus, Eucalyptus nitens, Pinus pinaster, and Pinus radiata. The Second Simulation of the Satellite Signal in the Solar Spectrum (Py6S) algorithm, used for atmospheric correction, provided the best compromise between execution time and image size, in comparison with other algorithms such as Sentinel-2 Level 2A Processor (Sen2Cor) and Sensor Invariant Atmospheric Correction (SIAC). To correct the topographic effect, we tested the modified Sun-canopy-sensor topographic correction (SCS + C) algorithm with digital elevation models (DEMs) of three different spatial resolutions (90, 30, and 10 m per pixel). The combination of Py6S, the SCS + C algorithm and the high-spatial resolution DEM (10 m per pixel) yielded the greatest precision, which demonstrated the need to match the pixel size of the image and the spatial resolution of the DEM used for topographic correction. We used the Ross-Thick/Li-Sparse-Reciprocal BRDF to correct the variation in reflectivity captured by the sensor. The BRDF corrections did not significantly improve the accuracy of the land cover classification with the Sentinel-2 images acquired in summer; however, we retained this correction for subsequent time series analysis of the images, as we expected it to be of much greater importance in images with larger solar incidence angles. Our final proposed dataset, with image correction for atmospheric (Py6S), topographic (SCS + C), and BRDF (Ross-Thick/Li-Sparse-Reciprocal BRDF) effects and a DEM of spatial resolution 10 m per pixel, yielded better goodness-of-fit statistics than other datasets available in the GEE catalogue. The Sentinel-2 images currently available in GEE are therefore not the most accurate for constructing land cover classification maps in areas with complex orography, such as northern Spain. Full article
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<p>Workflow adopted in this study to analyze different combinations of Sentinel-2 imagery corrections. In Algorithm_AT00B, Algorithm_ is the name or abbreviation of the algorithm used, A denotes “atmospheric correction”, T “topographic correction”, the number 00 refers to the spatial resolution of the digital elevation model (DEM) (90, 30, and 10 m per pixel, respectively) and B refers to “application of BRDF correction”. The datasets are shown in three different colours: datasets available in the GEE repository, in blue, the dataset developed in Sentinel Application Platform—SNAP 11.0.0 and uploaded in GEE assets, in purple; and the Level 1 C datasets derived from the GEE platform, in orange. In all cases, the Random Forest algorithm was used for fitting each processing dataset.</p>
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<p>Overview of (<b>a</b>) the location of the study area overlapping the Spanish National Forest Inventory plots used in this study, (<b>b</b>) Sentinel-2 granules for the study area, and (<b>c</b>) location of the region of interest in northern Spain. WGS 84/UTM zone 29N (EPSG: 32629).</p>
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<p>Visual comparison into the 4 datasets.</p>
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<p>Box plots of the overall accuracy (Accuracy) of the whole land cover classification corresponding to different levels of S2 image processing: absence of atmospheric, topographic, or BRDF correction (1C), atmospheric correction with the Sen2Cor algorithm and topographic correction with the Sen2Cor algorithm with DEM of 90 m per pixel (S2C_AT90) and atmospheric correction with the Py6S algorithm, topographic correction with the SCS + C algorithm with DEM of 10 m per pixel and the BRDF correction (Py6S_AT10B). The letters at the top of the box indicate the results of Tukey’s HSD multiple comparison test (different letters indicate significant differences between the difference levels of database processing and/or correction algorithms used).</p>
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16 pages, 3822 KiB  
Article
Cross-Resistance to Pyrethroids and Neonicotinoids in Malaria Vectors from Vegetable Farms in the Northern Benin
by Massioudou Koto Yérima Gounou Boukari, Innocent Djègbè, Ghislain T. Tepa-Yotto, Donald Hessou-Djossou, Genevieve Tchigossou, Eric Tossou, Michel Lontsi-Demano, Danahé Adanzounon, Adam Gbankoto, Luc Djogbénou and Rousseau Djouaka
Trop. Med. Infect. Dis. 2024, 9(12), 305; https://doi.org/10.3390/tropicalmed9120305 - 12 Dec 2024
Viewed by 294
Abstract
Agricultural pesticides may play a crucial role in the selection of resistance in field populations of mosquito vectors. This study aimed to determine the susceptibility level of An. gambiae s.l. to pyrethroids and neonicotinoids in vegetable farms in northern Benin, in West Africa, [...] Read more.
Agricultural pesticides may play a crucial role in the selection of resistance in field populations of mosquito vectors. This study aimed to determine the susceptibility level of An. gambiae s.l. to pyrethroids and neonicotinoids in vegetable farms in northern Benin, in West Africa, and the underlying insecticide resistance mechanisms. A survey on agricultural practices was carried out on 85 market gardeners chosen randomly in Malanville and Parakou. Anopheles gambiae s.l. larvae were collected, reared to adult stages, and identified to species level. Susceptibility was tested with impregnated papers (WHO bioassays) or CDC bottles according to the insecticides. Synergists (PBO, DEM, and DEF) were used to screen resistance mechanisms. Allelic frequencies of the kdr (L1014F), kdr (L1014S), N1575Y, and ace-1R G119S mutations were determined in mosquitoes using Taqman PCR. Fertilizers and pesticides were the agrochemicals most used with a rate of 97.78% and 100%, respectively, in Malanville and Parakou. Anopheles coluzzii was the predominant species in Malanville, while An. gambiae was the only species found in Parakou. Bioassays revealed a high resistance of An. gambiae s.l. to pyrethroids and DDT, while a susceptibility to bendiocarb, pyrimiphos-methyl, malathion, and clothianidin was recorded. Resistance to acetamiprid was suspected in mosquitoes from both localities. A lower resistance level was observed when mosquitoes were pre-treated with synergists, then exposed to insecticides. The kdr L1014F mutation was observed in both locations at moderate frequencies (0.50 in Malanville and 0.55 in Parakou). The allelic frequencies of N1575Y and G119S were low in both study sites. This study confirmed the resistance of An. gambiae s.l. to insecticides used in agriculture and public health. It reveals a susceptibility of vectors to bendiocarb, pyrimiphos-methyl, malathion, and clothianidin, thus indicating that these insecticides can be used as an alternative in Benin to control malaria vectors. Full article
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<p>Mapping showing the study sites.</p>
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<p>Use of chemicals by market gardeners in Malanville and Parakou.</p>
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<p>Mortality rate of <span class="html-italic">An. gambiae</span> s.l. from Malanville and Parakou exposed to neonicotinoids. Results are average percentage of mortalities from four replicates. N represents number of mosquitoes tested by insecticide. Error bar represents standard deviation, and ns means no significance with Mann–Whitney test.</p>
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<p>Insecticide resistance status of <span class="html-italic">An. gambiae</span> s.l. from Malanville and Parakou. Results are average percentage of mortalities from four replicates. N represents number of mosquitoes tested by insecticide. Error bars represent standard deviation. ns means no significance with Mann–Whitney test. * means a significant difference between the insecticide (Mann–Whitney test).</p>
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<p>Bioassay with synergists combined with imidacloprid in <span class="html-italic">An. gambiae</span> s.l. collected from Malanville. Results are average percentage of mortalities from four replicates. n represent number of mosquitoes tested by insecticide. Error bar represent standard deviation. The stars (*) represent the significance level and ns means no significance. Green sticks represent insecticides and grey sticks represent synergists.</p>
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<p>WHO bioassays showing the efficacy of insecticide in Malanville (<b>a</b>) and Parakou (<b>b</b>) with and without pre-exposure to the synergists (error bar represents standard deviations). n = number of mosquitoes tested by insecticide. The stars (*) represent significance level and ns means no significance. Green sticks represent insecticides and grey sticks represent synergists.</p>
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11 pages, 4179 KiB  
Proceeding Paper
A Methodology for Predicting the Stability Trend of Ground Collapse Under the Water Flow
by Qinglun He, Yizhao Wang, Wenfeng Bai, Fei Wang, Xing Min, Zhi Wang, Long Chen, Juncai Jiang and Yuming Qiao
Proceedings 2024, 110(1), 23; https://doi.org/10.3390/proceedings2024110023 - 12 Dec 2024
Viewed by 187
Abstract
Ground collapse is one of the common geological hazards in modern cities. With the development of urbanization, the risk of ground collapse increases, which has a great impact on urban public safety. Ground collapse accidents typically occur due to the presence of unstable [...] Read more.
Ground collapse is one of the common geological hazards in modern cities. With the development of urbanization, the risk of ground collapse increases, which has a great impact on urban public safety. Ground collapse accidents typically occur due to the presence of unstable cavities under the surface, or the generation and expansion of cavities induced by triggering factors. Investigating the stability of cavities in the strata is significant for identifying subsidence risks and mitigating the consequences of subsidence. This study proposed a method for predicting ground subsidence settlement based on the ARMA model. Firstly, CFD-DEM coupled simulation is employed to simulate the mechanism of cavity changes in the soil layers under the influence of triggering factors and to calculate the safety coefficient for ground subsidence stability. Subsequently, the safety coefficient data at different time points are fitted to predict the subsequent stability of the subsidence. We selected a subway permeable collapse accident in Foshan City, Guangdong Province for experimental verification, and compared the predicted results with the actual situation. The result shows that this method can effectively predict the changes in ground collapse safety factor and the collapse time point. With 40% of the data, high accuracy prediction can be achieved, improving the efficiency of collapse evolution prediction and providing strong support for ground collapse risk prevention and control. Full article
(This article belongs to the Proceedings of The 31st International Conference on Geoinformatics)
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<p>Method process.</p>
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<p>Diagram for stability analysis of soil cave mechanics.</p>
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<p>Accident site.</p>
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<p>Ground collapse model. (<b>a</b>) DEM module; (<b>b</b>) CFD module.</p>
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<p>Particle velocity (<b>left</b>) and displacement (<b>right</b>) at each time point. (<b>a</b>) t = 0.2 s; (<b>b</b>) t = 0.6 s; (<b>c</b>) t = 1.0.</p>
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<p>Development of safety coefficient.</p>
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<p>Autocorrelation function and partial autocorrelation function.</p>
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<p>Fitting results. (<b>a</b>) Simulate with 20% data; (<b>b</b>) Simulate with 40% data; (<b>c</b>) Simulate with 60% data.</p>
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17 pages, 4024 KiB  
Article
Anaplastic Lymphoma Kinase (ALK) Inhibitors Enhance Phagocytosis Induced by CD47 Blockade in Sensitive and Resistant ALK-Driven Malignancies
by Federica Malighetti, Matteo Villa, Mario Mauri, Simone Piane, Valentina Crippa, Ilaria Crespiatico, Federica Cocito, Elisa Bossi, Carolina Steidl, Ivan Civettini, Chiara Scollo, Daniele Ramazzotti, Carlo Gambacorti-Passerini, Rocco Piazza, Luca Mologni and Andrea Aroldi
Biomedicines 2024, 12(12), 2819; https://doi.org/10.3390/biomedicines12122819 - 12 Dec 2024
Viewed by 297
Abstract
Background: Anaplastic lymphoma kinase (ALK) plays a role in the development of lymphoma, lung cancer and neuroblastoma. While tyrosine kinase inhibitors (TKIs) have improved treatment outcomes, relapse remains a challenge due to on-target mutations and off-target resistance mechanisms. ALK-positive (ALK+) tumors can evade [...] Read more.
Background: Anaplastic lymphoma kinase (ALK) plays a role in the development of lymphoma, lung cancer and neuroblastoma. While tyrosine kinase inhibitors (TKIs) have improved treatment outcomes, relapse remains a challenge due to on-target mutations and off-target resistance mechanisms. ALK-positive (ALK+) tumors can evade the immune system, partly through tumor-associated macrophages (TAMs) that facilitate immune escape. Cancer cells use “don’t eat me” signals (DEMs), such as CD47, to resist TAMs-mediated phagocytosis. TKIs may upregulate pro-phagocytic stimuli (i.e., calreticulin, CALR), suggesting a potential therapeutic benefit in combining TKIs with an anti-CD47 monoclonal antibody (mAb). However, the impact of this combination on both TKIs-sensitive and resistant ALK+ tumors requires further investigation. Methods: A panel of TKIs-sensitive and resistant ALK+ cancer subtypes was assessed for CALR and CD47 expression over time using flow cytometry. Flow cytometry co-culture and fluorescent microscopy assays were employed to evaluate phagocytosis under various treatment conditions. Results: ALK inhibitors increased CALR expression in both TKIs-sensitive and off-target resistant ALK+ cancer cells. Prolonged TKIs exposure also led to CD47 upregulation. The combination of ALK inhibitors and anti-CD47 mAb significantly enhanced phagocytosis compared to anti-CD47 alone, as confirmed by flow cytometry and fluorescent microscopy. Conclusions: Anti-CD47 mAb can quench DEMs while exposing pro-phagocytic signals, promoting tumor cell phagocytosis. ALK inhibitors induced immunogenic cell damage by upregulating CALR in both sensitive and off-target resistant tumors. Continuous TKIs exposure in off-target resistant settings also resulted in the upregulation of CD47 over time. Combining TKIs with a CD47 blockade may offer therapeutic benefits in ALK+ cancers, especially in overcoming off-target resistance where TKIs alone are less effective. Full article
(This article belongs to the Special Issue Drug Resistance and Novel Targets for Cancer Therapy—Second Edition)
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<p>Surface expression of calreticulin (CALR) after tyrosine kinase inhibitors (TKIs) exposure in both sensitive and resistant ALK–positive cancer subtypes. (<b>A</b>) Representative flow cytometry plot of CALR+/7–AAD- cell population in SUP-M2 cell line, after exposure to crizotinib (0.5 µM) and lorlatinib (0.1 µM) for 20 h, compared to negative control (untreated, UT). (<b>B</b>) Representative histogram bars in terms of percentages of CALR<sup>+</sup>/7–AAD<sup>−</sup> population for each ALK-positive cancer cell lines available in institution, after exposure to different TKIs for 20 h. (<b>C</b>) Expression of CALR in sensitive and lorlatinib–resistant lung adenocarcinoma cell line H3122 after 20 h and 8 days of alectinib and lorlatinib exposure, respectively, (left and middle panels, alectinib 20 h: 2 µM; alectinib 8 days: 200 nM; lorlatinib 20 h and 8 days: 0.1 µM) and CALR expression in resistant neuroblastoma cell line (CLB-Ga-LR1000) after exposure to lorlatinib (1.0 µM) for 20 h and long exposure at day +8 (C, right panel). (<b>D</b>) CALR expression over time in K299 cell line after long exposure to crizotinib (120 nM) compared to the untreated setting (one-way ANOVA with multiple comparisons correction; K299 <span class="html-italic">F</span><sub>(2,6)</sub> = 16.98, SUP-M2 <span class="html-italic">F</span><sub>(2,6)</sub> = 25.36, AS4 <span class="html-italic">F</span><sub>(2,6)</sub> = 18.06, H3122 <span class="html-italic">F</span><sub>(2,6)</sub> = 6.323, H3122-LR100 <span class="html-italic">F</span><sub>(3,8)</sub> = 9.213, CLB-Ga-LR1000 <span class="html-italic">F</span><sub>(2,6)</sub> = 92.04, K299 <sub>CRIZO_120 nM</sub> <span class="html-italic">F</span><sub>(3,8)</sub> = 42.55, K299 <sub>CALR+DAY7</sub> <span class="html-italic">F</span><sub>(2,12)</sub> = 26.39, K299 <sub>CALR+DAY9</sub> <span class="html-italic">F</span><sub>(2,12)</sub> = 7.307, K299 <sub>CALR+DAY11</sub> <span class="html-italic">F</span><sub>(1,12)</sub> = 35.79; experimental triplicates; ns: not significant; * <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001, **** <span class="html-italic">p</span> &lt; 0.0001).</p>
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<p>CD47 surface expression after exposure to TKIs in sensitive and off-target resistant ALK-positive cell lines. (<b>A</b>–<b>F</b>) CD47 surface expression, analyzed using flow cytometry, in lymphoma cell line K299, AS4 cell line, lung cancer cell line H3122 (sensitive to alectinib and resistant to lorlatinib) and neuroblastoma cell line CLB-Ga-LR1000, according to TKIs used; two-way ANOVA with multiple comparisons correction, K299 <span class="html-italic">F</span><sub>(1,32)</sub> = 12.29, AS4<sub>CRIZO</sub> <span class="html-italic">F</span><sub>(1,8)</sub> = 52.08, AS4<sub>LORLA</sub> <span class="html-italic">F</span><sub>(1,8)</sub> = 182.8, H3122 <span class="html-italic">F</span><sub>(1,7)</sub> = 348.5, H3122<sub>LORLA</sub> <span class="html-italic">F</span><sub>(1,8)</sub> = 24.54; experimental triplicates; ns: not significant; * <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01, **** <span class="html-italic">p</span> &lt; 0.0001; for CLB-Ga-LR1000: unpaired, one-tailed Student’s <span class="html-italic">t</span>-test, * <span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Extended analysis of increased phagocytosis in a panel of ALK-positive tumor cell lines, treated with anti-CD47 mAb, previously exposed to ALKi. (<b>A</b>,<b>B</b>) Histogram analysis of phagocytic rate in ALK-positive lymphoma sensitive (K299, SUP-M2) and resistant (AS4) setting, previously exposed to crizotinib or lorlatinib, treated with anti-CD47 mAb (<b>A</b>); crizotinib 0.5 µM, lorlatinib 0.1 µM). (<b>C</b>) Histogram analysis of phagocytic rate in off-target resistant ALK-driven solid cancer cell lines (H3122-LR100, CLB-Ga-LR1000. One-way ANOVA with multiple comparisons correction; K299<sub>CRIZO</sub> <span class="html-italic">F</span><sub>(3,8)</sub> = 34.39, K299<sub>LORLA</sub> <span class="html-italic">F</span><sub>(3,8)</sub> = 49.50, SUP-M2<sub>CRIZO</sub> <span class="html-italic">F</span><sub>(3,8)</sub> = 3.932, SUP-M2<sub>LORLA</sub> <span class="html-italic">F</span><sub>(3,8)</sub> = 12.16, AS4<sub>CRIZO</sub> <span class="html-italic">F</span><sub>(3,8)</sub> = 8.794, AS4<sub>LORLA</sub> <span class="html-italic">F</span><sub>(3,8)</sub> = 9.344, H3122-LR100<sub>LORLA</sub> <span class="html-italic">F</span><sub>(3,8)</sub> = 17.07; CLB-Ga-LR1000<sub>LORLA</sub> <span class="html-italic">F</span><sub>(2,6)</sub> = 102.2; experimental triplicates, <span class="html-italic">n</span> = 3 donors; ns: not significant; * <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001, **** <span class="html-italic">p</span> &lt; 0.0001).</p>
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<p>Fluorescent microscopy after incubation of human macrophages with anti-CD47 mAb and the ALK-positive lymphoma AS4 cell line, previously exposed to crizotinib or lorlatinib. (<b>A</b>) Representative images of fluorescent microscopy where Hoechst 33342<sup>+</sup> macrophages were incubated with anti-CD47 mAb and the ALK-positive lymphoma AS4 cell line, labeled with the pH-sensitive dye pHrodo-Red and previously exposed to crizotinib (0.5 µM) or lorlatinib (100 nM) for 20 h. (<b>B</b>) Representative histogram bars of phagocytic index (number of pHrodo-red<sup>+</sup> tumoral cells per 100 macrophages) in case of combination of anti-CD47 mAb and lorlatinib treatment (one-way ANOVA with multiple comparisons correction; AS4 <span class="html-italic">F</span><sub>(5,12)</sub> = 275.6; technical triplicate; <span class="html-italic">n</span> = 1 donor, one experimental cohort; ns: not significant; **** <span class="html-italic">p</span> &lt; 0.0001).</p>
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16 pages, 8293 KiB  
Article
Research on the Calibration Method of the Bonding Parameters of the EDEM Simulation Model for Asphalt Mixtures
by Xiujun Li, Zhipeng Zhang, Linhao Zhao, Heng Zhang and Fangzhi Shi
Coatings 2024, 14(12), 1553; https://doi.org/10.3390/coatings14121553 - 11 Dec 2024
Viewed by 355
Abstract
To enhance the accuracy and reliability of the discrete element simulation software EDEM 2023 for pavement asphalt mixture simulation, three representative coarse aggregate particles were modeled in 3D using the SolidWorks 2018 software and imported into the EDEM 2023 software for particle filling. [...] Read more.
To enhance the accuracy and reliability of the discrete element simulation software EDEM 2023 for pavement asphalt mixture simulation, three representative coarse aggregate particles were modeled in 3D using the SolidWorks 2018 software and imported into the EDEM 2023 software for particle filling. The Hertz–Mindlin with bonding contact model was used to construct the EDEM simulation model of asphalt mixtures, and the quadratic regression model of asphalt mixtures’ splitting tensile strength and four bonding parameters, namely, normal stiffness per unit area, shear stiffness per unit area, critical normal stress, and critical shear stress, was found by the response surface methodology. The results show that the relationship between the significance magnitude of the four bonding parameters on the splitting tensile strength of the asphalt mixture simulation model is as follows: critical normal stress > shear stiffness per unit area > normal stiffness per unit area > critical shear stress. The calibration results of the bonding parameters were used for simulation verification, and the relative error between the simulation and actual splitting tensile strength was only −2.48%. The feasibility of this bonding parameter calibration method is demonstrated, and it can lay a foundation for EDEM to simulate the performance of asphalt mixtures on pavements with high-precision simulation. Full article
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<p>Aggregate gradation of asphalt mixture.</p>
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<p>Laboratory splitting test for asphalt mixtures.</p>
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<p>Interaction of the “Bond” between Particle A and Particle B.</p>
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<p>Asphalt mixture mastic theory.</p>
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<p>Marshall specimen mold and particle factory.</p>
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<p>Schematic diagram of Marshall specimen model generation and compaction process.</p>
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<p>Marshall specimen particle size distribution chart by grade.</p>
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<p>The simulation model for the splitting test.</p>
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<p>Response surfaces for the interaction effects of various factors on the splitting tensile strength <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>R</mi> </mrow> <mrow> <mi>T</mi> </mrow> </msub> </mrow> </semantics></math>: (<b>a</b>) interaction effects between <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>1</mn> </mrow> </msub> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>2</mn> </mrow> </msub> </mrow> </semantics></math>; (<b>b</b>) interaction effects between <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>1</mn> </mrow> </msub> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>3</mn> </mrow> </msub> </mrow> </semantics></math>; (<b>c</b>) interaction effects between <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>1</mn> </mrow> </msub> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>4</mn> </mrow> </msub> </mrow> </semantics></math>; (<b>d</b>) interaction effects between <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>2</mn> </mrow> </msub> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>3</mn> </mrow> </msub> </mrow> </semantics></math>; (<b>e</b>) interaction effects between <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>2</mn> </mrow> </msub> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>4</mn> </mrow> </msub> </mrow> </semantics></math>; (<b>f</b>) interaction effects between <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>3</mn> </mrow> </msub> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>4</mn> </mrow> </msub> </mrow> </semantics></math>.</p>
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<p>The variation in the load applied by the upper compression bar and the fracture state of the specimen over time.</p>
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23 pages, 28195 KiB  
Article
Slow-Moving Landslide Hazard Assessment Using LS-Unilab Deep Learning Model with Highlighted InSAR Deformation Signal
by Xiangyang Li, Peifeng Ma, Song Xu, Hong Zhang, Chao Wang, Yukun Fan and Yixian Tang
Remote Sens. 2024, 16(24), 4641; https://doi.org/10.3390/rs16244641 - 11 Dec 2024
Viewed by 350
Abstract
Slow-moving landslides are often precursors of catastrophic failure, posing a major threat to human life and property safety. Interferometric synthetic aperture radar (InSAR) has become a crucial tool for investigating slow-moving landslides hazard because of its high-precision detection capability for slow surface deformation. [...] Read more.
Slow-moving landslides are often precursors of catastrophic failure, posing a major threat to human life and property safety. Interferometric synthetic aperture radar (InSAR) has become a crucial tool for investigating slow-moving landslides hazard because of its high-precision detection capability for slow surface deformation. However, landslides usually occur in alpine canyon areas and vegetation coverage areas where InSAR measurements are still limited by temporal and spatial decorrelation and atmospheric influences. In addition, there are several difficulties in monitoring the multiscale characterization of landslides from the InSAR results. To address this issue, this paper proposes a novel method for slow-moving landslide hazard assessment in low-coherence regions. A window-based atmosphere correction method is designed to highlight the surface deformation signals of InSAR results in low-coherence regions and reduce false alarms in landslide hazard assessment. Then, the deformation annual velocity rate map, coherence map and DEM are used to construct the InSAR sample set. A landslide hazard assessment model named Landslide-SE-Unilab is subsequently proposed. The global–local relationship aggregation structure is designed to capture the spatial relationship between local pixel-level deformation features and global landslides, which can reduce the number of missed assessments and false assessments of small-scale landslides. Additionally, a squeeze-and-excitation network is embedded to adjust the weight relationship between the features of each channel in order to enhance the performance of network evaluation. The method was evaluated in Kangding city and the Jinsha River Valley in the Hengduan Mountains, where a total of 778 potential landslides with slow deformation were identified. The effectiveness and accuracy of this approach for low-coherence landslide hazard assessment are demonstrated through comparisons with optical images and previous research findings, as well as evaluations via time-series deformation results. Full article
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<p>Flowchart of the proposed technique.</p>
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<p>Flowchart of SBAS-InSAR with a window-based atmospheric correction.</p>
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<p>Flowchart of the sample production process.</p>
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<p>The LS-Unilab model. The deformation annual velocity rate map, coherence map, and DEM are selected for the model input.</p>
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<p>Study area and fault distribution. The black lines represent faults (source: <a href="https://docs.gmt-china.org/latest/dataset-CN/CN-faults/" target="_blank">https://docs.gmt-china.org/latest/dataset-CN/CN-faults/</a>, accessed on 16 May 2024). The red dots denote the earthquake locations since 2008 (source: <a href="https://data.earthquake.cn/" target="_blank">https://data.earthquake.cn/</a>, accessed on 16 May 2024), and the black boxes represent the Sentinel-1 data coverage used in this work. The background is the SRTM1 DEM (source: <a href="http://step.esa.int/auxdata/dem/SRTMGL1/" target="_blank">http://step.esa.int/auxdata/dem/SRTMGL1/</a>, accessed on 16 May 2024).</p>
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<p>Field photographs of the landslides along the Jinsha River.</p>
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<p>Annual velocity rate of path 26 from Sentinel-1 images from Jan 2022 to Sep 2023 and statistical results, where regions A–D are selected for detailed analysis. (<b>a</b>) The uncorrected results; (<b>b</b>) the elevation correction results; (<b>c</b>) the window based atmospheric correction results; and (<b>d</b>) the statistical results of (<b>a</b>,<b>c</b>).</p>
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<p>Annual deformation velocity of Kangding city (<b>a</b>) and the Jinsha River Gorge (<b>b</b>) from Sentinel-1 images from January 2022 to September 2023, where regions I–VI are selected for detailed analysis. (<b>c</b>) Zoomed-in view of area IV in (<b>b</b>), where the locations of P1–P6 correspond to the field photographs in <a href="#remotesensing-16-04641-f006" class="html-fig">Figure 6</a>. (<b>d</b>,<b>e</b>) (corresponding to areas (4) and (3) in <a href="#remotesensing-16-04641-f009" class="html-fig">Figure 9</a>) Corresponded to regions A and B in black circle of (<b>a</b>); (<b>f</b>,<b>g</b>) (corresponded to areas (2) and (1) in <a href="#remotesensing-16-04641-f009" class="html-fig">Figure 9</a>) Corresponded to regions V and VI in (<b>b</b>).</p>
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<p>Assessment results of slow-moving landslides, where regions in circles are selected for detailed analysis.</p>
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<p>Landslide hazard assessment results and statistical results for Kangding city (<b>a</b>,<b>c</b>) and the Jinsha River Gorge (<b>b</b>,<b>d</b>). The red triangles represent the locations of slow-moving landslides.</p>
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<p>Validation region in Kangding City; (<b>a</b>) Annual deformation rate map; (<b>b</b>) base image of the Sentinel-2 optical image; (<b>c</b>) model identification results; (<b>d</b>) threshold separation results.</p>
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<p>Validation region in the Jinsha River Gorge; (<b>a</b>) annual deformation rate map; (<b>b</b>) base image of the Sentinel-2 optical image; (<b>c</b>) model identification results; (<b>d</b>) threshold separation results.</p>
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<p>The upper background image is a Google Earth image overlaid with deformation rates, with red rectangles indicating the landslide identification results; the lower part shows the time-series deformation results of the monitoring points. (<b>a</b>–<b>d</b>) Areas of verification points in <a href="#remotesensing-16-04641-f010" class="html-fig">Figure 10</a>.</p>
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<p>Compared with other research results, the deformation period time is marked. (<b>a</b>) Results obtained by Zou et al. [<a href="#B45-remotesensing-16-04641" class="html-bibr">45</a>]; (<b>c</b>,<b>d</b>) results obtained by Liu et al. [<a href="#B12-remotesensing-16-04641" class="html-bibr">12</a>,<a href="#B13-remotesensing-16-04641" class="html-bibr">13</a>]; (<b>e</b>) results obtained by Zhang et al. [<a href="#B50-remotesensing-16-04641" class="html-bibr">50</a>]; (<b>b</b>,<b>f</b>) results obtained in the present study; (<b>g</b>–<b>k</b>) the Sentinel-2 optical imagery of areas delineated by black rectangles in (<b>f</b>). Red circels are selected for detailed analysis. The legend of the original text in the figure was redrawn.</p>
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16 pages, 6779 KiB  
Article
Evaluation of Mixing Process in Batch Mixer Using CFD-DEM Simulation and Automatic Post-Processing Method
by Guangming Li, Zhenbang Zhang, Jiahong Xiang, Haili Zhao, Feng Jiao, Tao Chen and Guo Li
Processes 2024, 12(12), 2840; https://doi.org/10.3390/pr12122840 - 11 Dec 2024
Viewed by 309
Abstract
A batch mixer is an important piece of equipment for polymer filling modification, and the kinematics of agglomerate breakup and distribution are necessary for the structure design and mixing process optimization of the rotor, particularly in light of the cohesive forces that exist [...] Read more.
A batch mixer is an important piece of equipment for polymer filling modification, and the kinematics of agglomerate breakup and distribution are necessary for the structure design and mixing process optimization of the rotor, particularly in light of the cohesive forces that exist within the agglomerate. In this paper, computational fluid dynamics (CFD) was coupled with discrete element method (DEM) to simulate the mixing process, including breakup and distribution, which was further quantitatively evaluated by the post-processing involving numerical method. To study the mixing process of an agglomerate composed of massive spherical particles (individual particle ratio was r), the coordinates of the particles were exported from the CFD-DEM simulation results. Then, the coordinate data were automatically processed with an automate custom-built post-processing program to obtain the average radius of gyration (Rgy) and the particle distribution density (ε). The kinematics analyzation of breakup and distribution was represented by curve of Rgy/r versus mixing time (t) and curve of ε versus t, respectively. The value of Rgy/r and ε decreased over time until they reached an equilibrium and vibrated around a certain value. In particular, a notable decline in the value of Rgy/r was observed following an increase prior to critical time. The increase in Rgy/r stated that the agglomerate or aggregates undergo stretching deformation. Additionally, mixing processes of rotors with different pressurization coefficients (S) and rotation speeds could be facilitated and intensified by large S and high rotation speed. Finally, a “breakup-line” was developed by considering the influence of cohesive force and rotation speed on the agglomerate breakup process. The agglomerate could be broken if the combination of rotation speed and bonding strength was above the “breakup line”, otherwise the agglomerate was not broken. Furthermore, rotors with larger slopes exhibited stronger breakup ability. Full article
(This article belongs to the Section Automation Control Systems)
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<p>Description for the adhesive contact model.</p>
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<p>The configuration and meshing for batch mixer: (<b>a</b>) flow domain; (<b>b</b>) rotor; (<b>c</b>) slide meshing; (<b>d</b>) grid independence verification, rotation speed is 28.7 r/min.</p>
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<p>Calculating procedure schemes for <span class="html-italic">R<sub>gyA</sub></span> and <span class="html-italic">ε</span>.</p>
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<p>Flow characterize of TYPE1, TYPE2 and TYPE3 rotor: (<b>a</b>–<b>c</b>) velocity vector pictures; (<b>d</b>–<b>f</b>) pressure cloud pictures; (<b>g</b>–<b>i</b>) mixing index cloud picture. Rotor rotational speed was 28.70 r/min, respectively, and rotors had rotated 1/4 revolutions.</p>
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<p>Mixing state of different rotors at (<b>a1</b>–<b>a9</b>) <span class="html-italic">t</span> = 0.955 s, (<b>b1</b>–<b>b9</b>) <span class="html-italic">t</span> = 12.295 s and (<b>c1</b>–<b>c9</b>) <span class="html-italic">t</span> = 20 s; the rotation speeds were 14.35 r/min, 28.7 r/min and 57.4 r/min, respectively; <span class="html-italic">λ</span> = 1.</p>
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<p>The morphology of broken agglomerate after processed with “graph” function at the moment of <span class="html-italic">t</span> = 12.295 s when <span class="html-italic">λ</span> = 1.</p>
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<p>Curves for the <span class="html-italic">R<sub>gyA</sub></span>/<span class="html-italic">r</span> (<span class="html-italic">r</span> was the particle radius) and <span class="html-italic">ε</span> changing with mixing time for different rotors and rotation speeds, and <span class="html-italic">λ</span> = 1.</p>
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<p><span class="html-italic">R<sub>gyA</sub></span>/<span class="html-italic">r</span> and <span class="html-italic">ε</span> versus <span class="html-italic">t</span> curves for TYPE1 rotor under different <span class="html-italic">λ</span>, and the rotation speed was 28.7 r/min.</p>
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<p>Established “breakup-line” for different rotors: (<b>a</b>) type1 rotor; (<b>b</b>) type2 rotor; (<b>c</b>) type3 rotor.</p>
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14 pages, 3544 KiB  
Article
Enhanced Synthesis of Volatile Compounds by UV-B Irradiation in Artemisia argyi Leaves
by Haike Gu, Zhuangju Peng, Xiuwen Kuang, Li Hou, Xinyuan Peng, Meifang Song and Junfeng Liu
Metabolites 2024, 14(12), 700; https://doi.org/10.3390/metabo14120700 - 11 Dec 2024
Viewed by 340
Abstract
Background: Volatile compounds have a deep influence on the quality and application of the medicinal herb Artemisia argyi; however, little is known about the effect of UV-B radiation on volatile metabolites. Methods: We herein investigated the effects of UV-B exposure on the [...] Read more.
Background: Volatile compounds have a deep influence on the quality and application of the medicinal herb Artemisia argyi; however, little is known about the effect of UV-B radiation on volatile metabolites. Methods: We herein investigated the effects of UV-B exposure on the volatile compounds and transcriptome of A. argyi to assess the potential for improving its quality and medicinal characteristics. Results: Out of 733 volatiles obtained, a total of 133 differentially expressed metabolites (DEMs) were identified by metabolome analysis. These were classified into 16 categories, primarily consisting of terpenoids, esters, heterocyclic compounds, alcohols, and ketones. Sensory odor analysis indicated that green was the odor with the highest number of annotations. Among the 544 differentially expressed genes (DEGs) identified by transcriptome analysis, most DEGs were linked to “metabolic pathways” and “biosynthesis of secondary metabolites”. Integrated analysis revealed that volatiles were mainly synthesized through the shikimate pathway and the MEP pathway. RNA-seq and qPCR results indicated that transcription factors HY5, bHLH25, bHLH18, bHLH148, MYB114, MYB12, and MYB111 were upregulated significantly after UV-B radiation, and were therefore considered key regulatory factors for volatiles synthesis under UV-B radiation. Conclusions: These findings not only provide new insights into UV-induced changes in volatile compounds, but also provide an exciting opportunity to enhance medicinal herbs’ value, facilitating the development of products with higher levels of essential oils, flavor, and bioactivity. Full article
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<p>Overview of volatile metabolite changes in <span class="html-italic">A. argyi</span> leaves in response to UV-B radiation. (<b>A</b>) PCA of metabolites. (<b>B</b>) Cluster heatmap of all metabolite contents. The horizontal axis represents the sample name, and the vertical axis represents the metabolite information. Different colors are filled with different values obtained after standardizing the relative content (red represents high content, green represents low content). (<b>C</b>) Volcano plot of DEMs. (<b>D</b>) KEGG enrichment analysis of DEMs. (<b>E</b>) Top 20 upregulated DEMs.</p>
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<p>Odorous compounds analysis. (<b>A</b>) Category and number of DEMs with sensory flavor. (<b>B</b>) Radar chart of sensory flavor characteristics of differential volatile compounds. (<b>C</b>) Correlation network diagram between sensory flavor characteristics and DEMs.</p>
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<p>Overview of transcriptome analysis of <span class="html-italic">A. argyi</span> responsive to UV-B irradiation. (<b>A</b>) PCA analysis of samples taken at 0 h, 4 h, 8 h, and 6 days. (<b>B</b>) Changes in the total number of genes and DEGs. (<b>C</b>) Volcano map of DEGs from the pairwise comparison of UV0 vs. UV6d. (<b>D</b>) Venn graph for up- and downregulated DEGs from the pairwise comparisons of UV0 vs. UV4h, UV0 vs. UV8h, and UV0 vs. UV6d.</p>
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<p>Enrichment analysis of metabolic pathways in comparison of UV0 vs. UV6d. (<b>A</b>) Top 20 enriched GO pathways of DEGs. (<b>B</b>) Top 20 enriched KEGG pathways of DEGs. The color and size of the solid circles represent the significant value of the enrichment factor and the number of transcripts involved in the specific pathway, respectively. (<b>C</b>) Classification of enriched metabolic pathways. The numbers in the figure represent the number of DEGs annotated to this pathway, and the parentheses indicate the ratio of DEGs annotated to this pathway to the number of background genes annotated to this pathway.</p>
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<p>Metabolic analysis of volatile compounds in <span class="html-italic">A. argyi</span> leaves. HK, hexokinase; PFK, 6-phosphofructokinase; PK, pyruvate kinase; MEP, 2-C-methyl-D-erythrin-4-phosphate; IPP, isopentenyl pyrophosphate; DXS, 1-Deoxy-D-xylulose-5-phosphate synthase; DXR, 1-deoxy-d-xylulose-5-phosphate reductoisomerase; CMS, 2-C-methyl-D-erythritol 4-phosphate cytidine synthase; CMK, 2-C-Methyl-D-erythritol 4-phosphate cytidine kinase; MCS, 2-C-methyl-D-erythritol 2,4-cyclodiphosphate synthase; HDS, Hydroxymethylbutene-4-phosphate synthase; HDR, 1-Hydroxy-2-methyl-2 (E)-butenyl-4-diphosphate reductase; GGPPS, geranylgeranyl diphosphate synthases; FPPS, Farnesyl pyrophosphate synthase; Cit2, citrate synthase; Icl, isocitrate lyase; Idh, isocitrate dehydrogenase; Kgd, alpha-ketoglutarate dehydrogenase; Sdh, succinate dehydrogenase; Fum, fumarase; Mdh, malate dehydrogenase; DS, DAHP synthase; DAS, 3-dehydroquinic acid synthase; DAD, 3-dehydroquinic acid dehydratase; SDH, shikimate dehydrogenase; SK, shikimate kinase; ES, EPSP synthase; BAS, branched acid synthase; ICS, isochorismate synthase; PBS3, avrPphB susceptible 3; PAL, phenylalanine ammonia-lyase; C4H, cinnamate4-hydroxylase; 4CL, 4-coumarate-CoA ligase. The results were expressed as mean ± SD of triplicate measurements.</p>
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<p>Transcriptional regulation of volatile compounds induced by UV-B. Gene expression of transcription factors analyzed by RNA-seq (<b>A</b>) and qPCR (<b>B</b>). Red characters indicate the upregulated metabolites. (<b>C</b>) A regulation model of volatile compounds-related genes. Red characters indicate the upregulated genes. Black characters indicate expression with insignificant differences. UVR8, UV Resistance Locus 8; COP1, Constitutively Photomorphogenetic 1; HY5, Elongated Hypocotyl 5.</p>
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18 pages, 5011 KiB  
Article
Design and Testing of a Bionic Seed Planter Furrow Opener for Gryllulus Jaws Based on the Discrete Element Method (DEM)
by Xinming Jiang, Xiaoxuan Wang, Senbo Yang, Yajun Yu, Tianyue Xu and Chunrong Li
Processes 2024, 12(12), 2834; https://doi.org/10.3390/pr12122834 - 11 Dec 2024
Viewed by 389
Abstract
In addition to improving the efficacy of the furrow opener by ensuring consistent seeding depth, the gryllulus jaw geometry curve was integrated into the furrow opener. Soil particles were modeled using the DEM combined with the Hertz–Mindlin with JKR model, and simulation tests [...] Read more.
In addition to improving the efficacy of the furrow opener by ensuring consistent seeding depth, the gryllulus jaw geometry curve was integrated into the furrow opener. Soil particles were modeled using the DEM combined with the Hertz–Mindlin with JKR model, and simulation tests were conducted using the DEM corn stover model. Three geometric curves of gryllulus jaws were extracted. The effect of each curve and magnification on the manipulation results was clarified by the simulation test. Subsequently, field trials were conducted to evaluate the stability of the seeding depth of the bionic structure. The experiment showed that the No. 1 structure with a magnification of 1000 was the best, and the stability was 42.10% higher than that of the original structure. The results of this research can provide key structural and simulation parameters for the development of planter furrow openers with both efficient straw crushing and stable sowing depth functions, which is of great significance for the improvement of agricultural machinery. Full article
(This article belongs to the Section Advanced Digital and Other Processes)
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<p>Structural analysis of gryllulus jaws and results. (<b>a</b>) Electron microscopy results, and (<b>b</b>) the case of the curve.</p>
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<p>Bionic furrow opener profile applications.</p>
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<p>Soil parameter test and simulation processes. (<b>a</b>) Soil particle size, (<b>b</b>) compression test, (<b>c</b>) falling ball test, and (<b>d</b>) Slope test.</p>
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<p>Multi-sphere modeling of soil particles. (<b>a</b>) Single soil particle, (<b>b</b>) 2-sphere models, and (<b>c</b>) 3-sphere models. (<b>d</b>) Corresponding 3D models.</p>
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<p>Soil parameter test and simulation processes. (<b>a</b>) Stacking angle tests, and (<b>b</b>) cone penetration tests.</p>
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<p>Straw size measurement.</p>
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<p>Multi-sphere modeling of straw. (<b>a</b>) Particle model, and (<b>b</b>) bonding model.</p>
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<p>Soil model machining test model. (<b>a</b>) Simulation model, and (<b>b</b>) machining test process.</p>
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<p>Soil model cutting test model.</p>
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<p>Straw bonding model tests. (<b>a</b>) Straw discrete element particle cutting test. (<b>b</b>) Bonding bond cutting test.</p>
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<p>Field experiments with furrow openers.</p>
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<p>Soil-cutting test results.</p>
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<p>Soil seeding process simulation results. (<b>a</b>) Rotation speed of 15, (<b>b</b>) rotation speed of 46, and (<b>c</b>) rotation speed of 78.</p>
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<p>Straw bonding model machining test results.</p>
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<p>Straw bonding model seeding process simulation results. (<b>a</b>) Rotation speed of 15, (<b>b</b>) rotation speed of 46, and (<b>c</b>) rotation speed of 78.</p>
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<p>Experimental results of the field furrow opener experiment.</p>
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35 pages, 19129 KiB  
Article
Mapping Lithology with Hybrid Attention Mechanism–Long Short-Term Memory: A Hybrid Neural Network Approach Using Remote Sensing and Geophysical Data
by Michael Appiah-Twum, Wenbo Xu and Emmanuel Daanoba Sunkari
Remote Sens. 2024, 16(23), 4613; https://doi.org/10.3390/rs16234613 - 9 Dec 2024
Viewed by 557
Abstract
Remote sensing provides an efficient roadmap in geological analysis and interpretation. However, some challenges arise when remote sensing techniques are integrated with machine learning in geological surveys. Factors including irregular spatial distribution, sample imbalance, interclass resemblances, regolith, and geochemical similarities impede geological feature [...] Read more.
Remote sensing provides an efficient roadmap in geological analysis and interpretation. However, some challenges arise when remote sensing techniques are integrated with machine learning in geological surveys. Factors including irregular spatial distribution, sample imbalance, interclass resemblances, regolith, and geochemical similarities impede geological feature diagnosis, interpretation, and identification across varied remote sensing datasets. To address these limitations, a hybrid-attention-integrated long short-term memory (LSTM) network is employed to diagnose, interpret, and identify lithological feature representations in a remote sensing-based geological analysis using multisource data fusion. The experimental design integrates varied datasets including Sentinel-2A, Landsat-9, ASTER, ALOS PALSAR DEM, and Bouguer anomaly gravity data. The proposed model incorporates a hybrid attention mechanism (HAM) comprising channel and spatial attention submodules. HAM utilizes an adaptive technique that merges global-average-pooled features with max-pooled features, enhancing the model’s accuracy in identifying lithological units. Additionally, a channel separation operation is employed to allot refined channel features into clusters based on channel attention maps along the channel dimension. The comprehensive analysis of results from comparative extensive experiments demonstrates HAM-LSTM’s state-of-the-art performance, outperforming existing attention modules and attention-based models (ViT, SE-LSTM, and CBAM-LSTM). Comparing HAM-LSTM to baseline LSTM, the HAM module’s integrated configurations equip the proposed model to better diagnose and identify lithological units, thereby increasing the accuracy by 3.69%. Full article
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<p>An overview of this study’s workflow: The multisource data fusion technique is employed to fuse the gravity anomaly data and remote sensing data. Channel and spatial attention mechanisms are modeled to learn the spatial and spectral information of pixels in the fused data and the resultant attention features, fed into the LSTM network for sequential iterative processing to map lithology.</p>
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<p>Location of study area and regional geological setting. (<b>a</b>) Administrative map of Burkina Faso; (<b>b</b>) administrative map of Bougouriba and Ioba Provinces within which the study area is located; (<b>c</b>) geological overview of Burkina Faso (modified from [<a href="#B44-remotesensing-16-04613" class="html-bibr">44</a>]) indicating the study area; (<b>d</b>) color composite image of Landsat-9 covering the study area.</p>
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<p>False color composite imagery of remote sensing data used: (<b>a</b>) Sentinel-2A (bands 4-3-2); (<b>b</b>) Landsat-9 (bands 4-3-2); (<b>c</b>) ASTER (bands 3-2-1); and (<b>d</b>) 12.5 m spatial resolution high-precision ALOS PALSAR DEM.</p>
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<p>Vegetation masking workflow.</p>
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<p>The HAM structure. It comprises three sequential components: channel attention submodule, feature separation chamber, and spatial attention submodule. One-dimensional and two-dimensional feature maps are produced by the channel and spatial attention submodules, respectively.</p>
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<p>Framework of HAM’s channel attention submodule. Dimensional feature information is generated by both max-pooling and average-pooling operations. The resultant features are then fed through a one-dimensional convolution with a sigmoid activation to deduce the definitive channel feature.</p>
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<p>Framework of HAM’s spatial attention. Two feature clusters of partitioned refined channel features from the separation chamber are fed into the submodule. Average-pooling and max-pooling functions subsequently synthesize two pairs of 2D maps into a shared convolution layer to synthesize spatial attention maps.</p>
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<p>The structural framework of the proposed HAM-LSTM model.</p>
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<p>Gravity anomaly maps of the terrane used: (<b>a</b>) complete Bouguer anomaly; (<b>b</b>) residual gravity.</p>
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<p>Band imagery: (<b>a</b>) Landsat-9 band 5; (<b>b</b>) Sentinel-2A band 5; (<b>c</b>) ASTER band 5; (<b>d</b>) fused image; (<b>e</b>) partial magnification of (<b>a</b>) (<math display="inline"><semantics> <mrow> <mn>279</mn> <mo>×</mo> <mn>235</mn> </mrow> </semantics></math> pixels); (<b>f</b>) partial magnification of (<b>b</b>) (<math display="inline"><semantics> <mrow> <mn>279</mn> <mo>×</mo> <mn>235</mn> </mrow> </semantics></math> pixels); (<b>g</b>) partial magnification of (<b>c</b>) (<math display="inline"><semantics> <mrow> <mn>279</mn> <mo>×</mo> <mn>235</mn> </mrow> </semantics></math> pixels); and (<b>h</b>) partial magnification of (<b>d</b>) (<math display="inline"><semantics> <mrow> <mn>279</mn> <mo>×</mo> <mn>235</mn> </mrow> </semantics></math> pixels).</p>
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<p>Resultant multisource fusion imagery.</p>
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<p>Annotation map of the study area.</p>
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<p>An illustration of the sliding window method implementation.</p>
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<p>Graphs of training performance of the varied model implementations in this study: (<b>a</b>) accuracy and (<b>b</b>) loss.</p>
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<p>Classification maps derived from implementing (<b>a</b>) HAM-LSTM, (<b>b</b>) CBAM-LSTM, (<b>c</b>) SE-LSTM, (<b>d</b>) ViT, and (<b>e</b>) LSTM on the multisource fusion dataset.</p>
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<p>Confusion matrices of (<b>a</b>) HAM-LSTM, (<b>b</b>) CBAM-LSTM, (<b>c</b>) SE-LSTM, (<b>d</b>) LSTM, and (<b>e</b>) ViT implementation.</p>
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