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23 pages, 8696 KiB  
Article
Enhanced Fishing Monitoring in the Central-Eastern North Pacific Using Deep Learning with Nightly Remote Sensing
by Jiajun Li, Jinyou Li, Kui Zhang, Xi Li and Zuozhi Chen
Remote Sens. 2024, 16(22), 4312; https://doi.org/10.3390/rs16224312 - 19 Nov 2024
Abstract
The timely and accurate monitoring of high-seas fisheries is essential for effective management. However, efforts to monitor industry fishing vessels in the central-eastern North Pacific have been hampered by frequent cloud cover and solar illumination interference. In this study, enhanced fishing extraction algorithms [...] Read more.
The timely and accurate monitoring of high-seas fisheries is essential for effective management. However, efforts to monitor industry fishing vessels in the central-eastern North Pacific have been hampered by frequent cloud cover and solar illumination interference. In this study, enhanced fishing extraction algorithms based on computer vision were developed and tested. The results showed that YOLO-based computer vision models effectively detected dense small fishing targets, with original YOLOv8 achieving a precision (P) of 89% and a recall (R) of 79%, while refined versions improved these metrics to 93% and 99%, respectively. Compared with traditional threshold methods, the YOLO-based enhanced models showed significantly higher accuracy. While the threshold method could identify similar trend changes, it lacked precision in detecting individual targets, especially in blurry scenarios. Using our trained computer vision model, we established a dataset of dynamic changes in fishing vessels over the past decade. This research provides an accurate and reproducible process for precise monitoring of lit fisheries in the North Pacific, leveraging the operational and near-real-time capabilities of Google Earth Engine and computer vision. The approach can also be applied to dynamic monitoring of industrial lit fishing vessels in other regions. Full article
(This article belongs to the Special Issue Artificial Intelligence for Ocean Remote Sensing)
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Figure 1
<p>Study region of the lit fishing grounds in the North Pacific (central-east stock, 176E–165W, 35N–48N), overlaid with the average sea surface temperature from the summer fishing season of 2020. The top global map shows the location of the study area, overlaid with the average cloud fraction from the summer fishing season of 2020. The cloud fraction data are sourced from GlobColour (<a href="http://globcolour.info" target="_blank">http://globcolour.info</a>), which has been developed, validated, and distributed by ACRI-ST, France. The sea surface temperature data come from the Copernicus Marine Service (<a href="https://data.marine.copernicus.eu" target="_blank">https://data.marine.copernicus.eu</a>), which is the marine component of the Copernicus Programme of the European Union.</p>
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<p>Typical nighttime remote sensing images observed by VIIRS-DNB with squid jiggers: (<b>A</b>) Clearly identifiable and distinguishable lit fishing vessels. (<b>B</b>) Blurry but distinguishable and locatable lit fishing vessels. (<b>C</b>) Obscured lit fishing vessels, only locatable.</p>
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<p>The overall framework of the original YOLOv8, YOLO-P2, and YOLO-SPD networks. In the YOLO-SPD model, SPD-Conv is integrated into the YOLOv8 backbone to enhance performance. Meanwhile, YOLO-P2 retains the YOLOv8 backbone but adds a P2 detection head to improve small target detection.</p>
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<p>Typical nighttime imagery and detection results from different methods: (<b>A</b>) Original nighttime image. (<b>B</b>) Detection results by YOLO, where missed targets are denoted by red arrows. (<b>C</b>) Detection results by YOLO-P2. (<b>D</b>) Detection results by YOLO-SPD.</p>
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<p>Changes in the number of vessels during the summer fishing season in the North Pacific central-east stock obtained using AIS, VBD, YOLO, and improved YOLO algorithms (with P2 representing YOLO-P2 and SPD representing YOLO-SPD) (<b>A</b>) and changes in M16 brightness temperature during the fishing season (<b>B</b>). The background colors in both subplots represent visual classification categories: yellow (type 1) for cases where most light fishing vessels can be located and distinguished, green (type 2) for cases where a significant portion of the vessels are blurred or partially obscured, and red (type 3) for cases where all vessels are completely obscured.</p>
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<p>Regression fit between visual observations (Eye) and results from VBD, YOLO, and improved YOLO models under conditions where most lit fishing vessels can be visually distinguished. (<b>A</b>) Visual observations vs. VBD. (<b>B</b>) Visual observations vs. YOLO. (<b>C</b>) Visual observations vs. YOLO-P2. (<b>D</b>) Visual observations vs. YOLO-SPD.</p>
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<p>Monthly density scatter plots of lit fishing vessels during the summer fishing season in the North Pacific central-east stock, obtained using VBD, YOLO, and their improved algorithms. (<b>A</b>) Distribution in June. (<b>B</b>) Distribution in July.</p>
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<p>Dynamic changes in the centroid position of fishing vessels (<b>A</b>) and the number of operating vessels (<b>B</b>) during the summer fishing seasons from 2012 to 2023 in the central-east stock of the North Pacific.</p>
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<p>Comparison of VBD and our data flow for high-seas lit fishing monitoring.</p>
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<p>Typical clear nightly images (<b>A</b>–<b>C</b>) and detections using various automated fishing extraction methods, (<b>D</b>–<b>F</b>) nightly images with detections by YOLO, (<b>G</b>–<b>I</b>) nightly images with detections by YOLO-P2, (<b>J</b>–<b>L</b>) nightly images with detections by YOLO-SPD, and (<b>M</b>–<b>O</b>) nightly images with detections by VBD.</p>
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<p>Typical blurry nightly images (<b>A</b>–C) and detections using various automated fishing extraction methods, (<b>D</b>–<b>F</b>) nightly images with detections by YOLO, (<b>G</b>–I) nightly images with detections by YOLO-P2, (<b>J</b>–<b>L</b>) nightly images with detections by YOLO-SPD, and (<b>M</b>–<b>O</b>) nightly images with detections by VBD.</p>
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<p>Satellite AIS-derived fishing vessels overlaid with typical obscured nightly images. While fishing locations can be roughly identified, the exact number of vessels cannot be determined. Panels (<b>A</b>,<b>C</b>,<b>E</b>,<b>G</b>) display typical obscured nightly remote sensing images, and panels (<b>B</b>,<b>D</b>,<b>F</b>,<b>H</b>) show AIS-derived fishing activity locations overlaid on nightly images.</p>
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<p>Satellite AIS-derived fishing vessels overlaid with typical obscured nightly images. While fishing locations can be roughly identified, the exact number of vessels cannot be determined. Panels (<b>A</b>,<b>C</b>,<b>E</b>,<b>G</b>) display typical obscured nightly remote sensing images, and panels (<b>B</b>,<b>D</b>,<b>F</b>,<b>H</b>) show AIS-derived fishing activity locations overlaid on nightly images.</p>
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<p>A typical scenario where discrepancies exist between AIS vessel positions and actual fishing locations during fishing ground transitions. (<b>A</b>) Nightly remote sensing images, (<b>B</b>) AIS vessel positions overlaid on nightly images, and (<b>C</b>) vessel positions extracted using machine vision algorithms, also overlaid on nightly images.</p>
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13 pages, 4582 KiB  
Article
Dual-Wavelength Confocal Laser Speckle Contrast Imaging Using a Deep Learning Approach
by E Du, Haohan Zheng, Honghui He, Shiguo Li, Cong Qiu, Weifeng Zhang, Guoqing Wang, Xingquan Li, Lan Ma, Shuhao Shen and Yuan Zhou
Photonics 2024, 11(11), 1085; https://doi.org/10.3390/photonics11111085 - 18 Nov 2024
Viewed by 300
Abstract
This study developed a novel dual-wavelength confocal laser speckle imaging platform. The system includes both visible and near-infrared lasers and two imaging modes: confocal and wide-field laser speckle contrast imaging. The experimental results confirm that the proposed system can be used to measure [...] Read more.
This study developed a novel dual-wavelength confocal laser speckle imaging platform. The system includes both visible and near-infrared lasers and two imaging modes: confocal and wide-field laser speckle contrast imaging. The experimental results confirm that the proposed system can be used to measure not only blood flow but also blood oxygen saturation. Additionally, we proposed a blood flow perfusion imaging method called BlingNet (a blood flow imaging CNN) based on the laser speckle contrast imaging technique and deep learning approach. Compared to the traditional nonlinear fitting method, this method has superior accuracy and robustness with higher imaging speed, making real-time blood flow imaging possible. Full article
(This article belongs to the Special Issue New Perspectives in Biomedical Optics and Optical Imaging)
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Figure 1
<p>Dual-wavelength confocal laser speckle contrast imaging system: (<b>a</b>) physical imaging configuration; (<b>b</b>) schematic. DM, dichroic mirror; M, mirror; HWP, half-wave plate; BE, beam expander; CL, cylindrical lens; PBS, polarizing beam splitter; GV, 1-D Galvo mirror; P, polarizer. The focal length of the CL was 50 mm. The focal lengths of lenses L1, L2, L3 and L4 were 50, 75, 40 and 100 mm, respectively.</p>
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<p>Workflow of real-time laser speckle blood flow imaging based on deep learning approach.</p>
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<p>Overview of BlingNet proposed for blood flow prediction from dual-wavelength speckle contrast images.</p>
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<p>Measurement results of laser speckle contrast at different flow rates.</p>
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<p>Laser speckle contrast imaging of chicken embryo (day 4). Wide-field mode: (<b>a</b>) intensity image and (<b>b</b>) blood flow image. Confocal mode using offset line detection of 0.4 mm: (<b>c</b>) intensity image and (<b>d</b>) blood flow image. The chicken heart (circled by the red region) is more visible in (<b>d</b>) compared to (<b>b</b>). The camera exposure time was set to 2 ms. The number of scanning lines is 500. The image size is 2560 pixels × 500 pixels, which corresponds to the field of view of 10.24 mm × 8.64 mm.</p>
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<p>Chicken embryo (day 4) (<b>a</b>) SO<sub>2</sub> image using offset line detection of 0.8 mm; (<b>b</b>) SO<sub>2</sub> image using offset line detection of 1.6 mm; (<b>c</b>) speckle contrast image. The camera exposure time was set to 2 ms. The number of scanning lines is 500. The image size is 2560 pixels × 500 pixels, which corresponds to the field of view of 10.24 mm × 8.64 mm. The red area circled in <a href="#photonics-11-01085-f006" class="html-fig">Figure 6</a> is the heart of the chicken embryo. The color bar values in (<b>a</b>,<b>b</b>) represent the oxygen saturation (<span class="html-italic">SO</span><sub>2</sub>), while in (<b>c</b>) the color bar represents speckle contrast.</p>
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<p>Comparison results of laser speckle blood flow imaging of the chicken embryo (day 4). (<b>a</b>) light intensity of the region of interest, (<b>b</b>) laser speckle contrast image, (<b>c</b>) blood flow image using the traditional nonlinear fitting method, (<b>d</b>) blood flow image using the deep learning method. The region of interest is 2.048 mm × 2.048 mm.</p>
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22 pages, 8045 KiB  
Article
A GIS Plugin for the Assessment of Deformations in Existing Bridge Portfolios via MTInSAR Data
by Mirko Calò, Sergio Ruggieri, Andrea Nettis and Giuseppina Uva
Remote Sens. 2024, 16(22), 4293; https://doi.org/10.3390/rs16224293 - 18 Nov 2024
Viewed by 218
Abstract
The paper presents a GIS plugin, named Bridge Assessment System via MTInSAR (BAS-MTInSAR), aimed at assessing deformations in existing simply supported concrete girder bridges through Multi-Temporal Interferometry Synthetic Aperture Radar (MTInSAR). Existing bridges require continuous maintenance to ensure functionality toward external effects undermining [...] Read more.
The paper presents a GIS plugin, named Bridge Assessment System via MTInSAR (BAS-MTInSAR), aimed at assessing deformations in existing simply supported concrete girder bridges through Multi-Temporal Interferometry Synthetic Aperture Radar (MTInSAR). Existing bridges require continuous maintenance to ensure functionality toward external effects undermining the safety of these structures, such as aging, material degradation, and environmental factors. Although effective and standardized methodologies exist (e.g., structural monitoring, periodic onsite inspections), new emerging technologies could be employed to provide time- and cost-effective information on the current state of structures and to drive prompt interventions to mitigate risk. One example is represented by MTInSAR data, which can provide near-continuous information about structural displacements over time. To easily manage these data, the paper presents BAS-MTInSAR. The tool allows users to insert information of the focused bridge (displacement time series, structural information, temperature data) and, through a user-friendly GUI, observe the occurrence of abnormal deformations. In addition, the tool implements a procedure of multisource data management and defines proper thresholds to assess bridge behavior against current code prescriptions. BAS-MTInSAR is fully described throughout the text and was tested on a real case study, showing the main potentialities of the tool in managing bridge portfolios. Full article
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<p>Framework of BAS-MTInSAR.</p>
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<p>Example of simply supported deck divided in three equally distributed sub-regions: 1st sub-region (blue) near the pinned support, 2nd sub-region (cyan) at midspan, and 3rd sub-region (purple) near the roller support. The bearing typology shown in the example is unbonded elastomeric, where the greater the bearing height, the lower the translation stiffness (i.e., higher displacement).</p>
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<p>Example of simply supported deck together with L-T-V reference system, in black, for each sub-region. In this case, each sub-region of the bridge is rotated by <span class="html-italic">γ</span> angle with respect to the East direction, reported by the red reference system (i.e., East-North-Zenith).</p>
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<p>Example of (<b>a</b>) STL and (<b>b</b>) LSRM decompositions of a generic time series from Step 2.</p>
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<p>Example of displacement scenario and simple analytical model employed (colored dots represent sub-region centroids): (<b>a</b>) Free longitudinal displacements under constant temperature delta, Δ<span class="html-italic">T<sub>C</sub></span>. The dashed shapes show the deformed configuration of the deck under positive and negative Δ<span class="html-italic">T<sub>C</sub></span>; (<b>b</b>) Vertical displacements under linear temperature delta, Δ<span class="html-italic">T<sub>L</sub></span>. The dashed shape shows the deformed configuration of the deck under positive and negative Δ<span class="html-italic">T<sub>L</sub></span>.</p>
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<p>QDialog window named “Bridge Analysis” with boxes showing the most recurrent GUI elements employed in BAS-MTInSAR.</p>
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<p>Deck and beam information defined in the QTableWidgets of “Deck section design” and “Beam section design” QFrames for a single span. The green reference system on the right shows the convention sign for bridge displacements of Steps 2 and 3 in the case in which the bridge centerline is drawn from the left to the right, which is from the beginning of the 1st sub-region to the end of the 3rd sub-region in the figure.</p>
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<p>“Database” QTabWidget of “Bridge analysis” QDialog window. Listed bridges (e.g., Bridge 1 in QListWidget) and numbers in the Summary QTableWidget are fictitious and added by the authors for demonstration purposes only. The Fiumicino (Rome) bridge is the one discussed in <a href="#sec4-remotesensing-16-04293" class="html-sec">Section 4</a>.</p>
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<p>“Inspection report” QDialog window.</p>
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<p>Single-span simply supported concrete girder bridge, Fiumicino, Rome (Italy) and a scale axonometric view. The single-span bridge, characterized by 10 double-T beams of equal sections is divided into three sub-regions (i.e., 1st, 2nd, and 3rd sub-region). The 1st sub-region is characterized by roller bearings, while the 3rd one by pinned bearings. Red and blue lines on the left of the deck represent the expected direction of free longitudinal displacements under constant temperature gradient Δ<span class="html-italic">T<sub>C</sub></span><sub>.</sub></p>
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<p>Definition of input data through the “Data collection” QTabWidget of “Bridge analysis” QDialog window and “Temperature” QDialog window. “Deck Section design” and “Beam Section design” are defined according to <a href="#remotesensing-16-04293-f003" class="html-fig">Figure 3</a>, resulting in <a href="#remotesensing-16-04293-f010" class="html-fig">Figure 10</a>. Regarding temperature data, the chart shows monthly average temperatures in 2017, 2018, 2019, and 2020 (red cross, blue cross, green cross, and red circle, respectively) used in the cosine temperature model [<a href="#B32-remotesensing-16-04293" class="html-bibr">32</a>]. The purple line is the cosine model, the parameters of which are the average of the model itself fitted over each year of temperature acquisition.</p>
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<p>“PS Selection” QTabWidget of “Bridge analysis” QDialog window.</p>
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<p>“Displacement time series” QTabWidget of “Bridge analysis” QDialog window.</p>
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<p>“Seasonal-Trend components” QTabWidget of “Bridge analysis” QDialog window.</p>
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<p>“Deformation scenarios” QTabWidget of “Bridge analysis” QDialog window.</p>
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<p>Longitudinal seasonal deformation scenario. Blue, cyan, and purple lines refers to 1st, 2nd, and 3rd sub-regions, while the red patch refers to the range defined by the temperature threshold under Δ<span class="html-italic">T<sub>C</sub></span>.</p>
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<p>Vertical seasonal deformation scenario. Blue, cyan, and purple lines refers to 1st, 2nd, and 3rd sub-regions, while the red patch refers to the range defined by the temperature threshold under Δ<span class="html-italic">T<sub>L</sub></span>.</p>
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<p>Some of the evaluated bridge displacement scenarios on the Fiumicino (Rome) bridge. (<b>a</b>) Longitudinal seasonal displacement scenario, dashed lines represent the deformed shape of the bridge under Δ<span class="html-italic">T<sub>C</sub></span>. Red lines refer to a positive Δ<span class="html-italic">T<sub>C</sub></span> (negative displacement), blue ones to a negative Δ<span class="html-italic">T<sub>C</sub></span> (positive displacement); (<b>b</b>) Longitudinal trend displacement scenario, focusing on the 3rd sub-region with the dashed lines showing a uniform positive displacement toward the East (black reference system on top left); (<b>c</b>) Vertical trend displacement scenario, focusing on the 3rd sub-region with the dashed lines showing a uniform downward negative displacement. Deformed shapes of the span are not scaled and represented only for description purposes.</p>
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18 pages, 14901 KiB  
Article
A Constantly Updated Flood Hazard Assessment Tool Using Satellite-Based High-Resolution Land Cover Dataset Within Google Earth Engine
by Alexandra Gemitzi, Odysseas Kopsidas, Foteini Stefani, Aposotolos Polymeros and Vasilis Bellos
Land 2024, 13(11), 1929; https://doi.org/10.3390/land13111929 - 16 Nov 2024
Viewed by 205
Abstract
This work aims to develop a constantly updated flood hazard assessment tool that utilizes readily available datasets derived by remote sensing techniques. It is based on the recently released global land use/land cover (LULC) dataset Dynamic World, which is readily available, covering the [...] Read more.
This work aims to develop a constantly updated flood hazard assessment tool that utilizes readily available datasets derived by remote sensing techniques. It is based on the recently released global land use/land cover (LULC) dataset Dynamic World, which is readily available, covering the period from 2015 until now, as an open data source within the Google Earth Engine (GEE) platform. The tool is updated constantly following the release rate of Sentinel-2 images, i.e., every 2 to 5 days depending on the location, and provides a near-real-time detection of flooded areas. Specifically, it identifies how many times each 10 m pixel is characterized as flooded for a selected time period. To investigate the fruitfulness of the proposed tool, we provide two different applications; the first one in the Thrace region, where the flood hazard map computed with the presented herein approach was compared against the flood hazard maps developed in the frames of the EU Directive 2007/60, and we found several inconsistencies between the two approaches. The second application focuses on the Thessaly region, aiming to assess the impacts of a specific, unprecedented storm event that affected the study area in September 2023. Moreover, a new economic metric is proposed, named maximum potential economic loss, to assess the socioeconomic implications of the flooding. The innovative character of the presented methodology consists of the use of remotely sensed-based datasets, becoming available at increasing rates, for developing an operational instrument that defines and updates the flood hazard zones in real-time as required. Full article
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<p>Location map of Thrace (<b>a</b>) and Thessaly (<b>b</b>) RBD and potential significant flood risk areas according to the EU Directive 2007/60 [<a href="#B10-land-13-01929" class="html-bibr">10</a>].</p>
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<p>Flow chart of the flood hazard mapping approach.</p>
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<p>Flood Hazard Map of the broader Thrace RBD based on the methodology presented herein, covering the 2015–2023 period.</p>
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<p>Flooded areas versus number of times flooded during 2015–2023 in Thrace RBD.</p>
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<p>100-year return period flood hazard map as defined in the flood management plan for Thrace RBD, Greece [<a href="#B28-land-13-01929" class="html-bibr">28</a>].</p>
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<p>Comparison of the flood hazard hap of the Thrace RBD based on the methodology presented herein against the 100-year flood hazard map based on the Flood Management Plan.</p>
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<p>Time series of monthly flooded areas from 2015 to 2023 in Thrace RBD.</p>
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<p>Annual flooded areas in Thrace RBD based on the DW approach.</p>
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<p>Flooded area prior to storm Daniel (<b>left</b>) and after storm Daniel (<b>right</b>).</p>
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<p>Flooded area against how many times is flooded before and after storm Daniel.</p>
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<p>Total annual economic loss from flooding of cultivated land in Thrace RBD based on the extent of flooding areas according to the SO coefficients.</p>
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<p>Mean monthly flood damage costs estimated in Thrace RBD with the MPEL method.</p>
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<p>Comparison of historical farm damage compensations with flood damage costs by MPEL and associated flooded crop areas in Thrace RBD.</p>
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13 pages, 1397 KiB  
Article
Near-Data Source Graph Partitioning
by Furong Chang, Hao Guo, Farhan Ullah, Haochen Wang, Yue Zhao and Haitian Zhang
Electronics 2024, 13(22), 4455; https://doi.org/10.3390/electronics13224455 - 13 Nov 2024
Viewed by 295
Abstract
Recently, numerous graph partitioning approaches have been proposed to distribute a big graph to machines in a cluster for distributed computing. Due to heavy communication overhead, these graph partitioning approaches always suffered from long ingress times. Also, heavy communication overhead not only limits [...] Read more.
Recently, numerous graph partitioning approaches have been proposed to distribute a big graph to machines in a cluster for distributed computing. Due to heavy communication overhead, these graph partitioning approaches always suffered from long ingress times. Also, heavy communication overhead not only limits the scalability of distributed graph-parallel computing platforms but also reduces the overall performance of clusters. In order to address this problem, this work proposed a near-data source parallel graph partitioning approach noted as NDGP. In NDGP, an edge was preferentially distributed to the machine where it was stored. We implemented NDGP over two classic graph partitioning approaches, Random and Greedy, and one most recently proposed graph partitioning approach, OLPGP, and evaluated its effectiveness. Extensive experiments conducted on real-world data sets verified the effectiveness of NDGP on reducing the communication overhead in the graph partitioning process and demonstrated that NDGP does not induce additional communication and computing workload to the graph-distributed computing that follows. Full article
(This article belongs to the Section Computer Science & Engineering)
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<p>Original graph partitioning.</p>
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<p>NDGP graph partitioning.</p>
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<p>Comparison of the number of edges sent while distributing the LiveJournal data set to eight machines. (Note: The thickness of the lines represents the number of edges sent).</p>
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<p>Comparison of the number of edges sent while distributing the Twitter data set to 16 machines. (Note; The thickness of the lines are representing the number of edges sent).</p>
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<p>Comparison of the runtime running PageRank on the Twitter data set.</p>
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<p>Comparison of the volume of communication overheads running PageRank on the Twitter data set.</p>
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<p>Comparison of the volume of communication overheads running SSSP on the BFS data set.</p>
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<p>Comparison of the runtime running Triangle Counting on the BFS data set.</p>
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<p>Comparison of the number of edges sent while distributing the com-Orkut data set.</p>
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<p>Comparison of the volume of communication overhead running Triangle Counting on the com-Orkut data set.</p>
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<p>Comparison of the runtime running Triangle Counting on the com-Orkut data set.</p>
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25 pages, 3232 KiB  
Article
A Framework for Distributed Orchestration of Cyber-Physical Systems: An Energy Trading Case Study
by Kostas Siozios
Technologies 2024, 12(11), 229; https://doi.org/10.3390/technologies12110229 - 13 Nov 2024
Viewed by 558
Abstract
The increasing number of active energy consumers, also known as energy prosumers, is dramatically changing the electricity system. New products and services that adopt the concept of dynamic pricing are available to the market, where demand and price forecasting are applied to determine [...] Read more.
The increasing number of active energy consumers, also known as energy prosumers, is dramatically changing the electricity system. New products and services that adopt the concept of dynamic pricing are available to the market, where demand and price forecasting are applied to determine schedule loads and prices. Throughout this manuscript, a novel framework for energy trading among prosumers is introduced. Rather than solving the problem in a centralized manner, the proposed orchestrator relies on a distributed game theory to determine optimal bids. Experimental results validate the efficiency of proposed solution, since it achieves average energy cost reduction of 2×, as compared to the associated cost from the main grid. Additionally, the hardware implementation of the introduced framework onto a low-cost embedded device achieves near real-time operation with comparable performance to state-of-the-art computational intensive solvers. Full article
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Graphical abstract

Graphical abstract
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<p>Functionality of a cyber–physical system.</p>
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<p>Template of our case study.</p>
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<p>Simulation framework for supporting the proposed MiL and HiL simulations.</p>
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<p>The proposed energy trading framework. Expected loads per energy prosumer (left part of the figure) are calculated based on [<a href="#B42-technologies-12-00229" class="html-bibr">42</a>].</p>
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<p>Candidate bidding aggressiveness schemes.</p>
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<p>Performance of simultaneous and sequential auctions.</p>
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<p>Efficiency of multiple partial auctions.</p>
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<p>Impact of cluster size on the auction’s outcome.</p>
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<p>VES charge during the 52-week experiment.</p>
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<p>Exploration of maximum number of rounds <math display="inline"><semantics> <mrow> <mo>(</mo> <mi>R</mi> <mo>)</mo> </mrow> </semantics></math> per auction.</p>
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<p>Demonstration setup for the proposed distributed auction framework.</p>
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<p>Efficiency for energy transactions that are performed (i) at run-time, (ii) a week ahead, and (iii) a day ahead.</p>
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<p>Execution run-times for different numbers of simultaneous games <math display="inline"><semantics> <mrow> <mo>(</mo> <msub> <mi>H</mi> <mi>i</mi> </msub> <mo>)</mo> </mrow> </semantics></math> per auction <math display="inline"><semantics> <msub> <mi>a</mi> <mi>i</mi> </msub> </semantics></math>.</p>
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12 pages, 265 KiB  
Article
Handheld NIR Spectroscopy Combined with a Hybrid LDA-SVM Model for Fast Classification of Retail Milk
by Francesco Maria Tangorra, Annalaura Lopez, Elena Ighina, Federica Bellagamba and Vittorio Maria Moretti
Foods 2024, 13(22), 3577; https://doi.org/10.3390/foods13223577 - 9 Nov 2024
Viewed by 524
Abstract
The EU market offers different types of milk, distinguished by origin, production method, processing technology, fat content, and other characteristics, which are often detailed on product labels. In this context, ensuring the authenticity of milk is crucial for maintaining standards and preventing fraud. [...] Read more.
The EU market offers different types of milk, distinguished by origin, production method, processing technology, fat content, and other characteristics, which are often detailed on product labels. In this context, ensuring the authenticity of milk is crucial for maintaining standards and preventing fraud. Various food authenticity techniques have been employed to achieve this. Among them, near-infrared (NIR) spectroscopy is valued for its non-destructive and rapid analysis capabilities. This study evaluates the effectiveness of a miniaturized NIR device combined with support vector machine (SVM) algorithms and LDA feature selection to discriminate between four commercial milk types: high-quality fresh milk, milk labeled as mountain product, extended shelf-life milk, and TSG hay milk. The results indicate that NIR spectroscopy can effectively classify milk based on the type of milk, relying on different production systems and heat treatments (pasteurization). This capability was greater in distinguishing high-quality mountain and hay milk from the other types, while resulting in less successful class assignment for extended shelf-life milk. This study demonstrated the potential of portable NIR spectroscopy for real-time and cost-effective milk authentication at the retail level. Full article
(This article belongs to the Special Issue Spectroscopic Methods Applied in Food Quality Determination)
17 pages, 3828 KiB  
Article
Analysis of Variability of Water Quality Indicators in the Municipality Water Supply System—A Case Study
by Andżelika Domoń, Weronika Wilczewska, Dorota Papciak and Beata Kowalska
Water 2024, 16(22), 3219; https://doi.org/10.3390/w16223219 - 8 Nov 2024
Viewed by 426
Abstract
This study investigated the variability of water quality indicators in four municipal water distribution systems near a medium-sized city. Despite the proximity of water intakes, water quality in different distribution systems can vary significantly due to local factors such as infrastructure conditions, treatment [...] Read more.
This study investigated the variability of water quality indicators in four municipal water distribution systems near a medium-sized city. Despite the proximity of water intakes, water quality in different distribution systems can vary significantly due to local factors such as infrastructure conditions, treatment technology, and specific environmental conditions affecting water in each water supply network. Water samples were collected from multiple points in each system and analyzed for physicochemical properties. The results showed significant differences in total carbon, dissolved organic carbon, and ammonium nitrogen, indicating variability in water quality between systems. These results emphasize the need for integrated management strategies, innovative technologies, and real-time monitoring to maintain water quality. The study also highlights challenges such as aging infrastructure, pollution, and financial constraints in managing water supplies. Full article
(This article belongs to the Section Urban Water Management)
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<p>Box plots showing the distribution of water quality indicators in DS(I), with white dots representing outliers.</p>
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<p>Box plots showing the distribution of water quality indicators in DS(II), with white dots representing outliers.</p>
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<p>Box plots showing the distribution of water quality indicators in DS(III), with white dots representing outliers.</p>
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<p>Box plots showing the distribution of water quality indicators in DS(IV), with white dots representing outliers.</p>
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<p>Time graph of the variable: (<b>a</b>) TC, (<b>b</b>) DOC, (<b>c</b>) Ammonium nitrogen.</p>
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<p>Time graph of the variable: (<b>a</b>) TC, (<b>b</b>) DOC, (<b>c</b>) Nitrite nitrogen.</p>
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<p>Time graph Nitrite nitrogen.</p>
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<p>Time graph of the variable: (<b>a</b>) Ammonium nitrogen, (<b>b</b>) Phosphorus, (<b>c</b>) Nitrate nitrogen.</p>
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28 pages, 45519 KiB  
Article
A Novel Input Schematization Method for Coastal Flooding Early Warning Systems Incorporating Climate Change Impacts
by Andreas G. Papadimitriou, Anastasios S. Metallinos, Michalis K. Chondros and Vasiliki K. Tsoukala
Climate 2024, 12(11), 178; https://doi.org/10.3390/cli12110178 - 5 Nov 2024
Viewed by 582
Abstract
Coastal flooding poses a significant threat to coastal communities, adversely affecting both safety and economic stability. This threat is exacerbated by factors such as sea level rise, rapid urbanization, and inadequate coastal infrastructure, as noted in recent climate change reports. Early warning systems [...] Read more.
Coastal flooding poses a significant threat to coastal communities, adversely affecting both safety and economic stability. This threat is exacerbated by factors such as sea level rise, rapid urbanization, and inadequate coastal infrastructure, as noted in recent climate change reports. Early warning systems (EWSs) have proven to be effective tools in coastal planning and management, offering a high cost-to-benefit ratio. Recent advancements have integrated operational numerical models with machine learning techniques to develop near-real-time EWSs, leveraging data obtained from reputable databases that provide reliable hourly sea-state and sea level data. Despite these advancements, a stepwise methodology for selecting representative events, akin to wave input reduction methods used in morphological modeling, remains undeveloped. Moreover, existing methodologies often overlook the significance of compound extreme events and their potential increased occurrence under climate change projections. This research addresses these gaps by introducing a novel input schematization method that combines efficient hydrodynamic modeling with clustering algorithms. The proposed methodοlogy, implemented in the coastal area of Pyrgos, Greece, aims to select an optimal number of representative sea-state and water level combinations to develop accurate EWSs for coastal flooding risk prediction. A key innovation of this methodology is the incorporation of weights in the clustering algorithm to ensure adequate representation of extreme compound events, also taking into account projections for future climate scenarios. This approach aims to enhance the accuracy and reliability of coastal flooding EWSs, ultimately improving the resilience of coastal communities against imminent flooding threats. Full article
(This article belongs to the Special Issue Coastal Hazards under Climate Change)
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<p>Overview of the study area, highlighting Alfios river and the outline of the dried-out Agoulinitsa Lake along with two characteristic coastal profile locations.</p>
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<p>Coastal profile sections for the two examined locations.</p>
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<p>Wave rose plot offshore of the study area for the (<b>a</b>) historical, (<b>b</b>) RCP 8.5, and (<b>c</b>) RCP 4.5 datasets.</p>
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<p>Total water levels for the study area for the historical, RCP 8.5, and RCP 4.5 datasets.</p>
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<p>Flow chart depicting the steps of the proposed methodology.</p>
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<p>Compound events as defined for the (<b>a</b>) historical, (<b>b</b>) RCP 8.5, and (<b>c</b>) RCP 4.5 datasets.</p>
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<p>Bathymetry of the numerical domain and extraction points of nearshore waves. Date of bathymetric survey: 26 July 2024.</p>
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<p>Comparison of significant wave heights for the historical dataset (1977–2005) between offshore wave data (circular markers), nearshore point P1 (x markers), and nearshore point P2 (triangular markers).</p>
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<p>Comparison of significant wave heights for the RCP8.5 dataset (2041–2070) between offshore wave data (circular markers), nearshore point P1 (x markers), and nearshore point P2 (triangular markers). Vertical plots indicate sequence of scenarios.</p>
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<p>Comparison of significant wave heights for the RCP4.5 dataset (2071–2100) between offshore wave data (circular markers), nearshore point P1 (x markers), and nearshore point P2 (triangular markers). Vertical plots indicate sequence of scenarios.</p>
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<p>Compound spectral wave height events that generate wave overtopping in comparison with (<b>a</b>) total water level elevation, (<b>b</b>) peak wave period, and (<b>c</b>) deep water wave incidence angle.</p>
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<p>Bar plot of estimated feature importances for (<b>a</b>) historical dataset, (<b>b</b>) RCP 8.5, and (<b>c</b>) RCP 4.5.</p>
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<p>Elbow graph for the subcritical historical dataset.</p>
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<p>Obtained clusters and centroids for the subcritical historical dataset using (<b>a</b>) no sample weighting function and (<b>b</b>) the sample weighting function based on permutation feature importance. The different colors of the points indicate the cluster membership.</p>
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<p>Compound events that generate wave overtopping superimposed with the centroids of the cluster analysis for the historical dataset.</p>
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<p>Compound events that generate wave overtopping superimposed with the centroids of the cluster analysis for the RCP 8.5 dataset without weighting function (green triangular markers) and with weighting function (red square markers).</p>
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<p>Obtained clusters for each dataset: (<b>a</b>) historical, (<b>b</b>) RCP 8.5, and (<b>c</b>) RCP 4.5.</p>
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18 pages, 2703 KiB  
Article
Single Laboratory Evaluation of the Q20+ Nanopore Sequencing Kit for Bacterial Outbreak Investigations
by Maria Hoffmann, Jay Hee Jang, Sandra M. Tallent and Narjol Gonzalez-Escalona
Int. J. Mol. Sci. 2024, 25(22), 11877; https://doi.org/10.3390/ijms252211877 - 5 Nov 2024
Viewed by 468
Abstract
Leafy greens are a significant source of produce-related Shiga toxin-producing Escherichia coli (STEC) outbreaks in the United States, with agricultural water often implicated as a potential source. Current FDA outbreak detection protocols are time-consuming and rely on sequencing methods performed in costly equipment. [...] Read more.
Leafy greens are a significant source of produce-related Shiga toxin-producing Escherichia coli (STEC) outbreaks in the United States, with agricultural water often implicated as a potential source. Current FDA outbreak detection protocols are time-consuming and rely on sequencing methods performed in costly equipment. This study evaluated the potential of Oxford Nanopore Technologies (ONT) with Q20+ chemistry as a cost-effective, rapid, and accurate method for identifying and clustering foodborne pathogens. The study focuses on assessing whether ONT Q20+ technology could facilitate near real-time pathogen identification, including SNP differences, serotypes, and antimicrobial resistance genes. This pilot study evaluated different combinations of two DNA extraction methods (Maxwell RSC Cultured Cell DNA kit and Monarch high molecular weight extraction kits) and two ONT library preparation protocols (ligation and the rapid barcoding sequencing kit) using five well-characterized strains representing diverse foodborne pathogens. High-quality, closed bacterial genomes were obtained from all combinations of extraction and sequencing kits. However, variations in assembly length and genome completeness were observed, indicating the need for further optimization. In silico analyses demonstrated that Q20+ nanopore sequencing chemistry accurately identified species, genotype, and virulence factors, with comparable results to Illumina sequencing. Phylogenomic clustering showed that ONT assemblies clustered with reference genomes, though some indels and SNP differences were observed, likely due to sequencing and analysis methodologies rather than inherent genetic variation. Additionally, the study evaluated the impact of a change in the sampling rates from 4 kHz (260 bases pair second) to 5 kHz (400 bases pair second), finding no significant difference in sequencing accuracy. This evaluation workflow offers a framework for evaluating novel technologies for use in surveillance and foodborne outbreak investigations. Overall, the evaluation demonstrated the potential of ONT Q20+ nanopore sequencing chemistry to assist in identifying the correct strain during outbreak investigations. However, further research, validation studies, and optimization efforts are needed to address the observed limitations and fully realize the technology’s potential for improving public health outcomes and enabling more efficient responses to foodborne disease threats. Full article
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<p>NGS validation workflow for pure bacterial isolates according to the Guidelines for the Validation of Analytical Methods Using Nucleic Acid Sequenced-Based Technologies from the FDA (<a href="https://www.fda.gov/food/laboratory-methods-food/foods-program-methods-validation-processes-and-guidelines" target="_blank">https://www.fda.gov/food/laboratory-methods-food/foods-program-methods-validation-processes-and-guidelines</a>, accessed on 30 October 2024).</p>
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<p>Results of the wgMLST analyses for CFSAN000189. (<b>A</b>) Snapshot of the NJ tree generated from the wgMLST analysis of the ONT assemblies obtained by the different combinations tested against a set of known genomes closely related to that same strain (ST909). (<b>B</b>) Minimum spanning tree (MST) showing the differences between the different CFSAN000189 assemblies obtained by different sequencing technologies. The complete NJ tree can be found in <a href="#app1-ijms-25-11877" class="html-app">Supplementary Figure S3</a>.</p>
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<p>Results of the wgMLST analyses for CFSAN123154. (<b>A</b>) NJ tree generated from the wgMLST analysis of the ONT assemblies obtained by the different combinations tested against a set of known genomes closely related to that same strain. (<b>B</b>) Minimum spanning tree (MST) showing the differences between the different CFSAN123154 assemblies obtained by different sequencing technologies. The complete NJ tree can be found in <a href="#app1-ijms-25-11877" class="html-app">Supplementary Figure S4</a>.</p>
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<p>Results of the wgMLST analyses for CFSAN030807. (<b>A</b>) Snapshot of the NJ tree generated from the wgMLST analysis of the ONT assemblies obtained by the different combinations tested against a set of known genomes (156) closely related to that same strain (ST152). (<b>B</b>) Minimum spanning tree (MST) showing the differences between the different CFSAN030807 assemblies obtained by different sequencing technologies. The complete NJ tree can be found in <a href="#app1-ijms-25-11877" class="html-app">Supplementary Figure S5</a>.</p>
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<p>Results of the wgMLST analyses for CFSAN076620. (<b>A</b>) NJ tree generated from the wgMLST analysis of the ONT assemblies obtained by the different combinations tested against a set of known genomes (54) closely related to that same strain (ST629). (<b>B</b>) Minimum spanning tree (MST) showing the differences between the different CFSAN076620 assemblies obtained by different sequencing technologies.</p>
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<p>Results of the wgMLST analyses for CFSAN086181. (<b>A</b>) Snapshot of the NJ tree generated from the wgMLST analysis of the ONT assemblies obtained by the different combination tested against a set of known genomes (54) closely related to that same strain (ST629). (<b>B</b>) Minimum spanning tree (MST) showing the differences between the different CFSAN086181 assemblies obtained by different sequencing technologies. The complete NJ tree can be found in <a href="#app1-ijms-25-11877" class="html-app">Supplementary Figure S6</a>.</p>
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37 pages, 34329 KiB  
Technical Note
The Cycle 46 Configuration of the HARMONIE-AROME Forecast Model
by Emily Gleeson, Ekaterina Kurzeneva, Wim de Rooy, Laura Rontu, Daniel Martín Pérez, Colm Clancy, Karl-Ivar Ivarsson, Bjørg Jenny Engdahl, Sander Tijm, Kristian Pagh Nielsen, Metodija Shapkalijevski, Panu Maalampi, Peter Ukkonen, Yurii Batrak, Marvin Kähnert, Tosca Kettler, Sophie Marie Elies van den Brekel, Michael Robin Adriaens, Natalie Theeuwes, Bolli Pálmason, Thomas Rieutord, James Fannon, Eoin Whelan, Samuel Viana, Mariken Homleid, Geoffrey Bessardon, Jeanette Onvlee, Patrick Samuelsson, Daniel Santos-Muñoz, Ole Nikolai Vignes and Roel Stappersadd Show full author list remove Hide full author list
Meteorology 2024, 3(4), 354-390; https://doi.org/10.3390/meteorology3040018 - 5 Nov 2024
Viewed by 986
Abstract
The aim of this technical note is to describe the Cycle 46 reference configuration of the HARMONIE-AROME convection-permitting numerical weather prediction model. HARMONIE-AROME is one of the canonical system configurations that is developed, maintained, and validated in the ACCORD consortium, a collaboration of [...] Read more.
The aim of this technical note is to describe the Cycle 46 reference configuration of the HARMONIE-AROME convection-permitting numerical weather prediction model. HARMONIE-AROME is one of the canonical system configurations that is developed, maintained, and validated in the ACCORD consortium, a collaboration of 26 countries in Europe and northern Africa on short-range mesoscale numerical weather prediction. This technical note describes updates to the physical parametrizations, both upper-air and surface, configuration choices such as lateral boundary conditions, model levels, horizontal resolution, model time step, and databases associated with the model, such as for physiography and aerosols. Much of the physics developments are related to improving the representation of clouds in the model, including developments in the turbulence, shallow convection, and statistical cloud scheme, as well as changes in radiation and cloud microphysics concerning cloud droplet number concentration and longwave cloud liquid optical properties. Near real-time aerosols and the ICE-T microphysics scheme, which improves the representation of supercooled liquid, and a wind farm parametrization have been added as options. Surface-wise, one of the main advances is the implementation of the lake model FLake. An outlook on upcoming developments is also included. Full article
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<p>The HARMONIE-AROME workflow.</p>
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<p>Dust case on the 20 of February 2023. Daily mean global SW radiation from HARMONIE-AROME Cycle 46 experiments. (<b>a</b>) using the default Tegen aerosol climatology, (<b>b</b>) using NRT CAMS aerosols, (<b>c</b>) difference between these.</p>
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<p>Daily cycle of global SW radiation for a desert dust intrusion case on 20 February 2023. The average of the measurements from 29 stations over the Spanish Peninsula is depicted by the dashed black line. Model results at the station points for the experiment with the Tegen aerosol climatology are shown in red, while those for NRT aerosols are shown in green.</p>
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<p>LW effective emissivity as a function of LWP. Grey dots are the values derived from the Cabauw measurements. The green curve represents Equation (<a href="#FD1-meteorology-03-00018" class="html-disp-formula">1</a>) with the default coefficient of −0.144. The blue and red curves use values −0.158 and −0.130, respectively. The black curve uses the coefficient of −0.096, which ensures a least squares best fit.</p>
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<p>Spectral absorptance for a LWP of (<b>a</b>) 1 gm<sup>−2</sup> (<b>b</b>) and 10 gm<sup>−2</sup> for the 16 LW bands of the Nielsen scheme. Corresponding values calculated from the emissivity by the Smith and Shi [<a href="#B27-meteorology-03-00018" class="html-bibr">27</a>] parametrization (purple continuous line) and the Kettler scheme (green continuous line [<a href="#B26-meteorology-03-00018" class="html-bibr">26</a>]) are shown.</p>
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<p>Spectral absorptance for a LWP of (<b>a</b>) 1 gm<sup>−2</sup> (<b>b</b>) and 10 gm<sup>−2</sup> for the 16 LW bands of the Nielsen scheme. Corresponding values calculated from the emissivity by the Smith and Shi [<a href="#B27-meteorology-03-00018" class="html-bibr">27</a>] parametrization (purple continuous line) and the Kettler scheme (green continuous line [<a href="#B26-meteorology-03-00018" class="html-bibr">26</a>]) are shown.</p>
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<p>(<b>a</b>) MSG visible satellite image. (<b>b</b>) MSG Seviri cloud water path product from KNMI. (<b>c</b>) Integrated cloud water condensate (gm<sup>−2</sup>) from the default HARMONIE-AROME Cycle 43 experiment. (<b>d</b>) Integrated cloud water condensate (gm<sup>−2</sup>) from the HARMONIE-AROME Cycle 43 experiment with a CDNC of 50 cm<sup>−3</sup> and the LW effective emissivity coefficient of Kettler [<a href="#B26-meteorology-03-00018" class="html-bibr">26</a>]. All at 12 Z on 19 July 2019.</p>
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<p>Distribution of CSI for summer (<b>a</b>) and winter (<b>b</b>) 2-week periods, obtained from observations over Ireland and from the results of two HARMONIE-AROME Cycle 46 experiments, with prescribed CDNC (Tegen) and with CDNC derived from CAMS data (CAMSNRT).</p>
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<p>SW radiation bias (Wm<sup>−2</sup>) for summer and winter 2-week periods for experiments with HARMONIE-AROME Cycle 46 over Ireland without NRT aerosols (Tegen) (<b>a</b>,<b>c</b>) and using the NRT aerosols (<b>b</b>,<b>d</b>).</p>
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<p>SW radiation bias (Wm<sup>−2</sup>) for summer and winter 2-week periods for experiments with HARMONIE-AROME Cycle 46 over Ireland without NRT aerosols (Tegen) (<b>a</b>,<b>c</b>) and using the NRT aerosols (<b>b</b>,<b>d</b>).</p>
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<p>Example of spurious cirrus clouds. (<b>a</b>) original OCND2. (<b>b</b>) OCND2 with technical corrections. Clouds are shown as cyan shading. The figures are from a 13 h forecast starting from 00 Z on 16 April 2018.</p>
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<p>Simulated cloud liquid water content, gm<sup>−3</sup>, in the Alta region for model level 41 (approximately 820 hPa) at 14 UTC 19 April 2023, from ICE3 (<b>a</b>), the ICE-T experiment (<b>b</b>), and the difference between these (<b>c</b>).</p>
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<p>The kinematic total turbulent moisture transport (<math display="inline"><semantics> <mover> <mrow> <msup> <mi>w</mi> <mo>′</mo> </msup> <msubsup> <mi>r</mi> <mrow> <mi>t</mi> <mo>,</mo> <mi>t</mi> <mi>o</mi> <mi>t</mi> </mrow> <mo>′</mo> </msubsup> </mrow> <mo>¯</mo> </mover> </semantics></math>) on the 9th hour of the simulation of the ARM shallow cumulus case [<a href="#B44-meteorology-03-00018" class="html-bibr">44</a>]. The blue line is the DALES model. The green lines are HARMONIE-AROME Cycle 40, with all the updates described in [<a href="#B39-meteorology-03-00018" class="html-bibr">39</a>], as applied later to HARMONIE-AROME Cycle 43 and 46. The green dashed line is for the experiment without the energy cascade; the green solid line is for the experiment with the energy cascade. European Geosciences Union 2022, from Figure 6 in [<a href="#B39-meteorology-03-00018" class="html-bibr">39</a>].</p>
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<p>Frequency bias of the cloud base height in feet (1 foot is 0.3048 m) for December 2018 with (<b>a</b>) HARMONIE-AROME Cycle 40 [<a href="#B1-meteorology-03-00018" class="html-bibr">1</a>] and (<b>b</b>) HARMONIE-AROME Cycle 40, with all of the updates described in [<a href="#B39-meteorology-03-00018" class="html-bibr">39</a>], as also applied to HARMONIE-AROME Cycle 43 and 46. The blue, green, and orange lines refer to +3, +24, and +48 h forecasts, respectively. European Geosciences Union 2022, from Figure 20 of [<a href="#B39-meteorology-03-00018" class="html-bibr">39</a>].</p>
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<p>Vertical profile of the variance in s (the distance to the saturation curve) for the 10th hour of the simulation of the ARM cumulus case [<a href="#B44-meteorology-03-00018" class="html-bibr">44</a>]. Results for the DALES model are in blue, the reference HARMONIE-AROME Cycle 40 [<a href="#B1-meteorology-03-00018" class="html-bibr">1</a>] (cy40 REF) is in orange, and HARMONIE-AROME Cycle 40 with all the updates described in [<a href="#B39-meteorology-03-00018" class="html-bibr">39</a>], which corresponds to HARMONIE-AROME Cycle 46, (cy40 NEW), is in green. European Geosciences Union 2022, from Figure 12 in [<a href="#B39-meteorology-03-00018" class="html-bibr">39</a>].</p>
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<p>The average modeled wind speed at 90 m height when the WFP is included (contours) and aircraft measurements from the WIPAFF campaign [<a href="#B53-meteorology-03-00018" class="html-bibr">53</a>], located between 80 and 100 m height (colored dots), for 6 September 2016, 8–10 UTC. The black dots indicate the locations of the wind turbines included in the simulation.</p>
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<p>Land cover types over Iceland in (<b>a</b>) the original ECOSG and (<b>b</b>) an improved version of ECOSG. Land cover types over southern Greenland in (<b>c</b>) the original ECOSG and (<b>d</b>) an improved version of ECOSG.</p>
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<p>10 m wind-speed bias and RMSE over Ireland for HARMONIE-AROME Cycle 40 (red), HARMONIE-AROME Cycle 43 default (green), and HARMONIE-AROME Cycle 43 “LFAKETREE” (blue) for 2 two week periods. (<b>a</b>) Spring (<b>b</b>) summer.</p>
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<p>Snow water equivalent (<math display="inline"><semantics> <msub> <mi mathvariant="normal">W</mi> <mrow> <mi>s</mi> <mi>n</mi> </mrow> </msub> </semantics></math>) dependency on time (hours) during melting for different values of <span class="html-italic">p</span>, where <span class="html-italic">p</span> is the replacement for <math display="inline"><semantics> <msub> <mi mathvariant="normal">f</mi> <mrow> <mi>s</mi> <mi>n</mi> </mrow> </msub> </semantics></math> in Equation (<a href="#FD5-meteorology-03-00018" class="html-disp-formula">5</a>).</p>
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<p>The difference in latent heat fluxes between eddy correlation measurements from the EUREC<sup>4</sup>A field campaign of January and February 2020 and model simulations with the ECUME (<b>a</b>) and ECUME6 (<b>b</b>) schemes. The biases are plotted in the phase-space of the specific humidity difference dq (between surface (qs) and 2 m (qa 2 m)) and 10 m wind speed. These plots are reproduced from Figures <math display="inline"><semantics> <mrow> <mn>4.15</mn> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <mn>4.16</mn> </mrow> </semantics></math> in [<a href="#B84-meteorology-03-00018" class="html-bibr">84</a>].</p>
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<p>Scatter-plots of simulated versus observed values of meteorological variables for experiments with and without FLake. The results of HARMONIE-AROME Cycle 40 forecasts starting from 00 and 12 UTC, and with lead times of 6, 18, 30, and 42 h, are shown for the period 18 May to 1 June 2016. The observations are from 3 SYNOP stations around Lake Ladoga. (<b>a</b>) 2 m temperature, °C, without FLake, (<b>b</b>) 2 m temperature, °C, with FLake (as in Cycle 46), (<b>c</b>) 2 m specific humidity, gkg<sup>−1</sup>, without FLake, (<b>d</b>) 2 m specific humidity, gkg<sup>−1</sup>, with FLake (as in Cycle 46).</p>
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<p>Vertical cross-section of cloud fraction, modeled by HARMONIE-AROME (<b>a</b>), along the blue dashed line in the satellite image (<b>b</b>). The cloud fraction is shown for simulations on 65 and 90 (MC_90) vertical level grids in HARMONIE-AROME for the Swedish domain on the 19th August 2023 at 12 UTC and compared to the satellite image over the Stockholm area (Uppland and Södermanland provinces) on the same date and time. The difference between the two 90-level vertical grids MC_90 and MF_90 available in HARMONIE-AROME is shown in (<b>c</b>), with a zoom-in on the lowest part in (<b>d</b>). MF refers to the Météo France version as used in the AROME-France NWP system, while MC refers to a modification suggested by the MetCoOp developers (see text for further details).</p>
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<p>Scatter plots and their linear regression estimates showing the performance of HARMONIE-AROME Cycle 46 with the implemented RSL parametrization [<a href="#B113-meteorology-03-00018" class="html-bibr">113</a>,<a href="#B114-meteorology-03-00018" class="html-bibr">114</a>] in the atmosphere–surface coupling layer versus flux–gradient observations for momentum (<b>a</b>), 10 m wind speed (<b>b</b>), and (sensible) heat fluxes (<b>c</b>,<b>d</b>). For validation, the half-hourly observed fluxes, as well as the wind speed above the canopy, are used, taken from the <a href="https://data.icos-cp.eu/portal/" target="_blank">https://data.icos-cp.eu/portal/</a> (accessed on 27 October 2024) and collected at four ICOS forest sites (Bilos, Norunda, Hyltemossa, and Svartberget) between 15 August and 15 September 2021. The corresponding model data were extracted from the nearest model grid points.</p>
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<p>Show case of the physiography developments planned to be integrated in HARMONIE-AROME in the future. Currently, HARMONIE-AROME uses the ECOSG database (<b>a</b>,<b>d</b>). The land cover map obtained with the agreement-based combination (ECOSG+, (<b>b</b>,<b>e</b>)) and the one obtained with machine learning (ECOSG-ML, (<b>c</b>,<b>f</b>)) are both at 60 m resolution. ECOSG+ and ECOSG-ML show increasing qualitative benefits; see [<a href="#B116-meteorology-03-00018" class="html-bibr">116</a>,<a href="#B117-meteorology-03-00018" class="html-bibr">117</a>] for the evaluation. The coordinates of the center points are given on the left hand side for both sites. Patches are approximately 25 km × 25 km in size. Colors represent different land cover types.</p>
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<p>Bias and standard deviation in low cloud cover for (<b>a</b>) a summer period (1–14 June 2018) and (<b>b</b>) a winter period (3–17 February 2020) for HARMONIE-AROME cycle 40 (red) and cycle 46 (blue) compared to observations recorded at 140 stations in Ireland and the UK. The data shown are from forecasts starting from 00 and 12 UTC for forecast lengths of up to 33 h.</p>
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20 pages, 2003 KiB  
Article
Enhanced Curvature-Based Fabric Defect Detection: A Experimental Study with Gabor Transform and Deep Learning
by Mehmet Erdogan and Mustafa Dogan
Algorithms 2024, 17(11), 506; https://doi.org/10.3390/a17110506 - 5 Nov 2024
Viewed by 447
Abstract
Quality control at every stage of production in the textile industry is essential for maintaining competitiveness in the global market. Manual fabric defect inspections are often characterized by low precision and high time costs, in contrast to intelligent anomaly detection systems implemented in [...] Read more.
Quality control at every stage of production in the textile industry is essential for maintaining competitiveness in the global market. Manual fabric defect inspections are often characterized by low precision and high time costs, in contrast to intelligent anomaly detection systems implemented in the early stages of fabric production. To achieve successful automated fabric defect identification, significant challenges must be addressed, including accurate detection, classification, and decision-making processes. Traditionally, fabric defect classification has relied on inefficient and labor-intensive human visual inspection, particularly as the variety of fabric defects continues to increase. Despite the global chip crisis and its adverse effects on supply chains, electronic hardware costs for quality control systems have become more affordable. This presents a notable advantage, as vision systems can now be easily developed with the use of high-resolution, advanced cameras. In this study, we propose a discrete curvature algorithm, integrated with the Gabor transform, which demonstrates significant success in near real-time defect classification. The primary contribution of this work is the development of a modified curvature algorithm that achieves high classification performance without the need for training. This method is particularly efficient due to its low data storage requirements and minimal processing time, making it ideal for real-time applications. Furthermore, we implemented and evaluated several other methods from the literature, including Gabor and Convolutional Neural Networks (CNNs), within a unified coding framework. Each defect type was analyzed individually, with results indicating that the proposed algorithm exhibits comparable success and robust performance relative to deep learning-based approaches. Full article
(This article belongs to the Special Issue Algorithms for Image Processing and Machine Vision)
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<p>(<b>a</b>) Experimental Setup. (<b>b</b>) Close-Up View of Experimental Setup.</p>
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<p>Defect data-set type hole, none, needle break, lycra, may (<b>left</b> to <b>right</b>).</p>
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<p>Fabric with simple defect.</p>
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<p>Fabric image with Canny edge detector.</p>
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<p>Contour Pieces.</p>
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<p>(<b>A</b>) Standard curve with points. (<b>B</b>) Calculation of discreate curvature.</p>
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<p>Curvature radius values.</p>
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<p>Exterior angle values.</p>
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<p>Curvature radius vs exterior angle.</p>
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<p>(<b>A</b>) Sample Curve, (<b>B</b>) Standard Curvature, (<b>C</b>) Optimized Curvature, (<b>D</b>) Efficient Curvature.</p>
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<p>Defect detection with modified discrete curvature function.</p>
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<p>MDCA Sample Fabric (<b>left</b> side) detected defects. (<b>rigth</b> side).</p>
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<p>Comparision CA and MDCA algorithms (<b>a</b>) original (<b>b</b>) CA (<b>c</b>) MDCA.</p>
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<p>Fabric image captured on experimental setup.</p>
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<p>Gabor filter on fabric with defect.</p>
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<p>Gabor filter on local fabric image.</p>
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<p>(<b>a</b>) model accuracy, (<b>b</b>) model loss.</p>
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<p>Fabric image dataset with defects.</p>
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<p>Fabric defect detection and label with Cnn.</p>
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23 pages, 3124 KiB  
Article
Quantification of Size-Binned Particulate Matter in Electronic Cigarette Aerosols Using Multi-Spectral Optical Sensing and Machine Learning
by Hao Jiang and Keith Kolaczyk
Sensors 2024, 24(21), 7082; https://doi.org/10.3390/s24217082 - 3 Nov 2024
Viewed by 701
Abstract
To monitor health risks associated with vaping, we introduce a multi-spectral optical sensor powered by machine learning for real-time characterization of electronic cigarette aerosols. The sensor can accurately measure the mass of particulate matter (PM) in specific particle size channels, providing essential information [...] Read more.
To monitor health risks associated with vaping, we introduce a multi-spectral optical sensor powered by machine learning for real-time characterization of electronic cigarette aerosols. The sensor can accurately measure the mass of particulate matter (PM) in specific particle size channels, providing essential information for estimating lung deposition of vaping aerosols. For the sensor’s input, wavelength-specific optical attenuation signals are acquired for three separate wavelengths in the ultraviolet, red, and near-infrared range, and the inhalation pressure is collected from a pressure sensor. The sensor’s outputs are PM mass in three size bins, specified as 100–300 nm, 300–600 nm, and 600–1000 nm. Reference measurements of electronic cigarette aerosols, obtained using a custom vaping machine and a scanning mobility particle sizer, provided the ground truth for size-binned PM mass. A lightweight two-layer feedforward neural network was trained using datasets acquired from a wide range of puffing conditions. The performance of the neural network was tested using unseen data collected using new combinations of puffing conditions. The model-predicted values matched closely with the ground truth, and the accuracy reached 81–87% for PM mass in three size bins. Given the sensor’s straightforward optical configuration and the direct collection of signals from undiluted vaping aerosols, the achieved accuracy is notably significant and sufficiently reliable for point-of-interest sensing of vaping aerosols. To the best of our knowledge, this work represents the first instance where machine learning has been applied to directly characterize high-concentration undiluted electronic cigarette aerosols. Our sensor holds great promise in tracking electronic cigarette users’ puff topography with quantification of size-binned PM mass, to support long-term personalized health and wellness. Full article
(This article belongs to the Special Issue Optical Spectroscopic Sensing and Imaging)
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<p>Schematic for the concept of a multi-spectral optical sensor for measuring the size-binned mass of particulate matter (PM) in e-cigarette aerosols using a neural network. (<b>a</b>) Schematic of optical configuration and the algorithm. (<b>b</b>) Scattering efficiency spectra for three wavelengths calculated based on Mie theory. (<b>c</b>) Schematic of mass of PM in three size bins.</p>
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<p>A prototype of a multi-spectral sensor for e-cigarette aerosols based on three wavelengths. (<b>a</b>) Photograph of the constructed sensor box connected to an electronic cigarette. (<b>b</b>) A 3-D schematic of the fundamental functional modules of the sensor, including a photometric module and a pressure module. (<b>c</b>) Design diagram and (<b>d</b>) photograph showing the cross-sectional view of the optical configuration inside the photometric module. (<b>e</b>) Diagram for the sensor circuit and data collection.</p>
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<p>Acquisition and preparation of data for training, validation, and testing of the neural network model. The example sensor signals and reference measurement results were collected from puff No. 30 listed in <a href="#app1-sensors-24-07082" class="html-app">Table S1</a>. (<b>a</b>) Schematic of the experimental setup and flowcharts for sensor signal processing and reference measurement of size-binned PM mass. (<b>b</b>) Raw optical signals of the three wavelengths and raw pressure signal. (<b>c</b>) Calculated optical attenuation for three wavelengths and inhalation pressure. (<b>d</b>) Calculated integrals of optical attenuation and mean inhalation pressure, which are used as predictors (model input). (<b>e</b>) Number concentration of PM in the dilution box. (<b>f</b>) Mass concentration of PM in the dilution box. (<b>g</b>) Measured mass of total PM in three size bins, which are used as responses (model output).</p>
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<p>Training, validation, and testing of the neural network. (<b>a</b>) Schematic of the two-layer feedforward neural network model. (<b>b</b>) Integrals of optical attenuation, (<b>c</b>) mean inhalation pressure, and (<b>d</b>) measured size-binned PM mass collected from the 100 puffs with varying e-cigarette puffing conditions for training and validation of the model. (<b>e</b>) Integrals of optical attenuation and (<b>f</b>) mean inhalation pressure collected from the 10 additional puffs for testing the model with unseen data. Comparison of the PM mass by reference measurement (target) and the PM mass calculated by the model (predicted) for (<b>g</b>) size bin #1 (100–300 nm), (<b>h</b>) size bin #2 (300–600 nm), and (<b>i</b>) size bin #3 (600–1000 nm).</p>
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<p>Experimental results of four exemplary puffs used for testing the model. (<b>a</b>) Sensor signals, (<b>b</b>) measured PM mass concentration of the diluted aerosol, and (<b>c</b>) the target and model-predicted PM mass for the three size bins from puff No. 1. (<b>d</b>–<b>f</b>) Results from puff No. 4. (<b>g</b>–<b>i</b>) Results from puff No. 7. (<b>j</b>–<b>l</b>) Results from puff No. 10.</p>
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23 pages, 23514 KiB  
Article
Deep-Learning-Based Automated Building Construction Progress Monitoring for Prefabricated Prefinished Volumetric Construction
by Wei Png Chua and Chien Chern Cheah
Sensors 2024, 24(21), 7074; https://doi.org/10.3390/s24217074 - 2 Nov 2024
Viewed by 837
Abstract
Prefabricated prefinished volumetric construction (PPVC) is a relatively new technique that has recently gained popularity for its ability to improve flexibility in scheduling and resource management. Given the modular nature of PPVC assembly and the large amounts of visual data amassed throughout a [...] Read more.
Prefabricated prefinished volumetric construction (PPVC) is a relatively new technique that has recently gained popularity for its ability to improve flexibility in scheduling and resource management. Given the modular nature of PPVC assembly and the large amounts of visual data amassed throughout a construction project today, PPVC building construction progress monitoring can be conducted by quantifying assembled PPVC modules within images or videos. As manually processing high volumes of visual data can be extremely time consuming and tedious, building construction progress monitoring can be automated to be more efficient and reliable. However, the complex nature of construction sites and the presence of nearby infrastructure could occlude or distort visual data. Furthermore, imaging constraints can also result in incomplete visual data. Therefore, it is hard to apply existing purely data-driven object detectors to automate building progress monitoring at construction sites. In this paper, we propose a novel 2D window-based automated visual building construction progress monitoring (WAVBCPM) system to overcome these issues by mimicking human decision making during manual progress monitoring with a primary focus on PPVC building construction. WAVBCPM is segregated into three modules. A detection module first conducts detection of windows on the target building. This is achieved by detecting windows within the input image at two scales by using YOLOv5 as a backbone network for object detection before using a window detection filtering process to omit irrelevant detections from the surrounding areas. Next, a rectification module is developed to account for missing windows in the mid-section and near-ground regions of the constructed building that may be caused by occlusion and poor detection. Lastly, a progress estimation module checks the processed detections for missing or excess information before performing building construction progress estimation. The proposed method is tested on images from actual construction sites, and the experimental results demonstrate that WAVBCPM effectively addresses real-world challenges. By mimicking human inference, it overcomes imperfections in visual data, achieving higher accuracy in progress monitoring compared to purely data-driven object detectors. Full article
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<p>Images that depict PPVC buildings under construction.</p>
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<p>Images of PPVC modules taken from different angles.</p>
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<p>Examples of pure window detection output by a finetuned YOLOv5-S [<a href="#B32-sensors-24-07074" class="html-bibr">32</a>] object detection model. Issues identified within each image: (<b>a</b>) detection of irrelevant or erroneous windows; (<b>b</b>) heavy machinery, construction materials, and temporary constructs causing occlusion of windows; (<b>c</b>) missed windows during detection due to small scale; and (<b>d</b>) missed windows due to sub-optimal camera angles causing some window columns to be out of frame or occluded.</p>
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<p>The architecture of WAVBCPM comprises the detection, rectification, and progress estimation modules. The detection module detects windows on the target building within an image and eliminates irrelevant detections. The rectification module accounts for missed window detections due to occlusion or poor detection. Lastly, the progress estimation module extracts relevant information from the processed window detections to estimate building construction progress.</p>
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<p>Two-scale window detection pipeline.</p>
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<p>(<b>a</b>) Initial set of detected windows before filtering. Detections (<b>b</b>) after building mask filtering and (<b>c</b>) vertical vectorisation.</p>
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<p>Output window columns predicted by vertical vectorisation are annotated by line vectors. Through vertical vectorisation and the implemented vectorisation checks, erroneous and irrelevant window detections that passed through building mask filtering could be identified and removed.</p>
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<p>Mid-section (<b>a</b>) identification and (<b>b</b>) rectification of missing windows. Bounding boxes that were added during rectification are annotated in green.</p>
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<p>A visual representation of near-ground missing window rectification. Yellow boxes represent the shortlisted boxes used to estimate the horizontal line vector. Green boxes represent added boxes used to rectify near-ground missing windows. Red boxes represent window predictions that were unused for the rectification step.</p>
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<p>End-stage detection conducted on output columns of windows represented by red boxes. Blue boxes represent window predictions that were filtered by earlier procedures. A window column is determined to be complete if a green circle is annotated above it.</p>
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<p>Output window columns represented by red and green boxes are assessed. Blue boxes represent window predictions that were filtered by earlier procedures. For this given image, there are several missing window columns.</p>
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<p>Images from test set A that were taken by the authors from construction sites around Singapore.</p>
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<p>Detection outputs of (<b>a</b>) WAVBCPM and (<b>b</b>) POD (YOLOv5-S) for test set A.</p>
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<p>The POD (YOLOv5-S) model encountered significant errors when estimating progress for images with infrastructure-dense backgrounds due to many irrelevant detections (<b>a</b>). Conversely, WAVBCPM was shown to be able to pinpoint the target building and evaluate its progress accurately (<b>b</b>).</p>
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<p>Missed and irrelevant windows can occur concurrently and offset each other during progress estimation by POD (<b>a</b>). In contrast, detection errors were rectified prior to progress estimation by WAVBCPM (<b>b</b>).</p>
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22 pages, 9742 KiB  
Article
Three-Dimensional Thermohaline Reconstruction Driven by Satellite Sea Surface Data Based on Sea Ice Seasonal Variation in the Arctic Ocean
by Xiangyu Wu, Jinlong Li, Xidong Wang, Zikang He, Zhiqiang Chen, Shihe Ren and Xi Liang
Remote Sens. 2024, 16(21), 4072; https://doi.org/10.3390/rs16214072 - 31 Oct 2024
Viewed by 419
Abstract
This study investigates and evaluates methods for the three-dimensional thermohaline reconstruction of the Arctic Ocean using multi-source observational data. A multivariate statistical regression model based on sea ice seasonal variation is developed, driving by satellite data, and in situ data is used to [...] Read more.
This study investigates and evaluates methods for the three-dimensional thermohaline reconstruction of the Arctic Ocean using multi-source observational data. A multivariate statistical regression model based on sea ice seasonal variation is developed, driving by satellite data, and in situ data is used to validate the model output. The study indicates that the multivariate statistical regression model effectively captures the characteristics of the three-dimensional thermohaline structure of the Arctic Ocean. Areas with large reconstruction errors are primarily observed in the salinity values of ice-free regions and the temperature values of ice-covered regions. The statistical regression experiments reveal that salinity errors in ice-free regions are caused by inaccuracies in the satellite salinity data, while temperature errors in ice-covered areas mainly result from the inadequate representation of the under-ice temperature structure of the reanalysis data. The continuous and stable thermohaline data produced using near real-time satellite data as input provide an important foundation for studying Arctic marine environmental characteristics and assessing climate change. Full article
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<p>Study area (60°N–90°N). The two green lines are the positions of the cross-sections analysis; details are in Figure 9. The two black lines are the traces of Argo and ITP that we chose in a period; details are in Figure 11 and Figure 12. The four star points are the positions we chose to show the comparation of three kinds of data; details are in Figure 14. The pink and blue dots stand for the positions that we chose from the in situ dataset.</p>
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<p>Reconstruction process of the three-dimensional thermohaline structure.</p>
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<p>Comparison of ocean heat content between the ideal experiment and PHC climatology. Where (<b>a</b>,<b>b</b>) show the ocean heat contents above 700 m for March and September, respectively, from the ideal experiment; and (<b>c</b>,<b>d</b>) show those for the same months from the PHC climatology.</p>
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<p>RMSE of ideal experiment and PHC climatology based on field observations. Where (<b>a</b>) shows the temperature RMSE, and (<b>b</b>) shows the salinity RMSE.</p>
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<p>Comparison of reconstructed temperature and TOPAZ reanalysis on 15 March 2020. Where (<b>a</b>–<b>c</b>), respectively, show the reconstructed temperature field, TOPAZ temperature field, and the difference between the reconstructed and TOPAZ temperature fields at 10 m; (<b>d</b>–<b>f</b>) show those at 200 m; and (<b>g</b>–<b>i</b>) show those at 1200 m.</p>
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<p>Comparison of reconstructed salinity field and TOPAZ reanalysis on 15 March 2020. Where (<b>a</b>–<b>c</b>), respectively, show the reconstructed salinity field, TOPAZ salinity field, and the difference between the reconstructed and TOPAZ salinity fields at 10 m; (<b>d</b>–<b>f</b>) show those at 200 m; and (<b>g</b>–<b>i</b>) show those at 1200 m.</p>
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<p>Comparison of reconstructed temperature and TOPAZ reanalysis on 15 September 2020. Where (<b>a</b>–<b>c</b>), respectively, show the reconstructed temperature field, TOPAZ temperature field, and the difference between the reconstructed and TOPAZ temperature fields at 10 m; (<b>d</b>–<b>f</b>) show those at 200 m; and (<b>g</b>–<b>i</b>) show those at 1200 m.</p>
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<p>Comparison of reconstructed salinity field and TOPAZ reanalysis on 15 September 2020. Where (<b>a</b>–<b>c</b>), respectively, show the reconstructed salinity field, TOPAZ salinity field, and the difference between the reconstructed and TOPAZ salinity fields at 10 m; (<b>d</b>–<b>f</b>) show those at 200 m; and (<b>g</b>–<b>i</b>) show those at 1200 m.</p>
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<p>Thermohaline cross-sections of reconstructed data and reanalysis data on 15 September 2020. Where (<b>a</b>,<b>b</b>), respectively, show the reconstructed and reanalysis temperature results for the 2.5°W cross-section; (<b>c</b>,<b>d</b>) show those for the 2.5°W cross-section; (<b>e</b>,<b>f</b>) show those for the 168°W cross-section; and (<b>g</b>,<b>h</b>) show those for the 168°W cross-section.</p>
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<p>Average curves of field observations, reconstructed data, and reanalysis data. Where (<b>a</b>,<b>b</b>) show the average temperature and salinity values for Area B, respectively; and (<b>c</b>,<b>d</b>) show the same values for Area A. The black, red and blue lines, respectively, represent the observed values, reconstructed data, and reanalysis data.</p>
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<p>Time series of thermohaline structures from Argo data, satellite-driven reconstructed data, reanalysis data, and ideal experiment. Where (<b>a</b>–<b>d</b>), respectively, show the temperature time series from the Argo data, reconstructed data, reanalysis data, and ideal experiment; and (<b>e</b>–<b>h</b>) show the salinity time series from the same data sets.</p>
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<p>Time series of thermohaline structures from ITP data, satellite-driven reconstructed data, reanalysis data, and ideal experiment. Where (<b>a</b>–<b>d</b>), respectively, show the temperature time series from the ITP data, reconstructed data, reanalysis data, and ideal experiment; and (<b>e</b>–<b>h</b>) show the salinity time series from the same datasets.</p>
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<p>Where (<b>a</b>) shows the SST from satellite data, observational data (Argo 3901620), and reanalysis surface data for ice-free areas; (<b>b</b>) shows the same data for SSS; (<b>c</b>) shows the temperature RMSE of ideal experiment and satellite-driven inversion results compared to the Argo 3901620 data; (<b>d</b>) shows the same data for salinity; (<b>e</b>) presents the SST from the satellite data, observational data (ITP 110), and reanalysis surface data for ice-covered areas; (<b>f</b>) shows the same data for SLA; (<b>g</b>) illustrates the temperature RMSE of ideal experiment and satellite-driven inversion results compared to ITP 110 data; and (<b>h</b>) shows the same data for salinity.</p>
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<p>Where (<b>a</b>) shows the temperature from in situ observation, reconstruction, and reanalysis data at point 1; (<b>b</b>) shows the same data for salinity at point 1; (<b>c</b>,<b>d</b>) show those at point 2; (<b>e</b>,<b>f</b>) show those at point 3; (<b>g</b>,<b>h</b>) show those at point 4.</p>
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