[go: up one dir, main page]

 
 
Sign in to use this feature.

Years

Between: -

Subjects

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Journals

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Article Types

Countries / Regions

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Search Results (534)

Search Parameters:
Keywords = inter-calibration

Order results
Result details
Results per page
Select all
Export citation of selected articles as:
16 pages, 2035 KiB  
Article
Performance Assessment of an Electrostatic Filter-Diverter Stent Cerebrovascular Protection Device: Evaluation of a Range of Potential Electrostatic Fields Focusing on Small Particles
by Beatriz Eguzkitza, José A. Navia, Guillaume Houzeaux, Constantine Butakoff and Mariano Vázquez
Bioengineering 2024, 11(11), 1127; https://doi.org/10.3390/bioengineering11111127 - 8 Nov 2024
Viewed by 425
Abstract
Silent Brain Infarction (SBI) is increasingly recognized in patients with cardiac conditions, particularly Atrial Fibrillation (AF) in elderly patients and those undergoing Transcatheter Aortic Valve Implantation (TAVI). While these infarcts often go unnoticed due to a lack of acute symptoms, they are associated [...] Read more.
Silent Brain Infarction (SBI) is increasingly recognized in patients with cardiac conditions, particularly Atrial Fibrillation (AF) in elderly patients and those undergoing Transcatheter Aortic Valve Implantation (TAVI). While these infarcts often go unnoticed due to a lack of acute symptoms, they are associated with a threefold increase in stroke risk and are considered a precursor to ischemic stroke. Moreover, accumulating evidence suggests that SBI may contribute to the development of dementia, depression, and cognitive decline, particularly in the elderly population. The burden of SBI is substantial, with studies showing that up to 11 million Americans may experience a silent stroke annually. In AF patients, silent brain infarcts are common and can lead to progressive brain damage, even in those receiving anticoagulation therapy. The use of cerebral embolic protection devices (CEPDs) during TAVI has been explored to mitigate the risk of stroke; however, their efficacy remains under debate. Despite advancements in TAVI technology, cerebrovascular events, including silent brain lesions, continue to pose significant challenges, underscoring the need for improved preventive strategies and therapeutic approaches. We propose a device consisting of a strut structure placed at the base of the treated artery to model the potential risk of cerebral embolisms caused by atrial fibrillation, thromboembolism, or dislodged debris of varying potential TAVI patients. The study has been carried out in two stages. Both are based on computational fluid dynamics (CFD) coupled with the Lagrangian particle tracking method. The first stage of the work evaluates a variety of strut thicknesses and inter-strut spacings, contrasting with the device-free baseline geometry. The analysis is carried out by imposing flow rate waveforms characteristic of healthy and AF patients. Boundary conditions are calibrated to reproduce physiological flow rates and pressures in a patient’s aortic arch. In the second stage, the optimal geometric design from the first stage was employed, with the addition of lateral struts to prevent the filtration of particles and electronegatively charged strut surfaces, studying the effect of electrical forces on the clots if they are considered charged. Flowrate boundary conditions were used to emulate both healthy and AF conditions. Results from numerical simulations coming from the first stage indicate that the device blocks particles of sizes larger than the inter-strut spacing. It was found that lateral strut space had the highest impact on efficacy. Based on the results of the second stage, deploying the electronegatively charged device in all three aortic arch arteries, the number of particles entering these arteries was reduced on average by 62.6% and 51.2%, for the healthy and diseased models respectively, matching or surpassing current oral anticoagulant efficacy. In conclusion, the device demonstrated a two-fold mechanism for filtering emboli: (1) while the smallest particles are deflected by electrostatic repulsion, avoiding micro embolisms, which could lead to cognitive impairment, the largest ones are mechanically filtered since they cannot fit in between the struts, effectively blocking the full range of particle sizes analyzed in this study. The device presented in this manuscript offers an anticoagulant-free method to prevent stroke and SBIs, imperative given the growing population of AF and elderly patients. Full article
(This article belongs to the Special Issue Computational Models in Cardiovascular System)
Show Figures

Figure 1

Figure 1
<p>Aortic arch geometry. In the original geometry, the main vessels were segmented manually and recreated based on a CT scan of a cadaver. Left ventricle, aortic valve and coronary arteries have been replaced in the inlet by a rigid tube, and superior mesenteric, iliac and renal arteries have been dismissed at the outlet. As highlighted in the zoomed-in figure on the right, extrusion extensions have been employed at the vessel outlets to enhance the stability of the simulated flux.</p>
Full article ">Figure 2
<p>Geometry of the aortic arch and zoom-in of the deflectors deployed at all three arteries.</p>
Full article ">Figure 3
<p>New deflector design. Lateral struts added are circled in red.</p>
Full article ">Figure 4
<p>HP/TAVI: Tables of efficiency defined in Equation (<a href="#FD1-bioengineering-11-01127" class="html-disp-formula">1</a>) for all electrical fields (ranging from 1 to 4 different intensities) generated with the applied superficial charge: (−24,000, −48,000, −75,000, −100,000 [statC/m<sup>2</sup>]) on the three devices positioned at the bases of the arteries, illustrated with the arrows.</p>
Full article ">Figure 5
<p>HP/TAVI—Field 1 (based on a device superficial charge of −24,000 statC/m<sup>2</sup>): Efficiency in each artery.</p>
Full article ">Figure 6
<p>HP/TAVI—Field 2 (based on a device superficial charge of −48,000 [statC/m<sup>2</sup>]): Efficiency in each artery.</p>
Full article ">Figure 7
<p>HP/TAVI—Field 3 (based on a device superficial charge of −75,000 [statC/m<sup>2</sup>]): Efficiency in each artery.</p>
Full article ">Figure 8
<p>HP/TAVI—Field 4 (based on a device superficial charge of −100,000 [statC/m<sup>2</sup>]): Efficiency in each artery.</p>
Full article ">Figure 9
<p>AF patient: Tables of efficiency defined in Equation (<a href="#FD1-bioengineering-11-01127" class="html-disp-formula">1</a>) for all electrical fields (ranging from 1 to 4 different intensities) generated with the applied superficial charge: (−24,000, −48,000, −75,000, −100,000 [statC/m<sup>2</sup>]) on the three devices positioned at the bases of the arteries, illustrated with the arrows.</p>
Full article ">Figure 10
<p>AF patient—Field 1 (based on a device superficial charge of −24,000 [statC/m<sup>2</sup>]): Efficiency in each artery.</p>
Full article ">Figure 11
<p>AF patient—Field 2 (based on a device superficial charge of −48,000 [statC/m<sup>2</sup>]): Efficiency in each artery.</p>
Full article ">Figure 12
<p>AF patient—Field 3(based on a device superficial charge of −75,000 [statC/m<sup>2</sup>]): Efficiency in each artery.</p>
Full article ">Figure 13
<p>AF patient—Field 4 (based on a device superficial charge of −100,000 [statC/m<sup>2</sup>]): Efficiency in each artery.</p>
Full article ">
17 pages, 4818 KiB  
Article
Fault Diagnosis for Rolling Bearings Under Complex Working Conditions Based on Domain-Conditioned Adaptation
by Xu Zhang and Gaoquan Gu
Machines 2024, 12(11), 787; https://doi.org/10.3390/machines12110787 - 7 Nov 2024
Viewed by 360
Abstract
To address the issue of low diagnostic accuracy caused by noise interference and varying rotational speeds in rolling bearings, a fault diagnosis method based on domain-conditioned feature correction is proposed for rolling bearings under complex working conditions. The approach first constructs a multi-scale [...] Read more.
To address the issue of low diagnostic accuracy caused by noise interference and varying rotational speeds in rolling bearings, a fault diagnosis method based on domain-conditioned feature correction is proposed for rolling bearings under complex working conditions. The approach first constructs a multi-scale self-calibrating convolutional neural network to aggregate input signals across different scales, adaptively establishing long-range spatial and inter-channel dependencies at each spatial location, thereby enhancing feature modeling under noisy conditions. Subsequently, a domain-conditioned adaptation strategy is introduced to dynamically adjust the activation of self-calibrating convolution channels in response to the differences between source and target domain inputs, generating correction terms for target domain features to facilitate effective domain-specific knowledge extraction. The method then aligns source and target domain features by minimizing inter-domain feature distribution discrepancies, explicitly mitigating the distribution variations induced by changes in working conditions. Finally, within a structural risk minimization framework, model parameters are iteratively optimized to achieve minimal distribution discrepancy, resulting in an optimal coefficient matrix for fault diagnosis. Experimental results using variable working condition datasets demonstrate that the proposed method consistently achieves diagnostic accuracies exceeding 95%, substantiating its feasibility and effectiveness. Full article
(This article belongs to the Section Machines Testing and Maintenance)
Show Figures

Figure 1

Figure 1
<p>Overall structure.</p>
Full article ">Figure 2
<p>Self-calibrated convolutions.</p>
Full article ">Figure 3
<p>Inception module.</p>
Full article ">Figure 4
<p>Test rig.</p>
Full article ">Figure 5
<p>The accuracy comparison curve of various methods for the A → A diagnosis task.</p>
Full article ">Figure 6
<p>Feature distribution of different methods at the same rotational speed (<b>a</b>) Feature distribution of EMD + SVM; (<b>b</b>) feature distribution of MCNN; (<b>c</b>) feature distribution of MMDCNN; (<b>d</b>) feature distribution of DAN; (<b>e</b>) feature distribution of proposed method.</p>
Full article ">Figure 7
<p>The accuracy comparison curve of various methods for the B → A diagnosis task.</p>
Full article ">Figure 8
<p>Feature distribution of different methods at the varying rotational speed (<b>a</b>) Feature distribution of EMD + SVM; (<b>b</b>) feature distribution of MCNN; (<b>c</b>) feature distribution of MMDCNN; (<b>d</b>) feature distribution of DAN; (<b>e</b>) feature distribution of proposed method.</p>
Full article ">Figure 9
<p>(<b>a</b>) Probability density plot of the original data; (<b>b</b>) probability density plot of the proposed method.</p>
Full article ">Figure 10
<p>Fault diagnosis results of different methods.</p>
Full article ">Figure 11
<p>Feature distribution of different methods on the SEU dataset at varying rotational speeds (<b>a</b>) Feature distribution of EMD + SVM; (<b>b</b>) feature distribution of MCNN; (<b>c</b>) feature distribution of MMDCNN; (<b>d</b>) feature distribution of DAN; (<b>e</b>) feature distribution of proposed method.</p>
Full article ">
30 pages, 5364 KiB  
Article
Characterizing Chromophoric Dissolved Organic Matter Spatio-Temporal Variability in North Andean Patagonian Lakes Using Remote Sensing Information and Environmental Analysis
by Ayelén Sánchez Valdivia, Lucia G. De Stefano, Gisela Ferraro, Diamela Gianello, Anabella Ferral, Ana I. Dogliotti, Mariana Reissig, Marina Gerea, Claudia Queimaliños and Gonzalo L. Pérez
Remote Sens. 2024, 16(21), 4063; https://doi.org/10.3390/rs16214063 - 31 Oct 2024
Viewed by 607
Abstract
Chromophoric dissolved organic matter (CDOM) is crucial in aquatic ecosystems, influencing light penetration and biogeochemical processes. This study investigates the CDOM variability in seven oligotrophic lakes of North Andean Patagonia using Landsat 8 imagery. An empirical band ratio model was calibrated and validated [...] Read more.
Chromophoric dissolved organic matter (CDOM) is crucial in aquatic ecosystems, influencing light penetration and biogeochemical processes. This study investigates the CDOM variability in seven oligotrophic lakes of North Andean Patagonia using Landsat 8 imagery. An empirical band ratio model was calibrated and validated for the estimation of CDOM concentrations in surface lake water as the absorption coefficient at 440 nm (acdom440, m−1). Of the five atmospheric corrections evaluated, the QUAC (Quick Atmospheric Correction) method demonstrated the highest accuracy for the remote estimation of CDOM. The application of separate models for deep and shallow lakes yielded superior results compared to a combined model, with R2 values of 0.76 and 0.82 and mean absolute percentage errors (MAPEs) of 14% and 22% for deep and shallow lakes, respectively. The spatio-temporal variability of CDOM was characterized over a five-year period using satellite-derived acdom440 values. CDOM concentrations varied widely, with very low values in deep lakes and moderate values in shallow lakes. Additionally, significant seasonal fluctuations were evident. Lower CDOM concentrations were observed during the summer to early autumn period, while higher concentrations were observed in the winter to spring period. A gradient boosting regression tree analysis revealed that inter-lake differences were primarily influenced by the lake perimeter to lake area ratio, mean lake depth, and watershed area to lake volume ratio. However, seasonal CDOM variation was largely influenced by Lake Nahuel Huapi water storage (a proxy for water level variability at a regional scale), followed by precipitation, air temperature, and wind. This research presents a robust method for estimating low to moderate CDOM concentrations, improving environmental monitoring of North Andean Patagonian Lake ecosystems. The results deepen the understanding of CDOM dynamics in low-impact lakes and its main environmental drivers, enhance the ability to estimate lacustrine carbon stocks on a regional scale, and help to predict the effects of climate change on this important variable. Full article
(This article belongs to the Collection Feature Papers for Section Environmental Remote Sensing)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Study area: (<b>a</b>) Nahuel Huapi National Park (Argentina) with the location of San Carlos de Bariloche city; (<b>b</b>) a zoomed-in window displaying a detailed image of Lake Nahuel Huapi, sampling sites, and the weather station; (<b>c</b>) a zoomed-in window displaying a detailed image of the remaining study lakes and sampling sites. The sampling sites are indicated by red triangles (shallow lakes) and yellow circles (deep lakes). The following lakes were included in the study: Lake Nahuel Huapi [three sites: Bahía Lopez (NH-BL), Dina Huapi (NH-DH), and Brazo Rincón (NH-BR)], Lake Moreno Este (two sites: ME-CE and ME-CA), Lake Moreno Oeste (three sites: MO-PU, MO-BA, and MO-PP), Lake Morenito (two sites: MITO-1 and MITO-2), Lake Trébol (one site: TRE), Lake Ezquerra (one site: EZQ), and Lake Escondido (one site: ESC).</p>
Full article ">Figure 2
<p>Scatter plot of field-measured and estimated CDOM absorption coefficients at 440 nm <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mo>(</mo> <mi>a</mi> </mrow> <mrow> <mi>c</mi> <mi>d</mi> <mi>o</mi> <mi>m</mi> </mrow> <mrow> <mn>440</mn> </mrow> </msubsup> <mo>)</mo> </mrow> </semantics></math> in the natural logarithm form using band ratio models of Landsat 8 imagery. Results correspond to validated models using the QUAC routine for all lakes together (<b>a</b>), deep lakes (<b>b</b>), and shallow lakes (<b>c</b>). Model performance metrics are also shown.</p>
Full article ">Figure 3
<p>Boxplots showing the distribution of satellite-derived <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>a</mi> </mrow> <mrow> <mi>c</mi> <mi>d</mi> <mi>o</mi> <mi>m</mi> </mrow> <mrow> <mn>440</mn> </mrow> </msubsup> </mrow> </semantics></math> values for each study lake, ranked from higher to lower retrieved CDOM values. The distributions are presented as boxplots where the central dashed line is the median of the data distribution, and the red diamond represents the mean. The edges of the boxes denote the 25th and 75th percentiles, while the whiskers denote the 10th and 90th percentiles.</p>
Full article ">Figure 4
<p>Mean monthly satellite-derived <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>a</mi> </mrow> <mrow> <mi>c</mi> <mi>d</mi> <mi>o</mi> <mi>m</mi> </mrow> <mrow> <mn>440</mn> </mrow> </msubsup> </mrow> </semantics></math> values for deep study lakes. The mean value for the entire 2016–2020 period is also shown as a grey line in the back and on the right side of each panel for reference. The bars with values lower than the average for the 5-year study period are shown with a striped pattern.</p>
Full article ">Figure 5
<p>Mean monthly satellite-derived <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>a</mi> </mrow> <mrow> <mi>c</mi> <mi>d</mi> <mi>o</mi> <mi>m</mi> </mrow> <mrow> <mn>440</mn> </mrow> </msubsup> </mrow> </semantics></math> values for shallow study lakes. The mean value for the entire 2016–2020 period is also shown as a grey line in the back and on the right side of each panel for reference. The bars with values lower than the average for the 5-year study period are shown with a striped pattern.</p>
Full article ">Figure 6
<p>Maps showing the spatial distribution of satellite-derived <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>a</mi> </mrow> <mrow> <mi>c</mi> <mi>d</mi> <mi>o</mi> <mi>m</mi> </mrow> <mrow> <mn>440</mn> </mrow> </msubsup> <mo> </mo> </mrow> </semantics></math>values in deep study lakes for the low CDOM period (<b>a</b>,<b>c</b>) and the high CDOM period (<b>b</b>,<b>d</b>). The low CDOM period corresponded to the January–April time window and the high CDOM period to the May–December time window. The average raster <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>a</mi> </mrow> <mrow> <mi>c</mi> <mi>d</mi> <mi>o</mi> <mi>m</mi> </mrow> <mrow> <mn>440</mn> </mrow> </msubsup> </mrow> </semantics></math> value for each period is indicated on the left side of the colour legend.</p>
Full article ">Figure 7
<p>Maps showing the spatial distribution of satellite-derived <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>a</mi> </mrow> <mrow> <mi>c</mi> <mi>d</mi> <mi>o</mi> <mi>m</mi> </mrow> <mrow> <mn>440</mn> </mrow> </msubsup> <mo> </mo> </mrow> </semantics></math>values in shallow study lakes for the low CDOM period (<b>a</b>,<b>c</b>,<b>e</b>,<b>g</b>) and the high CDOM period (<b>b</b>,<b>d</b>,<b>f</b>,<b>h</b>). The low CDOM period corresponded to the February–June time window in lakes EZQ and ESC and the February–April time window in lakes MITO and TRE. The high CDOM period corresponded to the July–January time window in lakes EZQ and ESC and the May–January time window in lakes MITO and TRE. The average raster <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>a</mi> </mrow> <mrow> <mi>c</mi> <mi>d</mi> <mi>o</mi> <mi>m</mi> <mo> </mo> </mrow> <mrow> <mn>440</mn> </mrow> </msubsup> </mrow> </semantics></math> value for each period is indicated on the left side of the colour legend.</p>
Full article ">Figure 8
<p>Temporal variability of the main evaluated meteorological variables and water storage of Lake Nahuel Huapi for the 2016–2020 period.</p>
Full article ">Figure 9
<p>GBRT results for the environmental model: (<b>a</b>) linear regression between satellite-derived <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>a</mi> </mrow> <mrow> <mi>c</mi> <mi>d</mi> <mi>o</mi> <mi>m</mi> </mrow> <mrow> <mn>440</mn> </mrow> </msubsup> </mrow> </semantics></math> values vs. estimated values with the environmental model and (<b>b</b>) variable importance rank from the GBRT analysis showing the main explanatory variables for the spatio-temporal variability of satellite-derived <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>a</mi> </mrow> <mrow> <mi>c</mi> <mi>d</mi> <mi>o</mi> <mi>m</mi> </mrow> <mrow> <mn>440</mn> </mrow> </msubsup> </mrow> </semantics></math> values in study lakes. In (<b>a</b>), the training and validation datasets and a zoomed-in panel for deep lakes are shown.</p>
Full article ">Figure 10
<p>Partial dependence plots for the top six explanatory variables from GBRT method. The y-axes (<span class="html-italic">yhat</span>, unitless) represent the marginal effect of the predictor variable on the satellite-derived <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>a</mi> </mrow> <mrow> <mi>c</mi> <mi>d</mi> <mi>o</mi> <mi>m</mi> </mrow> <mrow> <mn>440</mn> </mrow> </msubsup> </mrow> </semantics></math> values.</p>
Full article ">
35 pages, 16179 KiB  
Article
Vegetative Index Intercalibration Between PlanetScope and Sentinel-2 Through a SkySat Classification in the Context of “Riserva San Massimo” Rice Farm in Northern Italy
by Christian Massimiliano Baldin and Vittorio Marco Casella
Remote Sens. 2024, 16(21), 3921; https://doi.org/10.3390/rs16213921 - 22 Oct 2024
Viewed by 1749
Abstract
Rice farming in Italy accounts for about 50% of the EU’s rice area and production. Precision agriculture has entered the scene to enhance sustainability, cut pollution, and ensure food security. Various studies have used remote sensing tools like satellites and drones for multispectral [...] Read more.
Rice farming in Italy accounts for about 50% of the EU’s rice area and production. Precision agriculture has entered the scene to enhance sustainability, cut pollution, and ensure food security. Various studies have used remote sensing tools like satellites and drones for multispectral imaging. While Sentinel-2 is highly regarded for precision agriculture, it falls short for specific applications, like at the “Riserva San Massimo” (Gropello Cairoli, Lombardia, Northern Italy) rice farm, where irregularly shaped crops need higher resolution and frequent revisits to deal with cloud cover. A prior study that compared Sentinel-2 and the higher-resolution PlanetScope constellation for vegetative indices found a seasonal miscalibration in the Normalized Difference Vegetation Index (NDVI) and in the Normalized Difference Red Edge Index (NDRE). Dr. Agr. G.N. Rognoni, a seasoned agronomist working with this farm, stresses the importance of studying the radiometric intercalibration between the PlanetScope and Sentinel-2 vegetative indices to leverage the knowledge gained from Sentinel-2 for him to apply variable rate application (VRA). A high-resolution SkySat image, taken almost simultaneously with a pair of Sentinel-2 and PlanetScope images, offered a chance to examine if the irregular distribution of vegetation and barren land within rice fields might be a factor in the observed miscalibration. Using an unsupervised pixel-based image classification technique on SkySat imagery, it is feasible to split rice into two subclasses and intercalibrate them separately. The results indicated that combining histograms and agronomists’ expertise could confirm SkySat classification. Moreover, the uneven spatial distribution of rice does not affect the seasonal miscalibration object of past studies, which can be adjusted using the methods described here, even with images taken four days apart: the first method emphasizes accuracy using linear regression, histogram shifting, and histogram matching; whereas the second method is faster and utilizes only histogram matching. Full article
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Riserva San Massimo rice farm crops over 3 June 2021. SkySat image—EPSG: 4326.</p>
Full article ">Figure 2
<p>Process flowchart.</p>
Full article ">Figure 3
<p>SkySat unsupervised classification with vegetation in green and barren land in brown.</p>
Full article ">Figure 4
<p>SkySat image compared with the masks produced in MATLAB.</p>
Full article ">Figure 5
<p>Method 1 for NDVI.</p>
Full article ">Figure 6
<p>Method 1 for NDRE.</p>
Full article ">Figure 7
<p>Method 2 for NDVI—LR after HM is not useful for distribution and statistics.</p>
Full article ">Figure 8
<p>Method 2 for NDRE—LR after HM is not useful for distribution and statistics.</p>
Full article ">Figure A1
<p>Method 1 for NDVI—linear regression for full crops.</p>
Full article ">Figure A2
<p>Method 1 for NDVI—linear regression for vegetation subclass.</p>
Full article ">Figure A3
<p>Method 1 for NDVI—linear regression for barren land subclass.</p>
Full article ">Figure A4
<p>Method 1 for NDRE—linear regression for full crops.</p>
Full article ">Figure A5
<p>Method 1 for NDRE—linear regression for vegetation subclass.</p>
Full article ">Figure A6
<p>Method 1 for NDRE—linear regression for barren land subclass.</p>
Full article ">Figure A7
<p>Method 2 for NDVI—linear regression for full crops.</p>
Full article ">Figure A8
<p>Method 2 for NDVI—linear regression for vegetation subclass.</p>
Full article ">Figure A9
<p>Method 2 for NDVI—linear regression for barren land subclass.</p>
Full article ">Figure A10
<p>Method 2 for NDRE—linear regression for full crops.</p>
Full article ">Figure A11
<p>Method 2 for NDRE—linear regression for vegetation subclass.</p>
Full article ">Figure A12
<p>Method 2 for NDRE—linear regression for barren land subclass.</p>
Full article ">
32 pages, 100733 KiB  
Article
On-Orbit Geometric Calibration and Accuracy Validation of the Jilin1-KF01B Wide-Field Camera
by Hongyu Wu, Guanzhou Chen, Yang Bai, Ying Peng, Qianqian Ba, Shuai Huang, Xing Zhong, Haijiang Sun, Lei Zhang and Fuyu Feng
Remote Sens. 2024, 16(20), 3893; https://doi.org/10.3390/rs16203893 - 19 Oct 2024
Viewed by 868
Abstract
On-orbit geometric calibration is key to improving the geometric positioning accuracy of high-resolution optical remote sensing satellite data. Grouped calibration with geometric consistency (GCGC) is proposed in this paper for the Jilin1-KF01B satellite, which is the world’s first satellite capable of providing 150-km [...] Read more.
On-orbit geometric calibration is key to improving the geometric positioning accuracy of high-resolution optical remote sensing satellite data. Grouped calibration with geometric consistency (GCGC) is proposed in this paper for the Jilin1-KF01B satellite, which is the world’s first satellite capable of providing 150-km swath width and 0.5-m resolution data. To ensure the geometric accuracy of high-resolution image data, the GCGC method conducts grouped calibration of the time delay integration charge-coupled device (TDI CCD). Each group independently calibrates the exterior orientation elements to address the multi-time synchronization issues between imaging processing system (IPS). An additional inter-chip geometric positioning consistency constraint is used to enhance geometric positioning consistency in the overlapping areas between adjacent CCDs. By combining image simulation techniques associated with spectral bands, the calibrated panchromatic data are used to generate simulated multispectral reference band image as control data, thereby enhancing the geometric alignment consistency between panchromatic and multispectral data. Experimental results show that the average seamless stitching accuracy of the basic products after calibration is better than 0.6 pixels, the positioning accuracy without ground control points(GCPs) is better than 20 m, the band-to-band registration accuracy is better than 0.3 pixels, the average geometric alignment consistency between panchromatic and multispectral data are better than 0.25 multispectral pixels, the geometric accuracy with GCPs is better than 2.1 m, and the geometric alignment consistency accuracy of multi-temporal data are better than 2 m. The GCGC method significantly improves the quality of image data from the Jilin1-KF01B satellite and provide important references and practical experience for the geometric calibration of other large-swath high-resolution remote sensing satellites. Full article
Show Figures

Figure 1

Figure 1
<p>The diagram of detector look-angle model.</p>
Full article ">Figure 2
<p>CCD stitching and overlap imaging characteristics schematic diagram.</p>
Full article ">Figure 3
<p>Illustration of the large-scale dynamic variation of the y-coordinate differences in mountainous areas.</p>
Full article ">Figure 4
<p>Tie point matching method based on geometric positioning constraints for connection point extraction.</p>
Full article ">Figure 5
<p>Comparison of detailed images of typical land cover types for panchromatic data, red band data, and simulated red band data.</p>
Full article ">Figure 5 Cont.
<p>Comparison of detailed images of typical land cover types for panchromatic data, red band data, and simulated red band data.</p>
Full article ">Figure 6
<p>Jilin1-KF01B WF camera on-orbit geometric calibration of panchromatic and multispectral reference band flow chart.</p>
Full article ">Figure 7
<p>Jilin1-KF01B WF camera on-orbit geometric calibration of multispectral non-reference band flow chart.</p>
Full article ">Figure 8
<p>Calibration data.</p>
Full article ">Figure 9
<p>Comparison of geometric stitching before and after calibration.</p>
Full article ">Figure 10
<p>In-Scene stitching accuracy.</p>
Full article ">Figure 11
<p>RPC fitting accuracy.</p>
Full article ">Figure 12
<p>Geometric positioning consistency accuracy between panchromatic and multispectral data.</p>
Full article ">Figure 13
<p>The distribution of GCPs in experimental regions.</p>
Full article ">Figure 14
<p>Geographic distribution of experimental data.</p>
Full article ">Figure 14 Cont.
<p>Geographic distribution of experimental data.</p>
Full article ">Figure 14 Cont.
<p>Geographic distribution of experimental data.</p>
Full article ">Figure 14 Cont.
<p>Geographic distribution of experimental data.</p>
Full article ">Figure 15
<p>The effect of geometric positioning consistency before and after correction of GanSu data.</p>
Full article ">Figure 16
<p>The effect of geometric positioning consistency before and after correction of LinYi data.</p>
Full article ">Figure 17
<p>The effect of geometric positioning consistency before and after correction of QingDao data.</p>
Full article ">Figure 18
<p>The effect of geometric positioning consistency before and after correction of XinJiang data.</p>
Full article ">Figure A1
<p>Positioning accuracy without GCPs of PMS01-PMS06.</p>
Full article ">Figure A1 Cont.
<p>Positioning accuracy without GCPs of PMS01-PMS06.</p>
Full article ">
14 pages, 2377 KiB  
Article
Development and Validation of an Improved HPLC-MS/MS Method for Quantifying Total and Unbound Lenalidomide in Human Plasma
by Suhyun Lee, Seungwon Yang, Wang-Seob Shim, Eunseo Song, Seunghoon Han, Sung-Soo Park, Suein Choi, Sung Hwan Joo, Seok Jun Park, Beomjin Shin, Donghyun Kim, Hyeonsu Kim, Yujung Jung, Kyung-Tae Lee and Eun Kyoung Chung
Pharmaceutics 2024, 16(10), 1340; https://doi.org/10.3390/pharmaceutics16101340 - 19 Oct 2024
Viewed by 696
Abstract
Background/Objectives: This study aimed to develop a fully validated HPLC-MS/MS method for quantifying total and unbound lenalidomide concentrations in human plasma. Methods: Unbound concentrations were measured using plasma ultrafiltrate prepared with Amicon® Centrifugal Filters. Lenalidomide and lenalidomide-d5 (internal standard) were extracted from [...] Read more.
Background/Objectives: This study aimed to develop a fully validated HPLC-MS/MS method for quantifying total and unbound lenalidomide concentrations in human plasma. Methods: Unbound concentrations were measured using plasma ultrafiltrate prepared with Amicon® Centrifugal Filters. Lenalidomide and lenalidomide-d5 (internal standard) were extracted from 50 μL of human plasma using liquid–liquid extraction. Chromatography was conducted with a Halo® C18 column using 0.1% formic acid and methanol (20:80, v/v) as the mobile phase. The mass spectrometer was operated in a positive ion mode with an electrospray ionization interface and multiple reaction monitoring modes. Results: Calibration curves were linear over the range of 5 to 1000 ng/mL (r2 > 0.996) for both the total and unbound lenalidomide. For total lenalidomide concentrations, between-run precision (coefficients of variation) and accuracy were 1.70–7.65% and 94.45–101.10%, respectively. For unbound concentrations, inter-day precision and accuracy were 1.98–10.55% and 93.95–98.48%, respectively. Conclusions: We developed a highly reproducible, sensitive, and efficient bioanalytical method using a smaller volume of plasma sample (50 μL) with a relatively short run time (2.5 min). The proposed analytical method was successfully applied to measure total and unbound lenalidomide concentrations at various time points in multiple myeloma patients with renal impairment. Full article
Show Figures

Figure 1

Figure 1
<p>Product ion mass spectra and fragmentation of (<b>A</b>) lenalidomide and (<b>B</b>) lenalidomide-d5 (IS). Black arrows highlight the primary product ions at <span class="html-italic">m</span>/<span class="html-italic">z</span> 149 in (<b>A</b>) and <span class="html-italic">m</span><span class="html-italic">/z</span> 151 in (<b>B</b>), crucial for quantitative analysis in multiple reaction monitoring (MRM) mode. Red lines indicate the specific fragmentation sites leading to the formation of these product ions for lenalidomide and lenalidomide-d5, respectively.</p>
Full article ">Figure 2
<p>Process of separating unbound lenalidomide from human plasma.</p>
Full article ">Figure 3
<p>Representative chromatograms for total lenalidomide in plasma using (<b>A</b>) double blank sample, (<b>B</b>) blank sample spiked with lenalidomide-d5 as internal standard (IS, 1000 ng/mL), (<b>C</b>) blank sample spiked with lenalidomide (upper limit of quantification, 1000 ng/mL), (<b>D</b>) blank sample spiked with lenalidomide (lower limit of quantification, 5 ng/mL) and lenalidomide-d5 (IS, 1000 ng/mL). Panels on the left side are for lenalidomide, and those on the right side for IS.</p>
Full article ">Figure 4
<p>Representative chromatograms for unbound lenalidomide in post-ultrafiltration plasma using (<b>A</b>) double blank sample, (<b>B</b>) blank sample spiked with lenalidomide-d5 as internal standard (IS, 1000 ng/mL), (<b>C</b>) blank sample spiked with lenalidomide (upper limit of quantification, 1000 ng/mL), (<b>D</b>) blank sample spiked with lenalidomide (lower limit of quantification, 5 ng/mL) and lenalidomide-d5 (IS, 1000 ng/mL). Panels on the left side are for lenalidomide, and those on the right side for IS.</p>
Full article ">Figure 5
<p>Total and unbound lenalidomide concentrations in plasma from three patients after three days of the first cycle containing oral lenalidomide 25 mg or equivalent dose for renally impaired patients. (<b>A</b>–<b>C</b>) represent the total and unbound plasma concentrations of lenalidomide in each patient.</p>
Full article ">
8 pages, 449 KiB  
Protocol
Validity and Reliability According to the Type of Examiners in the Process of Calibrating Dental Caries Experience Using the DMFT Index
by Anna Paola Fernández-Coll, María Claudia Garcés-Elías, Jorge A. Beltrán, Roberto A. León-Manco and Janett Mas-López
Methods Protoc. 2024, 7(5), 83; https://doi.org/10.3390/mps7050083 - 16 Oct 2024
Viewed by 535
Abstract
The process of examiner calibration is an essential step in all epidemiological research, as it aims to ensure uniform interpretation, understanding, and application of the instrument to be used. This ensures that the data collected will be valid and reliable. This study aimed [...] Read more.
The process of examiner calibration is an essential step in all epidemiological research, as it aims to ensure uniform interpretation, understanding, and application of the instrument to be used. This ensures that the data collected will be valid and reliable. This study aimed to determine the differences in concordance in dental caries calibration across three dental specialties. The population consisted of 45 dentists, divided into three groups: 15 general dentists working in the public sector, 15 dentists specializing in Dental Public Health, and 15 dentists specializing in Restorative and Aesthetic Dentistry. The calibration process was carried out in three stages: theory, calibration using photographs, and calibration on natural teeth, performed by the gold standard. In the first validity process, a statistical difference was only found between the Kappa values of the inter-examiner calibration process using photographs. For the evaluation of teeth, in the second validity process, 33.33% (n = 15) of the participants achieved “almost perfect agreement.” Finally, only 75.56% (n = 34) of the examiners were considered for the reliability report; of this group, 52.94% (n = 18) were in “almost perfect agreement,” and 35.29% (n = 12) were in “substantial agreement.” The validity and reliability of the dental caries experience calibration process did not present significant statistical differences between general dentists in the public sector, dentists specializing in Dental Public Health, and dentists specializing in Restorative and Aesthetic Dentistry. Full article
(This article belongs to the Section Public Health Research)
30 pages, 27337 KiB  
Article
Nested Cross-Validation for HBV Conceptual Rainfall–Runoff Model Spatial Stability Analysis in a Semi-Arid Context
by Mohamed El Garnaoui, Abdelghani Boudhar, Karima Nifa, Yousra El Jabiri, Ismail Karaoui, Abdenbi El Aloui, Abdelbasset Midaoui, Morad Karroum, Hassan Mosaid and Abdelghani Chehbouni
Remote Sens. 2024, 16(20), 3756; https://doi.org/10.3390/rs16203756 - 10 Oct 2024
Viewed by 1198
Abstract
Accurate and efficient streamflow simulations are necessary for sustainable water management and conservation in arid and semi-arid contexts. Conceptual hydrological models often underperform in these catchments due to the high climatic variability and data scarcity, leading to unstable parameters and biased results. This [...] Read more.
Accurate and efficient streamflow simulations are necessary for sustainable water management and conservation in arid and semi-arid contexts. Conceptual hydrological models often underperform in these catchments due to the high climatic variability and data scarcity, leading to unstable parameters and biased results. This study evaluates the stability of the HBV model across seven sub-catchments of the Oum Er Rabia river basin (OERB), focusing on the HBV model regionalization process and the effectiveness of Earth Observation data in enhancing predictive capability. Therefore, we developed a nested cross-validation framework for spatiotemporal stability assessment, using optimal parameters from a donor-single-site calibration (DSSC) to inform target-multi-site calibration (TMSC). The results show that the HBV model remains spatially transferable from one basin to another with moderate to high performances (KGE (0.1~0.9 NSE (0.5~0.8)). Furthermore, calibration using KGE improves model stability over NSE. Some parameter sets exhibit spatial instability, but inter-annual parameter behavior remains stable, indicating potential climate change impacts. Model performance declines over time (18–124%) with increasing dryness. As a conclusion, this study presents a framework for analyzing parameter stability in hydrological models and highlights the need for more research on spatial and temporal factors affecting hydrological response variability. Full article
(This article belongs to the Special Issue Multi-Source Remote Sensing Data in Hydrology and Water Management)
Show Figures

Figure 1

Figure 1
<p>Location of the seven study catchments in the Oum Er Rabia river basin. Land use and Land cover of the study area.</p>
Full article ">Figure 2
<p>HBV (Hydrologiska Byråns Vattenbalansavedelning) model scheme, modified from [<a href="#B83-remotesensing-16-03756" class="html-bibr">83</a>].</p>
Full article ">Figure 3
<p>Work modeling flowchart. Note that the warm-up year (2000–2001) is not included in the original modeling time series.</p>
Full article ">Figure 4
<p>Hydrograph of observed against simulated streamflow in AOCH (donor catchment) and the six target catchments calibrated and validated in the year 2009–2010 (as example).</p>
Full article ">Figure 4 Cont.
<p>Hydrograph of observed against simulated streamflow in AOCH (donor catchment) and the six target catchments calibrated and validated in the year 2009–2010 (as example).</p>
Full article ">Figure 5
<p>Resume of optimal parameter sets versus performance metrics during spatiotemporal cross validation process.</p>
Full article ">Figure 6
<p>Best parameter set variation over seven sub-catchments of the study area.</p>
Full article ">Figure 7
<p>Variation of long-term trend of KGE performance metric across study catchments between 2001 and 2019 (mean: blue line, median: red line, standard deviation: orange line, trend: black line).</p>
Full article ">Figure 8
<p>Variation of long-term trend of NSE performance metric across study catchments between 2001 and 2019 (mean: blue line, median: red line, standard deviation: orange line, trend: black line).</p>
Full article ">Figure 9
<p>Variation of long-term trend of RMSE performance metric across study catchments between 2001 and 2019 (mean: blue line, median: red line, standard deviation: orange line, trend: black line).</p>
Full article ">Figure 10
<p>KGE, NSE, R<sup>2</sup>, and RMSE metric variations for different catchments across years.</p>
Full article ">Figure 11
<p>Variation of long-term trend of optimal parameters, across study catchments over time between 2001 and 2019 (mean: blue line, median: red line, standard deviation: orange line, trend: black line).</p>
Full article ">Figure 11 Cont.
<p>Variation of long-term trend of optimal parameters, across study catchments over time between 2001 and 2019 (mean: blue line, median: red line, standard deviation: orange line, trend: black line).</p>
Full article ">Figure 12
<p>HBV model performance loss assessment over time and space using MRC criterion [<a href="#B98-remotesensing-16-03756" class="html-bibr">98</a>]. Green icon: No performance loss (or performance gain), yellow icon: low performance loss, and red icon: high performance loss (model crash).</p>
Full article ">Figure 13
<p>HBV model performance loss trend over time and space ((<b>A</b>) KGE, (<b>B</b>) NSE, (<b>C</b>) R<sup>2</sup>).</p>
Full article ">Figure A1
<p>Variation of long-term trend of R<sup>2</sup> performance metric across study catchments between 2001 and 2019 (mean: blue line, median: red line, standard deviation: orange line, trend: black line).</p>
Full article ">Figure A2
<p>Variation of long-term trend of RVE performance metric across study catchments between 2001 and 2019 (mean: blue line, median: red line, standard deviation: orange line, trend: black line).</p>
Full article ">Figure A3
<p>RVE metric variation for different catchments across years.</p>
Full article ">
22 pages, 3440 KiB  
Article
An Ultra-Fast Green UHPLC-MS/MS Method for Assessing the In Vitro Metabolic Stability of Dovitinib: In Silico Study for Absorption, Distribution, Metabolism, Excretion, Metabolic Lability, and DEREK Alerts
by Mohamed W. Attwa, Ali S. Abdelhameed and Adnan A. Kadi
Medicina 2024, 60(10), 1626; https://doi.org/10.3390/medicina60101626 - 4 Oct 2024
Viewed by 805
Abstract
Background and Objectives: Dovitinib (DVB) is a pan-tyrosine kinase inhibitor (TKI) that can be administered orally. In September 2023, the FDA granted Oncoheroes approval to proceed with an Investigational New Drug (IND) application for dovitinib. This application is intended for the treatment [...] Read more.
Background and Objectives: Dovitinib (DVB) is a pan-tyrosine kinase inhibitor (TKI) that can be administered orally. In September 2023, the FDA granted Oncoheroes approval to proceed with an Investigational New Drug (IND) application for dovitinib. This application is intended for the treatment of relapsed or advanced juvenile solid tumors, namely, osteosarcoma. Materials and Methods: The target of the present study was to develop a rapid, green, accurate, and sensitive UHPLC-MS/MS method for measuring DVB levels in human liver microsomes (HLMs). The validations of the HLMs were performed via the established UHPLC-MS/MS approach, as stated in the US FDA reported guidelines for the standards of bioanalytical method validation protocol. The StarDrop in silico software package (version 6.6), which involves the DEREK and WhichP450 in silico modules, was used to check the DVB structure for hazardous alerts and metabolic instability. The DVB and encorafenib (EFB), internal standard, and chromatographic peaks were successfully separated using a reversed phase column (an Eclipse Plus Agilent C8 column) and an isocratic mobile phase. The production of DVB parent ions was accomplished by utilizing the positive ionization mode of an ESI source. The identification and measurement of DVB daughter ions were conducted using the MRM mode. Results: The inter-day accuracy and precision exhibited a spectrum of values in the range of −0.56% to 9.33%, while the intra-day accuracy and precision showcased a range of scores between 0.28% and 7.28%. The DVB calibration curve showed a linear relationship that ranged from 1 to 3000 ng/mL. The usefulness of the currently validated UHPLC-MS/MS method was approved by the lower limit of quantification (LLOQ) of 1 ng/mL. The AGREE findings demonstrate that the UHPLC-MS/MS method had a noteworthy degree of ecological greenness. The in vitro half-life (t1/2) and intrinsic clearance (Clint) of DVB were calculated to be 15.48 min and 52.39 mL/min/kg, respectively, which aligned with the findings from the WhichP450 software (version 6.6). Conclusions: Via the usage of in silico software, it has been observed that making small changes to the structure of the aryl piperazine ring and quinolinone moieties, or replacing these groups in the drug design process, shows potential for enhancing the metabolic safety and stability of newly developed derivatives compared to DVB. Full article
(This article belongs to the Section Pharmacology)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>CSL (0.9995) proving the increase in the metabolic lability of DVB. The results were assessed using the WhichP450 module.</p>
Full article ">Figure 2
<p>Structural alarms of DVB using DEREK in silico toxicity prediction tool of the StarDrop software (toxicity alerts marked in red color).</p>
Full article ">Figure 3
<p>The ADME radar chart of DVB generated from the freely available SwissADME online software.</p>
Full article ">Figure 4
<p>MRM (two mass transitions) mass spectrum of DVB [M + H]<sup>+</sup> (<b>A</b>) and Encorafenib [M + H]<sup>+</sup> (<b>B</b>) represented as two mass transitions. The proposed dissociation behaviors are elucidated.</p>
Full article ">Figure 5
<p>Negative control HLMs showed no interfering chromatographic peaks at the retention times of DVB and ENF (<b>A</b>). The total ion chromatogram (TIC) and MRM chromatogram of HLMs (negative control) with ENF at 2000 ng/mL (<b>B</b>). The overlaid MRM mass chromatograms of the 8 DVB CSs (<b>C</b>). The chromatograms reveal the peaks conforming to DVB (at 0.43 min) and IS at 2 µg/mL and at an elution time of 0.77 min.</p>
Full article ">Figure 6
<p>DVB LOQ peak at 1 ng/mL (<b>A</b>). Additionally, the EFB (IS) peak at 2000 ng/mL (<b>B</b>).</p>
Full article ">Figure 7
<p>The AGREE in silico software was utilized to assess the eco-friendly profile of the current UHPLC-MS/MS technique displayed in the shape of a circular diagram of 12 distinct traits.</p>
Full article ">Figure 8
<p>(<b>A</b>) DVB metabolic stability curve; (<b>B</b>) the natural logarithm (ln) curve (linear segment) exhibiting the linear regression equation.</p>
Full article ">Figure 9
<p>Dovitinib’s metabolic lability (blue color) using WhichP450 software. Dovitinib DEREK toxicity assessments (red color) revealing that the aryl piperazine ring and quinolinone moiety are accountable for the proposed toxicity and metabolic instability of DVB.</p>
Full article ">
24 pages, 4917 KiB  
Article
Calibration Method for Relativistic Navigation System Using Parallel Q-Learning Extended Kalman Filter
by Kai Xiong, Qin Zhao and Li Yuan
Sensors 2024, 24(19), 6186; https://doi.org/10.3390/s24196186 - 24 Sep 2024
Viewed by 461
Abstract
For the relativistic navigation system where the position and velocity of the spacecraft are determined through the observation of the relativistic perturbations including stellar aberration and starlight gravitational deflection, a novel parallel Q-learning extended Kalman filter (PQEKF) is presented to implement the measurement [...] Read more.
For the relativistic navigation system where the position and velocity of the spacecraft are determined through the observation of the relativistic perturbations including stellar aberration and starlight gravitational deflection, a novel parallel Q-learning extended Kalman filter (PQEKF) is presented to implement the measurement bias calibration. The relativistic perturbations are extracted from the inter-star angle measurement achieved with a group of high-accuracy star sensors on the spacecraft. Inter-star angle measurement bias caused by the misalignment of the star sensors is one of the main error sources in the relativistic navigation system. In order to suppress the unfavorable effect of measurement bias on navigation performance, the PQEKF is developed to estimate the position and velocity, together with the calibration parameters, where the Q-learning approach is adopted to fine tune the process noise covariance matrix of the filter automatically. The high performance of the presented method is illustrated via numerical simulations in the scenario of medium Earth orbit (MEO) satellite navigation. The simulation results show that, for the considered MEO satellite and the presented PQEKF algorithm, in the case that the inter-star angle measurement accuracy is about 1 mas, after calibration, the positioning accuracy of the relativistic navigation system is less than 300 m. Full article
(This article belongs to the Section Navigation and Positioning)
Show Figures

Figure 1

Figure 1
<p>Concept of relativistic navigation.</p>
Full article ">Figure 2
<p>Diagram of relativistic navigation and calibration method.</p>
Full article ">Figure 3
<p>Diagram of PQEKF algorithm.</p>
Full article ">Figure 4
<p>Position estimation error of traditional EKF without measurement bias calibration.</p>
Full article ">Figure 5
<p>Velocity estimation error of traditional EKF without measurement bias calibration.</p>
Full article ">Figure 6
<p>Position estimation error of calibration method based on PQEKF.</p>
Full article ">Figure 7
<p>Velocity estimation error of calibration method based on PQEKF.</p>
Full article ">Figure 8
<p>Position RMS errors of different methods vs. measurement bias.</p>
Full article ">Figure 9
<p>Velocity RMS errors of different methods vs. measurement bias.</p>
Full article ">Figure 10
<p>RMS errors as functions of measurement noise standard deviation.</p>
Full article ">Figure 11
<p>Position RMS error curves of different navigation filters.</p>
Full article ">Figure 12
<p>Position RMS error curves of PQEKF algorithms for different state numbers.</p>
Full article ">
14 pages, 7034 KiB  
Article
Macrophytes as Key Element to Determine Ecological Quality Changes in Transitional Water Systems: The Venice Lagoon as Study Case
by Adriano Sfriso, Alessandro Buosi, Yari Tomio, Giulia Silan, Marion Adelheid Wolf, Katia Sciuto and Andrea Augusto Sfriso
Environments 2024, 11(9), 209; https://doi.org/10.3390/environments11090209 - 22 Sep 2024
Viewed by 797
Abstract
According to European Union guidelines, the assessment of the ecological status of Transitional Water Systems (TWSs) should be based on the monitoring of biological communities rather than physico-chemical parameters and pollutants. Macrophytes, including aquatic angiosperms and macroalgae, are organisms that respond more quickly [...] Read more.
According to European Union guidelines, the assessment of the ecological status of Transitional Water Systems (TWSs) should be based on the monitoring of biological communities rather than physico-chemical parameters and pollutants. Macrophytes, including aquatic angiosperms and macroalgae, are organisms that respond more quickly to environmental changes by varying the structure and biomass of their assemblages. There are several ecological indices based on macrophytes, among them the Macrophyte Quality Index (MaQI), which has been intercalibrated with water and sediment parameters, nutrient concentrations, and pollutants and is used to determine the ecological status of Italian TWSs. In the Venice Lagoon, it was applied to 87 stations, showing a significant score increase over the last ten years of monitoring (2011–2021) due to progressive lagoon environmental recovery. The dominant taxa assemblages, previously dominated by Ulvaceae, were replaced by species of higher ecological value, with an increase in the number and distribution of sensitive species, as well as the spread and cover of aquatic angiosperms. The rise in the Ecological Quality Ratio (EQR) determined by the MaQI confirms the key role of macrophyte monitoring in detecting environmental changes in TWSs. In fact, a simple check of the presence or absence of aquatic angiosperms and sensitive species is sufficient for an initial rapid assessment of the ecological status of these environments. Full article
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Map of the Venice Lagoon.</p>
Full article ">Figure 2
<p>Macroalgal Quality Index (MaQI) scheme to assess the ecological status of transitional water systems (TWSs). As indicated by the Water Framework Directive (WFD 2000/60/EC) the Ecological Quality Ratio (EQR) values are highlighted in red (Bad conditions), ochre (Poor conditions), yellow (Moderate conditions), green (Good conditions) and light blue (High conditions).</p>
Full article ">Figure 3
<p>Ecological Quality Ratio (EQR) changes determined by the Macrophyte Quality Index (MaQI) in the water bodies (WBs) of the Venice Lagoon from 2011 to 2021. Legend: DV = Dogà Valley; CV = Cavallino Valley; ZV = Zappa Valley; ER = Euryhaline Restricted; ENR = Euryhaline Non-Restricted; PR = Polyhaline Restricted; PNR = Polyhaline Non-Restricted.</p>
Full article ">Figure 4
<p>Changes in (<b>A</b>) the mean number of total macroalgal taxa per station; (<b>B</b>) the mean number of sensitive macroalgal taxa per station; (<b>C</b>) the total number of stations colonized by aquatic angiosperms; (<b>D</b>) the mean percentage of aquatic angiosperm cover in the total stations during the 4 sampling years.</p>
Full article ">Figure 5
<p>(<b>A</b>) Number of colonized stations by each angiosperm species; (<b>B</b>) total mean cover of each angiosperm in the 87 stations between 2011 and 2021.</p>
Full article ">Figure 6
<p>(<b>A</b>) Mean values of Reactive Phosphorus (RP); (<b>B</b>) Dissolved Inorganic Nitrogen (DIN = sum of ammonium, nitrite, nitrate); (<b>C</b>) Total Chlorophyll-a (Chl-a); and (<b>D</b>) Total Suspended Solids (TSSs) in the 87 stations between 2011 and 2021.</p>
Full article ">
20 pages, 31687 KiB  
Article
Spatial and Temporal Variations of Total Suspended Matter Concentration during the Dry Season in Dongting Lake in the Past 35 Years
by Yifan Shao, Qian Shen, Yue Yao, Yuting Zhou, Wenting Xu, Wenxin Li, Hangyu Gao, Jiarui Shi and Yuting Zhang
Remote Sens. 2024, 16(18), 3509; https://doi.org/10.3390/rs16183509 - 21 Sep 2024
Viewed by 699
Abstract
Dongting Lake is the second largest freshwater lake in China, located in the middle reaches of the Yangtze River. Since the 21st century, it has faced intensified human activities, particularly the Three Gorges Dam impoundment and sand mining. The water quality of Dongting [...] Read more.
Dongting Lake is the second largest freshwater lake in China, located in the middle reaches of the Yangtze River. Since the 21st century, it has faced intensified human activities, particularly the Three Gorges Dam impoundment and sand mining. The water quality of Dongting Lake has significantly changed due to human activities and climate change. Currently, quantitative studies on the spatial–temporal variations of total suspended matter (TSM) during Dongting Lake’s dry season and the human impacts on its concentration are lacking. This study utilizes Landsat-5 TM and Landsat-8 OLI data to estimate the changes in TSM concentration during the dry season from 1986 to 2021, analyzing their spatial–temporal variations and driving mechanisms. By evaluating the atmospheric calibration accuracy and model precision metrics, we select a model based on the ratio of red to green band, achieving an R2 of 0.84, RMSE of 18.94 mg/L, and MRE of 27.32%. Applying this model to the images, we map the distribution of the TSM concentration during the dry season from 1986 to 2021, analyzing its spatial pattern and inter-annual variation, and further investigate the impacts of natural factors and human activities on the TSM concentration. Our results show the following: (1) From 1986 to 2021, the TSM concentration during the dry season ranges from 0 to 200 mg/L of Dongting Lake, with an area-wide average value between 41.61 and 75.44 mg/L. (2) The TSM concentration from 1986 to 2021 is significantly correlated with the water level. Before 2006, it correlates positively, but no significant correlation exists from 2006 onward. (3) From 2006 onward, the mean TSM concentration is notably decreased compared to that before 2006, likely due to the Three Gorges Dam, while our analysis indicates a significant positive correlation between the TSM concentration and sand mining intensity during this period. This study highlights the influence of the Three Gorges Dam and sand mining on the TSM concentration in Dongting Lake during the dry season, providing valuable insights for related research on similar lakes. Full article
Show Figures

Figure 1

Figure 1
<p>Location map of Dongting Lake.</p>
Full article ">Figure 2
<p>Distribution of sampling points in Dongting Lake. (<b>a</b>) 19 September 2022; (<b>b</b>) 15 April 2023.</p>
Full article ">Figure 3
<p>Evaluation of sand mining intensity: (<b>a</b>) true-color composite (Red-Green-Blue); (<b>b</b>) false-color composite (SWIR 1-NIR-Blue); (<b>c</b>) vessels identified from false-color images (suspected pixels marked in red).</p>
Full article ">Figure 4
<p>Spectra of Dongting Lake water on 19 September 2022: (<b>a</b>) measured spectra; (<b>b</b>) equivalent spectra.</p>
Full article ">Figure 5
<p>Evaluation of atmospheric calibration accuracy.</p>
Full article ">Figure 6
<p>Landsat inversion model and accuracy assessment for TSM concentration during the dry season in Dongting Lake: (<b>a</b>) linear regression fit for estimating the TSM concentration based on Landsat-8 OLI equivalent remote sensing reflectance (<math display="inline"><semantics> <msub> <mi>R</mi> <mi>rs</mi> </msub> </semantics></math>); (<b>b</b>) scatter plot of measured TSM concentration versus estimated TSM concentration based on equivalent <math display="inline"><semantics> <msub> <mi>R</mi> <mi>rs</mi> </msub> </semantics></math>.</p>
Full article ">Figure 7
<p>Comparison of measured TSM and estimated TSM based on imagery: (<b>a</b>) validation based on Landsat-8/9 OLI/OLI2 imagery; (<b>b</b>) validation based on synchronized Sentinel-2 MultiSpectral Instrument (MSI) imagery.</p>
Full article ">Figure 8
<p>Distribution of the TSM concentration during the dry season of Dongting Lake, 1986–2021.</p>
Full article ">Figure 9
<p>Inter-annual variation of TSM concentration during the dry season in Dongting Lake, 1986–2021.</p>
Full article ">Figure 10
<p>Consistency of the ratio of the red to green band based on Landsat-5 Thematic Mapper (TM) and Landsat-8 OLI.</p>
Full article ">Figure 11
<p>Comparison to analogous research: (<b>a</b>) applying Zheng et al.’s model [<a href="#B31-remotesensing-16-03509" class="html-bibr">31</a>] to equivalent <math display="inline"><semantics> <msub> <mi>R</mi> <mi>rs</mi> </msub> </semantics></math> using in situ spectra; (<b>b</b>) applying Zheng et al.’s model [<a href="#B31-remotesensing-16-03509" class="html-bibr">31</a>] to Landsat-8 OLI image; (<b>c</b>) applying Wu et al.’s model [<a href="#B30-remotesensing-16-03509" class="html-bibr">30</a>] to equivalent <math display="inline"><semantics> <msub> <mi>R</mi> <mi>rs</mi> </msub> </semantics></math> using in situ spectra; (<b>d</b>) applying Wu et al.’s model [<a href="#B30-remotesensing-16-03509" class="html-bibr">30</a>] to Landsat-8 OLI image.</p>
Full article ">Figure 11 Cont.
<p>Comparison to analogous research: (<b>a</b>) applying Zheng et al.’s model [<a href="#B31-remotesensing-16-03509" class="html-bibr">31</a>] to equivalent <math display="inline"><semantics> <msub> <mi>R</mi> <mi>rs</mi> </msub> </semantics></math> using in situ spectra; (<b>b</b>) applying Zheng et al.’s model [<a href="#B31-remotesensing-16-03509" class="html-bibr">31</a>] to Landsat-8 OLI image; (<b>c</b>) applying Wu et al.’s model [<a href="#B30-remotesensing-16-03509" class="html-bibr">30</a>] to equivalent <math display="inline"><semantics> <msub> <mi>R</mi> <mi>rs</mi> </msub> </semantics></math> using in situ spectra; (<b>d</b>) applying Wu et al.’s model [<a href="#B30-remotesensing-16-03509" class="html-bibr">30</a>] to Landsat-8 OLI image.</p>
Full article ">Figure 12
<p>Influence of natural factors on the TSM concentration in Dongting Lake during the dry season (the black line shows the linear regression of the TSM concentration with natural factors).</p>
Full article ">Figure 13
<p>Influence of the water level during different periods on the TSM concentration in Dongting Lake during the dry season (the orange line shows the linear regression of the TSM concentration with the water level between 1986 and 2005).</p>
Full article ">Figure 14
<p>Relationship between the TSM concentration and sand mining intensity during the dry season of Dongting Lake, 2006–2021: (<b>a</b>) variation in the TSM concentration and sand mining intensity; (<b>b</b>) correlation between the TSM concentration and sand mining intensity (the black line shows the linear regression of the TSM concentration with sand mining intensity).</p>
Full article ">
18 pages, 3651 KiB  
Article
Reference Materials for Thermal Conductivity Measurements: European Situation
by Alain Koenen, Damien Marquis and Susanne Dehn
Buildings 2024, 14(9), 2795; https://doi.org/10.3390/buildings14092795 - 5 Sep 2024
Viewed by 784
Abstract
A reference material (RM), as defined by the International Vocabulary of Metrology (VIM 2012), must be homogeneous, stable, and suitable for use in measurements. Certified reference materials (CRMs) are RMs with documented property values, uncertainties, and traceability. ISO 17034:2018 outlines the requirements for [...] Read more.
A reference material (RM), as defined by the International Vocabulary of Metrology (VIM 2012), must be homogeneous, stable, and suitable for use in measurements. Certified reference materials (CRMs) are RMs with documented property values, uncertainties, and traceability. ISO 17034:2018 outlines the requirements for RM producers, ensuring that CRMs meet standards for stability, uniformity, and reproducibility. In Europe, CE marking, from French “conformité Européenne”, which means European conformity, has been mandatory for thermal insulation products since 2002, ensuring their thermal performance is verified by accredited laboratories using RMs like IRMM440 and ERM FC440. Annually, European manufacturers produce over 200 million cubic meters of thermal insulation, necessitating thousands of thermal conductivity measurements daily to maintain CE marking compliance. Key characteristics of Reference Materials include long-term stability, thermal conductivity within specified ranges, and minimal dependence on density, thickness, and applied load. Sample thickness must conform to apparatus specifications, and homogeneity must be quantified. Reference Materials must also have appropriate dimensions, surface smoothness, and manufacturability. The Joint Research Centre (JRC) Geel has produced two Reference Materials, IRMM 440 and ERM FC 440, with specific characteristics to meet these requirements. Both are glass wool fibers with low thermal conductivity and specific density and thickness. The qualification of RMs involves inter-laboratory comparisons to ensure the accuracy and traceability of thermal conductivity measurements. The European market’s organization, including the use of Reference Materials and CE marking, has significantly improved measurement consistency and product quality. This system has led to lower uncertainties in thermal conductivity measurements compared to North America, highlighting the impact of standardized RMs on industry practices. Future needs include developing RMs with lower conductivity and increased thickness to accommodate market trends towards super insulation materials and bio-based components, enhancing energy performance calculations for buildings. This paper will present the process of defining a reference material and how it affects the uncertainty level of the calculation of building energy performance. This level depends on the characteristics of the materials used, their implementation, and external factors, such as the weather, as well as the reference material used for calibration of all European thermal conductivity measurement devices. Full article
(This article belongs to the Section Building Energy, Physics, Environment, and Systems)
Show Figures

Figure 1

Figure 1
<p>Thermal resistance, <span class="html-italic">R</span>, as a function of specimen thickness, <span class="html-italic">d</span>.</p>
Full article ">Figure 2
<p>Thermal resistance of white EPS with a density of 21.2 kg/m<sup>3</sup> as a function of the specimen thickness.</p>
Full article ">Figure 3
<p>Thermal resistance of white EPS with a density of 32.8 kg/m<sup>3</sup> as a function of the specimen thickness.</p>
Full article ">Figure 4
<p>Thermal resistance of a stone wool with a density of 44.1 kg/m<sup>3</sup> as a function of the specimen thickness.</p>
Full article ">Figure 5
<p>Variation of thermal conductivity with the density.</p>
Full article ">Figure 6
<p>Effect of moisture on thermal conductivity (wood fiber between 60 and 190 kg/m<sup>3</sup>).</p>
Full article ">Figure 7
<p>Moisture content in wood fiber product in mass percent (wood fiber between 60 and 190 kg/m<sup>3</sup>).</p>
Full article ">Figure 8
<p>Variation of thermal conductivity with temperature of IRMM 440 and ERM FC 440.</p>
Full article ">Figure 9
<p>Stability data on IRMM-440 over 12 years from [<a href="#B24-buildings-14-02795" class="html-bibr">24</a>].</p>
Full article ">Figure 10
<p>Stability data for IRMM-440 from [<a href="#B24-buildings-14-02795" class="html-bibr">24</a>].</p>
Full article ">Figure 11
<p>Thermal conductivity dispersion comparison between North America and Europe.</p>
Full article ">
19 pages, 2672 KiB  
Article
Simultaneous Determination of Tobacco Smoke Exposure and Stress Biomarkers in Saliva Using In-Tube SPME and LC-MS/MS for the Analysis of the Association between Passive Smoking and Stress
by Hiroyuki Kataoka, Saori Miyata and Kentaro Ehara
Molecules 2024, 29(17), 4157; https://doi.org/10.3390/molecules29174157 - 2 Sep 2024
Viewed by 989
Abstract
Passive smoking from environmental tobacco smoke not only increases the risk of lung cancer and cardiovascular disease but may also be a stressor triggering neuropsychiatric and other disorders. To prevent these diseases, understanding the relationship between passive smoking and stress is vital. In [...] Read more.
Passive smoking from environmental tobacco smoke not only increases the risk of lung cancer and cardiovascular disease but may also be a stressor triggering neuropsychiatric and other disorders. To prevent these diseases, understanding the relationship between passive smoking and stress is vital. In this study, we developed a simple and sensitive method to simultaneously measure nicotine (Nic) and cotinine (Cot) as tobacco smoke exposure biomarkers, and cortisol (CRT), serotonin (5-HT), melatonin (MEL), dopamine (DA), and oxytocin (OXT) as stress-related biomarkers. These were extracted and concentrated from saliva by in-tube solid-phase microextraction (IT-SPME) using a Supel-Q PLOT capillary as the extraction device, then separated and detected within 6 min by liquid chromatography–tandem mass spectrometry (LC−MS/MS) using a Kinetex Biphenyl column (Phenomenex Inc., Torrance, CA, USA). Limits of detection (S/N = 3) for Nic, Cot, CRT, 5-HT, MEL, DA, and OXT were 0.22, 0.12, 0.78, 0.39, 0.45, 1.4, and 3.7 pg mL−1, respectively, with linearity of calibration curves in the range of 0.01–25 ng mL−1 using stable isotope-labeled internal standards. Intra- and inter-day reproducibilities were under 7.9% and 14.6% (n = 5) relative standard deviations, and compound recoveries in spiked saliva samples ranged from 82.1 to 106.6%. In thirty nonsmokers, Nic contents positively correlated with CRT contents (R2 = 0.5264, n = 30), while no significant correlation was found with other biomarkers. The standard deviation of intervals between normal beats as the standard measure of heart rate variability analysis negatively correlated with CRT contents (R2 = 0.5041, n = 30). After passive smoke exposure, Nic levels transiently increased, Cot and CRT levels rose over time, and 5-HT, DA, and OXT levels decreased. These results indicate tobacco smoke exposure acts as a stressor in nonsmokers. Full article
(This article belongs to the Special Issue Applications of Solid-Phase Microextraction and Related Techniques)
Show Figures

Figure 1

Figure 1
<p>On-line IT-SPME LC–MS/MS system.</p>
Full article ">Figure 2
<p>Effects of capillary coatings on IT-SPME of seven biomarkers. Extraction was performed by 25 draw/eject cycles of 40 μL of standard solution.</p>
Full article ">Figure 3
<p>Effects of draw/eject cycles on IT-SPME of seven biomarkers. Extraction was performed with Supel-Q PLOT capillary by draw/eject cycles of 40 μL of standard solution.</p>
Full article ">Figure 4
<p>MRM chromatograms obtained from (<b>A</b>) a standard solution containing 5.0 ng mL<sup>−1</sup> Nic, 1.0 ng mL<sup>−1</sup> Cot, 0.20 ng mL<sup>−1</sup> CRT, 2.0 ng mL<sup>−1</sup> 5-HT, 1.0 ng mL<sup>−1</sup> MEL, 20 ng mL<sup>−1</sup> DA, 50 ng mL<sup>−1</sup> OXT, and their stable isotope-labeled internal standard (IS) compounds and (<b>B</b>) 0.05 mL of saliva sample. IT-SPME LC-MS/MS conditions are described in the Materials and Methods section.</p>
Full article ">Figure 5
<p>Correlation between salivary biomarker concentrations and HRV indicators in 30 nonsmokers. (<b>A</b>) Nic concentration vs. Cot concentration, (<b>B</b>) Nic concentration vs. CRT concentration, (<b>C</b>) SDNN vs. CRT concentration, (<b>D</b>) SDNN vs. Ln TP.</p>
Full article ">Figure 6
<p>Variation in salivary biomarker concentrations and HRV indicators before and after tobacco smoke exposure in nonsmoker. (<b>A</b>) Tobacco smoke exposure biomarkers, (<b>B</b>) Stress and relaxation biomarkers and (<b>C</b>) HRV indicators.</p>
Full article ">Figure 7
<p>Structures of target biomarkers and their stable isotope-labeled internal standards.</p>
Full article ">
14 pages, 3400 KiB  
Article
Design of Selective Nanoparticles of Layered Double Hydroxide (Mg/Al-LDH) for the Analysis of Anti-Inflammatory Non-Steroidal Agents in Environmental Samples, Coupled with Solid-Phase Extraction and Capillary Electrophoresis
by David Aurelio-Soria, Xochitl H. Canales, Isai Vázquez-Garrido, Gabriela Islas, Giaan A. Álvarez-Romero and Israel S. Ibarra
Separations 2024, 11(9), 259; https://doi.org/10.3390/separations11090259 - 1 Sep 2024
Viewed by 625
Abstract
A simple, fast, and low-cost pre-concentration methodology based on the application of solid-phase extraction coupled to layered double hydroxides (LDHs) and capillary electrophoresis was developed for the determination of naproxen (NPX), diclofenac (DFC), and ibuprofen (IBP) in environmental sample waters. A systematic study [...] Read more.
A simple, fast, and low-cost pre-concentration methodology based on the application of solid-phase extraction coupled to layered double hydroxides (LDHs) and capillary electrophoresis was developed for the determination of naproxen (NPX), diclofenac (DFC), and ibuprofen (IBP) in environmental sample waters. A systematic study of the LDH composition was designed, including the effects of interlayer anions (NO3, Cl, CO32−, BenO, and SDS) and the effect of molar ratio (Mg:Al). The optimal composition of MgAl/Cl-LDH (Mg:Al; 1.5:1.0) was coupled to an SPE system: pH (neutral pH), LDH amount (15 mg), and extraction capacity ranged from 79.71 to 83.11% for the three anti-inflammatory non-steroidal agents analyzed. A recovery rate of up to 80.87% was obtained when 0.01 M chloride acid in methanol was used as the eluent and 50 mL of sample was used. Under optimal conditions, the linear range of the calibration curve ranges from 18.02 to 200 μg L−1, with limits of detection ranging from 6.03 to 18.02 μg L−1 for the three NSAIDs. The precision of the methodology was evaluated in terms of inter- and intra-day repeatability, with %RSD < 10% in all cases. The proposed method was applied to analyze environmental water samples (bottle, tap, cistern, well, and river water samples). The developed method is a robust technique capable of combining with other analytical methods to quantitatively determine anti-inflammatory non-steroidal agents. Full article
(This article belongs to the Special Issue Development of Materials for Separation and Analysis Applications)
Show Figures

Figure 1

Figure 1
<p>(<b>a</b>) FTIR spectra of the MgAl/Cl<sup>−</sup>-LDH and (<b>b</b>) TGA curve MgAl/Cl<sup>−</sup>-LDH.</p>
Full article ">Figure 2
<p>(<b>a</b>) Scanning electron microscope image and (<b>b</b>) particle size distribution of the MgAl/Cl<sup>−</sup>-LDH.</p>
Full article ">Figure 3
<p>Effect of the LDH composition on the NSAID extraction performance. (<b>a</b>) Anion interlayer effect and (<b>b</b>) molar ratio M<sup>2+</sup>:M<sup>3+</sup> effect.</p>
Full article ">Figure 4
<p>Univariate optimization of the SPE process. (<b>a</b>) pH effect, (<b>b</b>) LDH amount effect, (<b>c</b>) concentration effect (salting-out effect) and (<b>d</b>) elution.</p>
Full article ">Figure 5
<p>Electropherograms obtained in the analysis of NSAIDs and interferents. (<b>a</b>) Solution standard containing NSAIDs, IS, ASP, PHEN and SAC [10 mg L<sup>−1</sup>] and (<b>b</b>) solution standard containing NSAIDs, IS, ASP, PHEN and SAC [10 mg L<sup>−1</sup>] and treated by the optimal conditions of the SPE methodology.</p>
Full article ">Figure 6
<p>Electropherograms obtained in the analysis of real water samples. (<b>a</b>) Cistern water sample spiked with internal standard (0.5 mg L<sup>−1</sup>) and analyzed by the SPE-CE-UV. (<b>b</b>) NPX-positive cistern water sample, with internal standard (0.5 mg L<sup>−1</sup>) and analyzed by SPE-CE-UV. (<b>c</b>) Positive sample spiked with NPX 100 µg L<sup>−1</sup> with internal standard (0.5 mg L<sup>−1</sup>) analyzed by SPE-CE-UV.</p>
Full article ">
Back to TopTop