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Search Results (143)

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15 pages, 1137 KiB  
Article
Breeding Season Habitat Selection of the Eurasian Collared Dove in a Dry Mediterranean Landscape
by Alan Omar Bermúdez-Cavero, Edgar Bernat-Ponce, José Antonio Gil-Delgado and Germán Manuel López-Iborra
Birds 2024, 5(4), 737-751; https://doi.org/10.3390/birds5040050 - 24 Nov 2024
Viewed by 399
Abstract
Birds select habitats to optimize resources and maximize fitness, with some species recently colonizing new areas, like the Eurasian collared dove (ECD) in the Iberian Peninsula. The ECD spread across Europe in the early 20th century from South Asia. This study reanalyzes data [...] Read more.
Birds select habitats to optimize resources and maximize fitness, with some species recently colonizing new areas, like the Eurasian collared dove (ECD) in the Iberian Peninsula. The ECD spread across Europe in the early 20th century from South Asia. This study reanalyzes data from the Atlas of Breeding Birds in the Province of Alicante (SE Spain) to identify macrohabitat-level environmental variables related to its occurrence and abundance in this semi-arid Mediterranean landscape during the breeding season. We performed Hierarchical Partitioning analyses to identify important environmental variables for the species associated with natural vegetation, farming, topography, hydrographical web, urbanization, and climate. Results show that ECD has a higher occurrence probability near anthropic areas (isolated buildings, suburban areas), water points (medium-sized ponds), larger crop surfaces (total cultivated area), and warmer localities (thermicity index). The species avoids natural habitats like pine forests and scrublands. Abundance is positively linked to anthropic features like larger suburban areas and urban-related land uses. These findings can help predict its expansion in regions with a Mediterranean climate in South America, North America, or Australia, and its continuous natural expansion and population increase within the Mediterranean basin and Europe. Full article
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Figure 1
<p>Map of Alicante province and its location in SE Spain. The 10 × 10-km UTM grid is shown (thin line) along with the 2 × 2 squares that were randomly selected for the fieldwork of the <span class="html-italic">Atlas of Breeding Birds in the Province of Alicante</span> [<a href="#B34-birds-05-00050" class="html-bibr">34</a>,<a href="#B35-birds-05-00050" class="html-bibr">35</a>].</p>
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<p>Relationships of the most relevant environmental variables, according to the HP analyses, showing a positive relationship for the presence (blue line: (<b>A</b>–<b>E</b>)) and abundance (red line: (<b>F</b>,<b>G</b>)) of the Eurasian collared dove in SE Spain.</p>
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20 pages, 11797 KiB  
Article
Relative Radiometric Normalization for the PlanetScope Nanosatellite Constellation Based on Sentinel-2 Images
by Rafael Luís Silva Dias, Ricardo Santos Silva Amorim, Demetrius David da Silva, Elpídio Inácio Fernandes-Filho, Gustavo Vieira Veloso and Ronam Henrique Fonseca Macedo
Remote Sens. 2024, 16(21), 4047; https://doi.org/10.3390/rs16214047 - 30 Oct 2024
Viewed by 1068
Abstract
Detecting and characterizing continuous changes on Earth’s surface has become critical for planning and development. Since 2016, Planet Labs has launched hundreds of nanosatellites, known as Doves. Despite the advantages of their high spatial and temporal resolution, these nanosatellites’ images still present inconsistencies [...] Read more.
Detecting and characterizing continuous changes on Earth’s surface has become critical for planning and development. Since 2016, Planet Labs has launched hundreds of nanosatellites, known as Doves. Despite the advantages of their high spatial and temporal resolution, these nanosatellites’ images still present inconsistencies in radiometric resolution, limiting their broader usability. To address this issue, a model for radiometric normalization of PlanetScope (PS) images was developed using Multispectral Instrument/Sentinel-2 (MSI/S2) sensor images as a reference. An extensive database was compiled, including images from all available versions of the PS sensor (e.g., PS2, PSB.SD, and PS2.SD) from 2017 to 2022, along with data from various weather stations. The sampling process was carried out for each band using two methods: Conditioned Latin Hypercube Sampling (cLHS) and statistical visualization. Five machine learning algorithms were then applied, incorporating both linear and nonlinear models based on rules and decision trees: Multiple Linear Regression (MLR), Model Averaged Neural Network (avNNet), Random Forest (RF), k-Nearest Neighbors (KKNN), and Support Vector Machine with Radial Basis Function (SVM-RBF). A rigorous covariate selection process was performed for model application, and the models’ performance was evaluated using the following statistical indices: Root Mean Squared Error (RMSE), Mean Absolute Error (MAE), Lin’s Concordance Correlation Coefficient (CCC), and Coefficient of Determination (R2). Additionally, Kruskal–Wallis and Dunn tests were applied during model selection to identify the best-performing model. The results indicated that the RF model provided the best fit across all PS sensor bands, with more accurate results in the longer wavelength bands (Band 3 and Band 4). The models achieved RMSE reflectance values of approximately 0.02 and 0.03 in these bands, with R2 and CCC ranging from 0.77 to 0.90 and 0.87 to 0.94, respectively. In summary, this study makes a significant contribution to optimizing the use of PS sensor images for various applications by offering a detailed and robust approach to radiometric normalization. These findings have important implications for the efficient monitoring of surface changes on Earth, potentially enhancing the practical and scientific use of these datasets. Full article
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Figure 1
<p>Location of the study area.</p>
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<p>Schematic flowchart of the steps for the radiometric normalization of the PS constellation.</p>
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<p>Spatial distribution of samples in the study quadrant, where orange points represent locations identified by the cLHS method, and green points represent those obtained through statistical evaluation of band-to-band pseudo-invariant pixels.</p>
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<p>Importance of covariates in normalizing the PlanetScope sensor using the MSI sensor, based on Multiple Linear Regression (MLR), Model Averaged Neural Network (avNNet), Random Forest (RF), k-Nearest Neighbors (KKNN), and Support Vector Machines with Radial Basis Function Kernel (SVM-RBF), applied to bands B1, B2, B3, and B4.</p>
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<p>Comparison of predicted and observed reflectance values for Bands 1, 2, 3, and 4 using RF, avNNet, KKNN, MLR, and SVM-RBF machine learning models. In black the 1:1 line and in gold the trend line.</p>
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<p>Violin plot showing the results of the Kruskal–Wallis and Dunn’s tests applied to the statistical indices CCC and R<sup>2</sup> for the machine learning models studied.</p>
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<p>Dispersion plot showing predicted versus observed data, along with the statistical indices used to evaluate the normalized bands of the PS sensor for various spectral indices.</p>
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25 pages, 10179 KiB  
Article
An Improved Physics-Based Dual-Band Model for Satellite-Derived Bathymetry Using SuperDove Imagery
by Chunlong He, Qigang Jiang and Peng Wang
Remote Sens. 2024, 16(20), 3801; https://doi.org/10.3390/rs16203801 - 12 Oct 2024
Viewed by 670
Abstract
Shallow water bathymetry is critical for environmental monitoring and maritime security. Current widely used statistical models based on passive optical satellite remote sensing often rely on prior bathymetric data, limiting their application to regions lacking such information. In contrast, the physics-based dual-band log-linear [...] Read more.
Shallow water bathymetry is critical for environmental monitoring and maritime security. Current widely used statistical models based on passive optical satellite remote sensing often rely on prior bathymetric data, limiting their application to regions lacking such information. In contrast, the physics-based dual-band log-linear analytical model (P-DLA) can estimate shallow water bathymetry without in situ measurements, offering significant potential. However, the quasi-analytical algorithm (QAA) used in the P-DLA is sensitive to non-ideal pixels, resulting in unstable bathymetry estimation. To address this issue and evaluate the potential of SuperDove imagery for bathymetry estimation in regions without prior bathymetric data, this study proposes an improved physics-based dual-band model (IPDB). The IPDB replaces the QAA with a spectral optimization algorithm that integrates deep and shallow water sample pixels to estimate diffuse attenuation coefficients for the blue and green bands. This allows for more accurate estimation of shallow water bathymetry. The IPDB was tested on SuperDove images of Dongdao Island, Yongxing Island, and Yongle Atoll. The results showed that SuperDove images are capable of estimating shallow water bathymetry in regions without prior bathymetric data. The IPDB achieved Root Mean Square Error (RMSE) values below 1.7 m and R2 values above 0.89 in all three study areas, indicating strong performance in bathymetric estimation. Notably, the IPDB outperformed the standard P-DLA model in accuracy. Furthermore, this study outlines four sampling principles that, when followed, ensure that variations in the spatial distribution of sampling pixels do not significantly impact model performance. This study also showed that the blue–green band combination is optimal for the analytical expression of the physics-based dual-band model. Full article
(This article belongs to the Special Issue Advances in Remote Sensing of the Inland and Coastal Water Zones II)
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<p>Geographic distribution of the study area.</p>
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<p>Spatial distribution of measured bathymetric data. (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll. The yellow text in the figures indicates the collection dates of the nearest bathymetric lines.</p>
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<p>Technical workflow for satellite-derived bathymetry.</p>
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<p>Distribution of sample pixels: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
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<p>Estimated <math display="inline"><semantics> <mrow> <mrow> <mrow> <msub> <mrow> <mi>g</mi> </mrow> <mrow> <mn>1</mn> </mrow> </msub> </mrow> <mo>/</mo> <mrow> <msub> <mrow> <mi>g</mi> </mrow> <mrow> <mn>2</mn> </mrow> </msub> </mrow> </mrow> </mrow> </semantics></math> ratios from the <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>1</mn> </mrow> </msub> </mrow> </semantics></math>~<math display="inline"><semantics> <mrow> <msub> <mrow> <mi>X</mi> </mrow> <mrow> <mn>2</mn> </mrow> </msub> </mrow> </semantics></math> datasets for the same substrate type but different depths: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
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<p>Bathymetry maps derived from the IPDB model: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
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<p>Scatter plots comparing estimated and measured water depths using the IPDB model: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
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<p>Distribution of different pixels pairs: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
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<p>Distribution of different waterlines: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
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<p>Distribution of different deep water regions: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
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22 pages, 29196 KiB  
Article
MPG-Net: A Semantic Segmentation Model for Extracting Aquaculture Ponds in Coastal Areas from Sentinel-2 MSI and Planet SuperDove Images
by Yuyang Chen, Li Zhang, Bowei Chen, Jian Zuo and Yingwen Hu
Remote Sens. 2024, 16(20), 3760; https://doi.org/10.3390/rs16203760 - 10 Oct 2024
Viewed by 811
Abstract
Achieving precise and swift monitoring of aquaculture ponds in coastal regions is essential for the scientific planning of spatial layouts in aquaculture zones and the advancement of ecological sustainability in coastal areas. However, because the distribution of many land types in coastal areas [...] Read more.
Achieving precise and swift monitoring of aquaculture ponds in coastal regions is essential for the scientific planning of spatial layouts in aquaculture zones and the advancement of ecological sustainability in coastal areas. However, because the distribution of many land types in coastal areas and the complex spectral features of remote sensing images are prone to the phenomenon of ‘same spectrum heterogeneous objects’, the current deep learning model is susceptible to background noise interference in the face of complex backgrounds, resulting in poor model generalization ability. Moreover, with the image features of aquaculture ponds of different scales, the model has limited multi-scale feature extraction ability, making it difficult to extract effective edge features. To address these issues, this work suggests a novel semantic segmentation model for aquaculture ponds called MPG-Net, which is based on an enhanced version of the U-Net model and primarily comprises two structures: MS and PGC. The MS structure integrates the Inception module and the Dilated residual module in order to enhance the model’s ability to extract the features of aquaculture ponds and effectively solve the problem of gradient disappearance in the training of the model; the PGC structure integrates the Global Context module and the Polarized Self-Attention in order to enhance the model’s ability to understand the contextual semantic information and reduce the interference of redundant information. Using Sentinel-2 and Planet images as data sources, the effectiveness of the refined method is confirmed through ablation experiments conducted on the two structures. The experimental comparison using the FCN8S, SegNet, U-Net, and DeepLabV3 classical semantic segmentation models shows that the MPG-Net model outperforms the other four models in all four precision evaluation indicators; the average values of precision, recall, IoU, and F1-Score of the two image datasets with different resolutions are 94.95%, 92.95%, 88.57%, and 93.94%, respectively. These values prove that the MPG-Net model has better robustness and generalization ability, which can reduce the interference of irrelevant information, effectively improve the extraction precision of individual aquaculture ponds, and significantly reduce the edge adhesion of aquaculture ponds in the extraction results, thereby offering new technical support for the automatic extraction of aquaculture ponds in coastal areas. Full article
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Figure 1
<p>Map of the study area. In the figure, the top half is the location of the study area, and the bottom half is a standard false-color map of Planet (<b>a</b>) and Sentinel-2 (<b>b</b>). (A,C) are the aquaculture areas of Yingluo Harbor, and (B,D) are the aquaculture areas of Anpu Harbor.</p>
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<p>The construction of U-Net.</p>
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<p>The structure of MPG-Net. MS and PGC are the two improved structures proposed in this study.</p>
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<p>The MS structure. Inception module on the left. Dilated residual module with Dilation rate equal to 5 on the right.</p>
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<p>The PGC structure. The upper branch is the bottleneck module and GC module, and the lower branch is the PSA module.</p>
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<p>The construction process of the aquaculture pond extraction model. The top, middle, and bottom sections of the figure represent data cropping, data enhancement, and model training and prediction, respectively.</p>
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<p>Results of testing set segmentation of aquaculture ponds on Sentinel-2 dataset with different models.</p>
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<p>Results of testing set segmentation of aquaculture ponds on Planet dataset with different models.</p>
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<p>Results of ablation experiments on Sentinel-2 testing set.</p>
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<p>Results of ablation experiments on the Planet testing set.</p>
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<p>The extraction results of Yingluo Harbor. Frames (<b>a</b>,<b>b</b>) original images, (<b>c,d</b>) extraction results, and (<b>e</b>,<b>f</b>) accuracy maps.</p>
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<p>The extraction results of Anpu Harbor. Frames (<b>a</b>,<b>b</b>) original images, (<b>c</b>,<b>d</b>) extraction results, and (<b>e</b>,<b>f</b>) accuracy maps.</p>
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20 pages, 11481 KiB  
Article
Where Are We Going Now? The Current and Future Distributions of the Monk Parakeet (Myiopsitta monachus) and Eurasian Collared Dove (Streptopelia decaocto) in a Megalopolis
by Jorge E. Ramírez-Albores, Luis A. Sánchez-González, David A. Prieto-Torres and Adolfo G. Navarro-Sigüenza
Sustainability 2024, 16(16), 7071; https://doi.org/10.3390/su16167071 - 17 Aug 2024
Viewed by 1825
Abstract
The monk parakeet (Myiopsitta monachus) and the Eurasian collared dove (Streptopelia decaocto) are two of the most prevalent invasive species globally due to their high dispersal ability. Since these birds were first recorded (1999 for the monk parakeet and [...] Read more.
The monk parakeet (Myiopsitta monachus) and the Eurasian collared dove (Streptopelia decaocto) are two of the most prevalent invasive species globally due to their high dispersal ability. Since these birds were first recorded (1999 for the monk parakeet and 2013 for Eurasian collared dove) in the Mexico City Metropolitan Area (MCMA), both species have spread rapidly throughout the area. However, the impacts of global climate changes on the distribution patterns of these species remain poorly studied across the MCMA. Therefore, based on an ecological niche modeling approach, we assessed the expansion and potential invasion of both species in this megalopolis using current and future climate projections (year 2050). Our results estimated that the current suitable areas are 5564 km2 for the monk parakeet and 5489 km2 for the Eurasian collared dove, covering ~70% of the study area, suggesting a rapidly invading species, as expected. We observed a slight decrease (up to 24%) in both species in future climate scenarios, but our models estimated that the sizes of the suitable areas would remain stable. We found that the range expansion of these species in the megalopolis may be largely attributed to their propensity for jump dispersion and short-time niche expansion ability. Our findings allow for a better understanding of the factors contributing to the range expansion of the monk parakeet and the Eurasian collared dove in Mexico and can better inform the monitoring guidelines for and assessments of these invasive species. Full article
(This article belongs to the Section Sustainability, Biodiversity and Conservation)
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Graphical abstract

Graphical abstract
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<p>Geographical distribution of occurrence records for <span class="html-italic">Myiopsitta monachus</span> (<b>A</b>) and <span class="html-italic">Streptopelia decaocto</span> (<b>B</b>) across Mexico City Metropolitan Area and adjacent areas. First (<span style="color:#0066FF">▲</span>) and subsequent occurrence records (<span style="color:red">●</span>) were obtained from different databases and personal field surveys (see Materials and Methods <a href="#sec2dot2-sustainability-16-07071" class="html-sec">Section 2.2</a>).</p>
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<p>Potential distribution areas of <span class="html-italic">Myiopsitta monachus</span> [current (<b>A</b>) and future climate change scenarios in 2050: (<b>B</b>) SSP 126, (<b>C</b>) SSP 370, and (<b>D</b>) SSP 585 for IPSL-CM6A-LR, and (<b>E</b>) SSP 126, (<b>F</b>) SSP 370, and (<b>G</b>) SSP 585 for GFDL-ESM4] and <span class="html-italic">Streptopelia decaocto</span> [current (<b>H</b>) and future climate change scenarios in 2050: (<b>I</b>) SSP 126, (<b>J</b>) SSP 370, and (<b>K</b>) SSP 585 for IPSL-CM6A-LR, and (<b>L</b>) SSP 126, (<b>M</b>) SSP 370, and (<b>N</b>) SSP 585 for GFDL-ESM4] were estimated based on ensemble climate models.</p>
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<p>Analysis of multivariate environmental similarity surface (MESS) of <span class="html-italic">Myiopsitta monachus</span> [current (<b>A</b>) and future climate change scenario in 2050: (<b>B</b>) SSP 126, (<b>C</b>) SSP 370, and (<b>D</b>) SSP 585 for GFDL-ESM4 and IPSL-CM6A-LR, and (<b>E</b>) SSP 126, (<b>F</b>) SSP 370, and (<b>G</b>) SSP 585 for IPSL-CM6A-LR] and <span class="html-italic">Streptopelia decaocto</span> [current (<b>H</b>) and future climate change scenario in 2050: (<b>I</b>) SSP 126, (<b>J</b>) SSP 370, and (<b>K</b>) SSP 585 for IPSL-CM6A-LR, and (<b>L</b>) SSP 126, (<b>M</b>) SSP 370, and (<b>N</b>) SSP 585 for GFDL-ESM4] within the MCMA under climate change scenarios. Red areas show one or more environmental variables outside the range present in the training data, so predictions in those areas should be treated with strong caution, while blue areas are more similar.</p>
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<p>Suitable habitat areas of <span class="html-italic">Myiopsitta monachus</span> [current (<b>A</b>) and future climate change scenario in 2050: (<b>B</b>) SSP 126, (<b>C</b>) SSP 370, and (<b>D</b>) SSP 585 for IPSL-CM6A-LR, and (<b>E</b>) SSP 126, (<b>F</b>) SSP 370, and (<b>G</b>) SSP 585 for GFDL-ESM4] and <span class="html-italic">Streptopelia decaocto</span> [current (<b>H</b>) and future climate change scenario in 2050: (<b>I</b>) SSP 126, (<b>J</b>) SSP 370, and (<b>K</b>) SSP 585 for IPSL-CM6A-LR, and (<b>L</b>) SSP 126, (<b>M</b>) SSP 370, and (<b>N</b>) SSP 585 for GFDL-ESM4] in agricultural lands within the MCMA under climate change scenarios. Green areas show the suitable habitat of the invasive alien species (considering a threshold &gt; 0.3); gray areas indicate the unsuitable habitat of the invasive alien species (considering a threshold &lt; 0.3); and blue lines show the agricultural areas in the MCMA.</p>
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<p>Suitable habitat areas of <span class="html-italic">Myiopsitta monachus</span> [current (<b>A</b>) and future climate change scenario in 2050: (<b>B</b>) SSP 126, (<b>C</b>) SSP 370, and (<b>D</b>) SSP 585 for IPSL-CM6A-LR, and (<b>E</b>) SSP 126, (<b>F</b>) SSP 370, and (<b>G</b>) SSP 585 for GFDL-ESM4] and <span class="html-italic">Streptopelia decaocto</span> [current (<b>H</b>) and future climate change scenario in 2050: (<b>I</b>) SSP 126, (<b>J</b>) SSP 370, and (<b>K</b>) SSP 585 for IPSL-CM6A-LR, and (<b>L</b>) SSP 126, (<b>M</b>) SSP 370, and (<b>N</b>) SSP 585 for GFDL-ESM4] in protected areas within the MCMA under climate change scenarios. Green areas show the suitable habitat of the invasive alien species (considering a threshold &gt; 0.3); gray areas indicate the unsuitable habitat of the invasive alien species (considering a threshold &lt; 0.3); and blue lines show the PAs in the MCMA.</p>
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<p>Piecewise linear regression of the annual distances from the <span class="html-italic">M. monachus</span> ((<b>A</b>); adjR<sup>2</sup> = 0.033, <span class="html-italic">p</span> &lt; 0.05) and <span class="html-italic">S. decaocto</span> ((<b>B</b>); adjR<sup>2</sup> = 0.013, <span class="html-italic">p</span> &lt; 0.05) first occurrence record in the MCMA provides rates of spread (<span class="html-italic">V</span>), corresponding to the slope of each segment, with black lines showing three possible phases of the spread process with two breakpoints (<span style="color:#FFC000">▲</span>) in 2011 and 2016 for <span class="html-italic">M. monachus</span> and 2016 and 2019 for <span class="html-italic">S. decaocto</span>. Slopes ± SE values reveal two possible stages of expansion and potential saturation of these invasive species. Red line is the regression line, and green dots are the distances of the points of occurrence per year with respect to the first point of occurrence detected.</p>
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16 pages, 9926 KiB  
Article
Automatic Methodology for Forest Fire Mapping with SuperDove Imagery
by Dionisio Rodríguez-Esparragón, Paolo Gamba and Javier Marcello
Sensors 2024, 24(16), 5084; https://doi.org/10.3390/s24165084 - 6 Aug 2024
Viewed by 621
Abstract
The global increase in wildfires due to climate change highlights the need for accurate wildfire mapping. This study performs a proof of concept on the usefulness of SuperDove imagery for wildfire mapping. To address this topic, we present an automatic methodology that combines [...] Read more.
The global increase in wildfires due to climate change highlights the need for accurate wildfire mapping. This study performs a proof of concept on the usefulness of SuperDove imagery for wildfire mapping. To address this topic, we present an automatic methodology that combines the use of various vegetation indices with clustering algorithms (bisecting k-means and k-means) to analyze images before and after fires, with the aim of improving the precision of the burned area and severity assessments. The results demonstrate the potential of using this PlanetScope sensor, showing that the methodology effectively delineates burned areas and classifies them by severity level, in comparison with data from the Copernicus Emergency Management Service (CEMS). Thus, the potential of the SuperDove satellite sensor constellation for fire monitoring is highlighted, despite its limitations regarding radiometric distortion and the absence of Short-Wave Infrared (SWIR) bands, suggesting that the methodology could contribute to better fire management strategies. Full article
(This article belongs to the Section Intelligent Sensors)
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Figure 1
<p>Pre-fire (first column) and post-fire (second column) images for the four selected events: (<b>a</b>,<b>b</b>) north Attica; (<b>c</b>,<b>d</b>) Portbou; (<b>e</b>,<b>f</b>) Euboea; (<b>g</b>,<b>h</b>) Sierra de los Guájares.</p>
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<p>Pre-fire (first column) and post-fire (second column) images for the four selected events: (<b>a</b>,<b>b</b>) north Attica; (<b>c</b>,<b>d</b>) Portbou; (<b>e</b>,<b>f</b>) Euboea; (<b>g</b>,<b>h</b>) Sierra de los Guájares.</p>
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<p>Scheme of the methodology to obtain the maps of burned area and fire severity.</p>
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<p>Processing of the DEM.</p>
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<p>Average differences between vegetation indices in pre- and post-fire images.</p>
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<p>Difference between pre- and post-fire images for different vegetation indices in north Attica area: (<b>a</b>) fire delimitation mask provided by CEMS, (<b>b</b>) EVI, (<b>c</b>) GEMI, (<b>d</b>) GNDVI1, (<b>e</b>) GNDVI2, (<b>f</b>) MSR, (<b>g</b>) NDVI, (<b>h</b>) SAVI, (<b>i</b>) SR, (<b>j</b>) WDRVI, and (<b>k</b>) YNDVI.</p>
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<p>Difference between pre- and post-fire images for different vegetation indices in north Attica area: (<b>a</b>) fire delimitation mask provided by CEMS, (<b>b</b>) EVI, (<b>c</b>) GEMI, (<b>d</b>) GNDVI1, (<b>e</b>) GNDVI2, (<b>f</b>) MSR, (<b>g</b>) NDVI, (<b>h</b>) SAVI, (<b>i</b>) SR, (<b>j</b>) WDRVI, and (<b>k</b>) YNDVI.</p>
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<p>Comparative visualization of the burned areas computed using the described methodology (in black) and those extracted from the CEMS report (in red) for the fires in (<b>a</b>) north Attica, (<b>b</b>) Portbou, (<b>c</b>) Euobea, and (<b>d</b>) Sierra de los Guájeres.</p>
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<p>Detailed views of discrepancy in burned-area edges. The red line delineates the fire’s extent as per CEMS data, contrasting with the yellow line that maps the area using the specified methodology: (<b>a</b>) pre-fire, (<b>b</b>) post-fire.</p>
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<p>Synthetized severity maps computed using the proposed methodology: (<b>a</b>) north Attica, (<b>b</b>) Portbou, (<b>c</b>) Euobea, and (<b>d</b>) Sierra de los Guájeres.</p>
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<p>Synthetized severity maps computed using the proposed methodology: (<b>a</b>) north Attica, (<b>b</b>) Portbou, (<b>c</b>) Euobea, and (<b>d</b>) Sierra de los Guájeres.</p>
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29 pages, 13770 KiB  
Article
Limitations of a Multispectral UAV Sensor for Satellite Validation and Mapping Complex Vegetation
by Brendan Cottrell, Margaret Kalacska, Juan-Pablo Arroyo-Mora, Oliver Lucanus, Deep Inamdar, Trond Løke and Raymond J. Soffer
Remote Sens. 2024, 16(13), 2463; https://doi.org/10.3390/rs16132463 - 5 Jul 2024
Cited by 3 | Viewed by 3127
Abstract
Optical satellite data products (e.g., Sentinel-2, PlanetScope, Landsat) require proper validation across diverse ecosystems. This has conventionally been achieved using airborne and more recently unmanned aerial vehicle (UAV) based hyperspectral sensors which constrain operations by both their cost and complexity of use. The [...] Read more.
Optical satellite data products (e.g., Sentinel-2, PlanetScope, Landsat) require proper validation across diverse ecosystems. This has conventionally been achieved using airborne and more recently unmanned aerial vehicle (UAV) based hyperspectral sensors which constrain operations by both their cost and complexity of use. The MicaSense Altum is an accessible multispectral sensor that integrates a radiometric thermal camera with 5 bands (475 nm–840 nm). In this work we assess the spectral reflectance accuracy of a UAV-mounted MicaSense Altum at 25, 50, 75, and 100 m AGL flight altitudes using the manufacturer provided panel-based reflectance conversion technique for atmospheric correction at the Mer Bleue peatland supersite near Ottawa, Canada. Altum derived spectral reflectance was evaluated through comparison of measurements of six known nominal reflectance calibration panels to in situ spectroradiometer and hyperspectral UAV reflectance products. We found that the Altum sensor saturates in the 475 nm band viewing the 18% reflectance panel, and for all brighter panels for the 475, 560, and 668 nm bands. The Altum was assessed against pre-classified hummock-hollow-lawn microtopographic features using band level pair-wise comparisons and common vegetation indices to investigate the sensor’s viability as a validation tool of PlanetScope Dove 8 band and Sentinel-2A satellite products. We conclude that the use of the Altum needs careful consideration, and its field deployment and reflectance output does not meet the necessary cal/val requirements in the peatland site. Full article
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<p>(<b>A</b>) Unmanned aerial vehicle (UAV) photograph of the Mer Bleue Peatland Observatory. (<b>B</b>) UAV photograph of the peatland margin illustrating a beaver pond with open water. (<b>C</b>) Vascular plants in hummocks. (<b>D</b>) Moss vegetation in hollows.</p>
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<p>(<b>A</b>) Altum mounted on the M300. (<b>B</b>) Mjolnir VS-620 hyperspectral sensor mounted on an octocopter with a gimbal for stabilization. (<b>C</b>) Six diffuse reflectance panels (2%, 5%, 10%, 18%, 40%, 50%) and the included MicaSense calibration reflectance panel. (<b>D</b>) HR1024i spectroradiometer taking field measurements of diffuse reflectance panels.</p>
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<p>Bottom-up approach to satellite product validation using UAV multispectral imagery.</p>
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<p>MicaSense recommended calibration procedure captured using an Insta360 camera. (<b>a</b>) Visible obstruction of diffuse irradiance during calibration (excluding the holder of the Insta360 at bottom). (<b>b</b>) Unobstructed sky.</p>
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<p>MicaSense Altum assessment workflow diagram. The field assessment is divided into two sections. Firstly, a comparison is made of panels with known HCRF to both the resampled Mjolnir V-1240 and each Altum flight. The vegetation assessment utilized pre-classified hummock hollow vegetation to compare the two satellite data products to both the Mjolnir V-1240 and Altum output.</p>
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<p>Comparison between the <span class="html-italic">R<sub>measured</sub></span> and <span class="html-italic">R<sub>adjusted</sub></span> of the calibration panel reflectance factor based on the proximity of the operator during calibration.</p>
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<p>Diffuse reference panel BCRF measurements in the laboratory with constant illumination conditions and in the field (HCRF) during time of data collection. HR1024i spectroradiometer and laboratory reflectance measurement under constant irradiance (dashed) and HR1024i spectroradiometer and field HCRF measurement (solid) on 19 July 2021. The scattered values are UAV mounted hyperspectral Mjolnir V-1240 reference panel spectra pixel values from 19 July 2021, resampled to the five bands of the Altum.</p>
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<p>Saturation of the Altum at the 475 nm, 560 nm, and 668 nm bands. Transect follows path shown on right with each panel labelled on the 25 m AGL graph at the top left.</p>
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<p>Reference panel reflectance factor using the recommended MicaSense workflow and independent calibration. (<b>a</b>) Altum panel spectra for all seven reference panels using recommended workflow; (<b>b</b>) Altum panel spectra for all seven reference panels using an independent workflow ELM.</p>
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<p>HR1024i panel HCRF plotted against the MicaSense recommended workflow and independent calibration. Progressively lighter colours indicate shorter wavelengths. Dotted line represents a 1:1 ratio between image and reference reflectance. (<b>a</b>) HR1024i HCRF relative to MicaSense workflow panel measurements; (<b>b</b>) HR1024i HCRF relative to independent ELM calibration panel measurements.</p>
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<p>Spatial offsets identified of the Altum relative to the Mjolnir V-1240.</p>
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<p>Comparing all pixels in the common study area to identify differences between sensors independent of the target composition.</p>
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<p>Comparison of the mean spectra of two complex vegetation targets. (<b>a</b>) Hummock measurements for all Altum altitudes, Mjolnir V-1240 hyperspectral, and two satellite products. (<b>b</b>) Hollow measurements for all Altum altitudes, Mjolnir V-1240 hyperspectral, and two satellite products.</p>
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<p>Histograms of each band (resampled for the Mjolnir V-1240) for hummocks and hollows of the four different altitude Altum datasets and the Mjolnir V-1240 dataset.</p>
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<p>Histograms of each index investigated for hummocks and hollows of the four different altitude Altum datasets and the Mjolnir V-1240 dataset.</p>
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<p>Boxplots comparing hummock and hollow data per band for seven datasets, the Altum multispectral data collected at four altitudes, the resampled Mjolnir V-1240 hyperspectral, as well as the Sentinel-2A surface reflectance product and PlanetScope Dove 8 band imagery. Abbreviations: Alt25: Altum (25 m), Alt50: Altum (50 m), Alt75: Altum (75 m), Alt100: Altum (100 m), HSI: Hyperspectral, S-2: Sentinel-2A, PS: PlanetScope Dove. The top and bottom of the whiskers in the boxplots represent minimum and maximum values, with the boxes representing the first quartile to the third quartile of values. The horizontal line through each box represents the median value of each dataset.</p>
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<p>Boxplots comparing hummock and hollow data for seven datasets at three different indices, the Altum multispectral data collected at four altitudes, the Mjolnir V-1240 hyperspectral, as well as the Sentinel-2A surface reflectance product and PlanetScope Dove 8 band imagery. Abbreviations: Alt25: Altum (25 m), Alt50: Altum (50 m), Alt75: Altum (75 m), Alt100: Altum (100 m), HSI: Hyperspectral, S-2: Sentinel-2A, PS: PlanetScope Dove. The top and bottom of the whiskers in the boxplots represent minimum and maximum values, with the boxes representing the first quartile to the third quartile of values. The horizontal line through each box represents the median value of each dataset.</p>
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<p>Multiple comparisons between each of the seven collected datasets for a total of twenty-one comparisons for each of the five bands. The closer to the center line of zero difference in means indicates closer agreement between the pairs. If the confidence interval includes zero, the results are not significantly different from one another. Abbreviations: Alt25: Altum (25 m), Alt50: Altum (50 m), Alt75: Altum (75 m), Alt100: Altum (100 m), HSI: Hyperspectral, S-2: Sentinel-2A, PS: PlanetScope Dove.</p>
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<p>Multiple comparisons between each of the seven collected datasets for a total of twenty-one comparisons for each of the three indices. The closer to the center line of zero difference in means indicates closer agreement between the pairs. If the confidence interval includes zero, the two compared are not significantly different from one another. Abbreviations: Alt25: Altum (25 m), Alt50: Altum (50 m), Alt75: Altum (75 m), Alt100: Altum (100 m), HSI: Hyperspectral, S-2: Sentinel-2A, PS: PlanetScope Dove.</p>
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33 pages, 32638 KiB  
Article
Design of a Technology-Based Magic Show System with Virtual User Interfacing to Enhance the Entertainment Effects
by Chao-Ming Wang and Qi-Jia Huang
Appl. Sci. 2024, 14(13), 5535; https://doi.org/10.3390/app14135535 - 26 Jun 2024
Cited by 2 | Viewed by 1111
Abstract
The integration of interactive technology into magic performances was explored in this study, with a focus on leveraging virtual user interfacing and interactive video projection techniques to enhance the entertainment effects. A thorough literature review identified transformation techniques between virtual and real forms [...] Read more.
The integration of interactive technology into magic performances was explored in this study, with a focus on leveraging virtual user interfacing and interactive video projection techniques to enhance the entertainment effects. A thorough literature review identified transformation techniques between virtual and real forms in the magic performance, along with various digital magic effects. Design principles derived from the review were applied in constructing a magic show system named “FUI Magic”, where FUI stands for fantasy user interface. The system is based on virtual user interfacing, implemented via laser range-finding and video projection techniques. The “FUI Magic” system facilitated the development and presentation of a digital-multimedia magic show titled “Fantasy Doves”, publicly showcased in an exhibition. Statistical evaluation of the feedback from expert interviews and a questionnaire survey revealed positive audience impressions and confirmed the effectiveness of incorporating virtual user-interfacing technology for captivating entertainment. This study affirms the significance of visual design through virtual user interfacing in enhancing technological ambiance and magic effects, suggesting its practicality for further exploration in diverse applications. Full article
(This article belongs to the Special Issue Application of Intelligent Human-Computer Interaction)
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<p>Diagram of magic effects resulting from conversions between the physical and the digital worlds.</p>
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<p>System module structure.</p>
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<p>The research process of this study.</p>
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<p>Physical design of the proposed system “FUI Magic”. (<b>a</b>) The structure of the system. (<b>b</b>) The appearance of the system when used in magic shows with the projections of magic presentation contents being displayed.</p>
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<p>The architecture of the proposed magic show system “FUI Magic”.</p>
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<p>Public exhibition of the proposed system “FUI Magic” and the presentation of the magic show “Fantasy Doves” designed in this study. (<b>a</b>) The stage and the background environment. (<b>b</b>) A back view of the audience watching the show. (<b>c</b>) A broader view of the stage and the audience.</p>
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<p>Results of the confirmatory factor analysis (CFA) using the AMOS package. (<b>a</b>) Diagram of the structural model of the scale of “magic viewing experience” generated through the CFA. (<b>b</b>) Diagram of the structural model of the scale of “multimedia technology understanding” generated through the CFA.</p>
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26 pages, 9310 KiB  
Article
Discrimination of Degraded Pastures in the Brazilian Cerrado Using the PlanetScope SuperDove Satellite Constellation
by Angela Gabrielly Pires Silva, Lênio Soares Galvão, Laerte Guimarães Ferreira Júnior, Nathália Monteiro Teles, Vinícius Vieira Mesquita and Isadora Haddad
Remote Sens. 2024, 16(13), 2256; https://doi.org/10.3390/rs16132256 - 21 Jun 2024
Cited by 1 | Viewed by 1149
Abstract
Pasture degradation poses significant economic, social, and environmental impacts in the Brazilian savanna ecosystem. Despite these impacts, effectively detecting varying intensities of agronomic and biological degradation through remote sensing remains challenging. This study explores the potential of the eight-band PlanetScope SuperDove satellite constellation [...] Read more.
Pasture degradation poses significant economic, social, and environmental impacts in the Brazilian savanna ecosystem. Despite these impacts, effectively detecting varying intensities of agronomic and biological degradation through remote sensing remains challenging. This study explores the potential of the eight-band PlanetScope SuperDove satellite constellation to discriminate between five classes of pasture degradation: non-degraded pasture (NDP); pastures with low- (LID) and moderate-intensity degradation (MID); severe agronomic degradation (SAD); and severe biological degradation (SBD). Using a set of 259 cloud-free images acquired in 2022 across five sites located in central Brazil, the study aims to: (i) identify the most suitable period for discriminating between various degradation classes; (ii) evaluate the Random Forest (RF) classification performance of different SuperDove attributes; and (iii) compare metrics of accuracy derived from two predicted scenarios of pasture degradation: a more challenging one involving five classes (NDP, LID, MID, SAD, and SBD), and another considering only non-degraded and severely degraded pastures (NDP, SAD, and SBD). The study assessed individual and combined sets of SuperDove attributes, including band reflectance, vegetation indices, endmember fractions from spectral mixture analysis (SMA), and image texture variables from Gray-level Co-occurrence Matrix (GLCM). The results highlighted the effectiveness of the transition from the rainy to the dry season and the period towards the beginning of a new seasonal rainy cycle in October for discriminating pasture degradation. In comparison to the dry season, more favorable discrimination scenarios were observed during the rainy season. In the dry season, increased amounts of non-photosynthetic vegetation (NPV) complicate the differentiation between NDP and SBD, which is characterized by high soil exposure. Pastures exhibiting severe biological degradation showed greater sensitivity to water stress, manifesting earlier reflectance changes in the visible and near-infrared bands of SuperDove compared to other classes. Reflectance-based classification yielded higher overall accuracy (OA) than the approaches using endmember fractions, vegetation indices, or texture metrics. Classifications using combined attributes achieved an OA of 0.69 and 0.88 for the five-class and three-class scenarios, respectively. In the five-class scenario, the highest F1-scores were observed for NDP (0.61) and classes of agronomic (0.71) and biological (0.88) degradation, indicating the challenges in separating low and moderate stages of pasture degradation. An initial comparison of RF classification results for the five categories of degraded pastures, utilizing reflectance data from MultiSpectral Instrument (MSI)/Sentinel-2 (400–2500 nm) and SuperDove (400–900 nm), demonstrated an enhanced OA (0.79 versus 0.66) with Sentinel-2 data. This enhancement is likely to be attributed to the inclusion of shortwave infrared (SWIR) spectral bands in the data analysis. Our findings highlight the potential of satellite constellation data, acquired at high spatial resolution, for remote identification of pasture degradation. Full article
(This article belongs to the Section Remote Sensing in Agriculture and Vegetation)
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<p>Summary of the methodology used in the current work to discriminate pasture degradation with SuperDove satellite constellation data.</p>
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<p>Location of the five sites (15 × 15 km each) selected in the southeastern region of the Brazilian state of Goiás in a climatically homogeneous region. The insets show photographs representative of non-degraded pasture (NDP) and of pastures with low-intensity degradation (LID), moderate-intensity degradation (MID), severe agronomic degradation (SAD), and severe biological degradation (SBD). The sites are numbered according to the municipality where they are located: 1. Bela Vista de Goiás; 2. Caldas Novas; 3. Piracanjuba; 4. Pontalina; and 5. Trindade. Long-term monthly precipitation (average values between 2001 and 2021) and the dry season period are also indicated for reference.</p>
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<p>Frequency of cloud-free images captured by the SuperDove satellite constellation in 2022 for each of the five selected sites targeted for analysis. The dry season period is indicated for reference.</p>
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<p>False color composites generated from SuperDove imagery, illustrating visual distinctions between plots of biologically degraded (SBD) and non-degraded (NDP) pastures across various seasonal stages. Notable time points include the rainy season (DOY 62 and 324 in (<b>a</b>,<b>e</b>)), the transition from the rainy to the dry season (DOY 153 in (<b>b</b>)), the middle of the dry season (DOY 227 in (<b>c</b>)), and the transition from the dry to the rainy season (DOY 273 in (<b>d</b>)). SuperDove bands 8 (NIR), 7 (red-edge) and 6 (red) are shown in red, green and blue colors, respectively.</p>
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<p>Seasonal variations in mean reflectance for both (<b>a</b>) red and (<b>b</b>) near-infrared (NIR) bands (SuperDove bands 6 and 8) across different pasture degradation classes. The symbols within the profiles denote data acquisition in 2022 through the satellite constellation. Class abbreviations are defined in the text.</p>
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<p>Seasonal variation in the Mahalanobis distance for discriminating areas of Severe Agronomic Degradation (SAD) from those with Low- (LID) and Moderate-intensity (MID) degradation using the eight-band reflectance data from SuperDove.</p>
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<p>Endmember reflectance spectra derived from Sequential Maximum Angle Convex Cone (SMACC) for SuperDove data acquired on 2 June (DOY 153) over areas exhibiting varying degrees of pasture degradation across the five studied sites in central Brazil.</p>
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<p>Scatterplots illustrating the relationships between (<b>a</b>) NDVI and GRND and (<b>b</b>) EVI and REND for three field-sampled classes of pasture degradation: Non-degraded pasture (NDP) and pastures with severe agronomic (SAD) and biological (SBD) degradation.</p>
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<p>False color composites (SuperDove bands 8, 7, and 6 in RGB) illustrating examples of the five classes of pasture degradation (NDP, LID, MID, SAD, and SBD) are presented on the left side of the figure. In the middle panel, color composites of green vegetation (GV1), GV2, and soil (S) fraction images in RGB are displayed. Lastly, NDVI images are presented on the right side.</p>
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<p>Variations in Gray Level Co-occurrence Matrix (GLCM) texture metrics, specifically (<b>a</b>) texture mean and (<b>b</b>) texture variance, calculated from the Near-Infrared (NIR) band 8 of SuperDove for the five classes of pasture degradation.</p>
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<p>Variations in Precision, Recall, F1-score, and Overall Accuracy (OA) resulting from the Random Forest (RF) classification of five classes of pasture degradation (NDP, LID, MID, SAD, and SBD). The classifier utilized individual attributes, including the reflectance of the eight SuperDove bands, five vegetation indices (EVI, GRND, MPRI, NDVI, and REND), and four-endmember fractions from Spectral Mixture Analysis (SMA) (GV1, GV2, soil, and shade). Results from GLCM texture metrics were excluded for enhanced graphical representation. The reported results refer to the validation dataset.</p>
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<p>Percentage of importance assigned to each variable in the Random Forest (RF) classification of five classes of pasture degradation (NDP, LID, MID, SAD, and SBD).</p>
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<p>(<b>a</b>) Ground truth map and (<b>b</b>) Random Forest classification of degraded and non-degraded pastures. Classification uncertainties are depicted in (<b>c</b>). The abbreviations are defined in the text.</p>
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<p>Variations in F1-score and Overall Accuracy (OA) resulting from the Random Forest (RF) classification of five classes of pasture degradation (NDP, LID, MID, SAD, and SBD) using the combined sets of attributes. Results are presented for two dates representing the transition from the rainy to the dry season (DOY 153 in June; blue color results) and the middle of the dry season (DOY 227 in August; red color results). The reported results refer to the validation dataset.</p>
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<p>Average reflectance spectra from OLI/Landsat-8 data acquired over field-surveyed plots representing non-degraded pastures and pastures experiencing severe agronomical or biological degradation. The results are presented for various dates during the year 2021, specifically during (<b>a</b>) the transition from the rainy to the dry season, (<b>b</b>) the middle of the dry season, and (<b>c</b>) after the occurrence of the first rainfall events in the new seasonal cycle in October.</p>
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<p>Variations in F1-score and Overall Accuracy (OA) resulting from the Random Forest (RF) classification of five classes of pasture degradation (NDP, LID, MID, SAD, and SBD) using reflectance data of 10 bands (10-m and 20-m spatial resolution) from the Multispectral Instrument (MSI)/Sentinel-2 (400–2500 nm) and eight bands from the SuperDove (400–900 nm). Images from both instruments were acquired in approximately coincident dates (2 and 4 June 2022). The reported results in blue (SuperDove) and red (MSI/Sentinel-2) colors refer to the validation dataset.</p>
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15 pages, 3798 KiB  
Article
Human Perception of Birds in Two Brazilian Cities
by Gabriela Rosa Graviola, Milton Cezar Ribeiro and João Carlos Pena
Birds 2024, 5(2), 202-216; https://doi.org/10.3390/birds5020014 - 19 Apr 2024
Viewed by 2176
Abstract
Understanding how humans perceive animals is important for biodiversity conservation, however, only a few studies about this issue have been carried out in South America. We selected two Brazilian cities to assess people’s perceptions of birds: Bauru (São Paulo, Brazil) and Belo Horizonte [...] Read more.
Understanding how humans perceive animals is important for biodiversity conservation, however, only a few studies about this issue have been carried out in South America. We selected two Brazilian cities to assess people’s perceptions of birds: Bauru (São Paulo, Brazil) and Belo Horizonte (Minas Gerais, Brazil). From the available bird data for each city, we developed a questionnaire and applied it between September 2020 and June 2021. The data obtained were analyzed by simple counts, a Likert scale, and percentages. Also, human feelings related to birds were placed on the Free Word Cloud Generator website. Our study confirmed that most respondents were aware of the importance of birds to ecological balance and that respondents had a generally positive attitude towards most of the bird species. However, they disliked exotic species such as the Domestic Dove and the House Sparrow, which are associated with disease, dirt, and disgust. Respondents also underestimated the number of birds that can live in urban areas and the song of birds is still a sense less experienced and perceived by people. Understanding these human–biodiversity relationships can help guide public policies and environmental education activities. Full article
(This article belongs to the Special Issue Birds and People)
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<p>Percentage of people who observed these 15 bird species most frequently recorded during surveys in Brazilian cities: (<b>A</b>) Bauru (São Paulo) and (<b>B</b>) Belo Horizonte (Minas Gerais). The percentage represents birds that are the most seen by people daily and f means the frequency of each species recorded during our surveys. The bird’s pictures are watercolors painted by Gabriela Rosa based on scientific illustrations from the <span class="html-italic">Handbook of the Birds of the World</span> (HBW Alive).</p>
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<p>Percentage of people who had seen the 5 bird species least frequently recorded during surveys in Brazilian cities: (<b>A</b>) Bauru (São Paulo) and (<b>B</b>) Belo Horizonte (Minas Gerais). The percentage represents birds that are the most seen by people daily and f means the frequency of each species recorded during our surveys. The bird’s pictures are watercolors painted by Gabriela Rosa based on scientific illustrations from the <span class="html-italic">Handbook of the Birds of the World</span> (HBW Alive).</p>
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<p>Percentage of people who have heard the song of these bird species in Brazilian cities: (<b>A</b>) Bauru (São Paulo) and (<b>B</b>) Belo Horizonte (Minas Gerais). The percentage represents birds that are the most seen by people daily and f means the frequency of each species recorded during our surveys. The bird’s pictures are watercolors painted by Gabriela Rosa based on scientific illustrations from the <span class="html-italic">Handbook of the Birds of the World</span> (HBW Alive).</p>
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<p>Word cloud analysis of the main feelings that respondents associate with urban birds in two Bra-zilian cities: (<b>A</b>) Bauru (São Paulo) and (<b>B</b>) Belo Horizonte (Minas Gerais).</p>
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13 pages, 231 KiB  
Article
Nature’s Apostle: The Dove as Communicator in the Hebrew Bible, from Ararat to Nineveh
by Menahem Blondheim and Hananel Rosenberg
Religions 2024, 15(4), 502; https://doi.org/10.3390/rel15040502 - 19 Apr 2024
Viewed by 1522
Abstract
The dove, the most frequently mentioned bird in the Hebrew Bible, appears in diverse contexts, spanning its appearance as an element in the narrative (as in the case of Noah’s ark), and as an allegory and metaphor (as in the cryptic “sword of [...] Read more.
The dove, the most frequently mentioned bird in the Hebrew Bible, appears in diverse contexts, spanning its appearance as an element in the narrative (as in the case of Noah’s ark), and as an allegory and metaphor (as in the cryptic “sword of the dove”—twice in Jeremiah—and “the city of the dove”—Zephaniah). The dove even appears as the proper name of a prophet (or possibly of two, both named Jonah, son of Amittai). This article applies a communication perspective to better interpret some of these texts. We argue that the dove’s communicative attributes, to include unique acoustics, remarkable power of flight, but primarily the trait of returning home—the basis for the use of doves as carrier pigeons—may either explain or deepen the interpretation of many of the references to the pigeon in the Bible. In this vein, a major focus of the article is on using the dove’s homing ability as a key for reinterpreting the Book of Jonah. We conclude by suggesting that the dove’s trait of returning and, hence, its use as envoy made it a useful symbol of the deity’s presence in the world. In the Jewish reading, it became an emblem of one of the main political and eschatological themes of the Bible: the return home from exile, beginning with the exodus and return of Jacob’s sons to Canaan and ending with the Eschaton. Full article
(This article belongs to the Section Religions and Theologies)
13 pages, 8585 KiB  
Article
Genetic Characterization, Pathogenicity, and Epidemiology Analysis of Three Sub-Genotype Pigeon Newcastle Disease Virus Strains in China
by Zeren Wang, Zhengyang Geng, Hongbo Zhou, Pengju Chen, Jing Qian and Aizhen Guo
Microorganisms 2024, 12(4), 738; https://doi.org/10.3390/microorganisms12040738 - 4 Apr 2024
Viewed by 1633
Abstract
Pigeon Newcastle disease (ND) is a serious infectious illness caused by the pigeon Newcastle disease virus (NDV) or Paramyxovirus type 1 (PPMV-1). Genotype VI NDV is a primary factor in ND among Columbiformes (such as pigeons and doves). In a recent study, eight [...] Read more.
Pigeon Newcastle disease (ND) is a serious infectious illness caused by the pigeon Newcastle disease virus (NDV) or Paramyxovirus type 1 (PPMV-1). Genotype VI NDV is a primary factor in ND among Columbiformes (such as pigeons and doves). In a recent study, eight pigeon NDV strains were discovered in various provinces in China. These viruses exhibited mesogenic characteristics based on their MDT and ICPI values. The complete genome sequences of these eight strains showed a 90.40% to 99.19% identity match with reference strains of genotype VI, and a 77.86% to 80.45% identity match with the genotype II vaccine strain. Additionally, analysis of the F gene sequence revealed that these NDV strains were closely associated with sub-genotypes VI.2.2.2, VI.2.1.1.2.1, and VI.2.1.1.2.2. The amino acid sequence at the cleavage site of the F protein indicated virulent characteristics, with the sequences 112KRQKRF117 and 112RRQKRF117 observed. Pigeons infected with these sub-genotype strains had a low survival rate of only 20% to 30%, along with lesions in multiple tissues, highlighting the strong spread and high pathogenicity of these pigeon NDV strains. Molecular epidemiology data from the GenBank database revealed that sub-genotype VI.2.1.1.2.2 strains have been prevalent since 2011. In summary, the findings demonstrate that the prevalence of genotype VI NDV is due to strains from diverse sub-genotypes, with the sub-genotype VI.2.1.1.2.2 strain emerging as the current epidemic strain, highlighting the significance of monitoring pigeon NDV in China. Full article
(This article belongs to the Special Issue Poultry Pathogens and Poultry Diseases)
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<p>Nucleotide identity analysis was performed on the whole genome sequences of eight pigeon NDV isolates detected in this study, as well as 21 other reference NDV strains.</p>
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<p>Phylogenetic analysis of the F region of eight pigeon NDV isolates detected in this study and other reference NDV strains (n = 43). A phylogenetic tree was constructed based on the complete F gene sequences using the maximum likelihood (ML) method with 500 bootstrap replicates and the Poisson model in MEGA 7.0 software. Note: Pigeon/China/VI-NJ/2006, Pigeon/China/VI-HZ/2017, Pigeon/China/WZ2201/2022, Pigeon/China/WZ2205/2022, Pigeon/China/HB2306/2023, Pigeon/China/HB2307/2023, Pigeon/China/HB2308/2023, and Pigeon/China/HB2309/2023 in this study are labeled with a red solid circle (<span style="color:red">●</span>).</p>
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<p>Survival rates, virus shedding, and histopathological observations of tissues were recorded from pigeons inoculated with three sub-genotypes of NDV: Pigeon/China/VI-NJ/2006, Pigeon/China/VI-HZ/2017, and Pigeon/China/WZ2205/2022. (<b>a</b>) Survival rate of pigeons inoculated with three sub-genotype strains. (<b>b</b>) Detection of virus shedding from pigeons with three sub-genotype strains on Day 14. (<b>c</b>–<b>e</b>) Edema in the brain. (<b>f</b>) No abnormality in the brain. (<b>g</b>–<b>i</b>) Necrosis and desquamation of mucous epithelial cells in the trachea. (<b>j</b>) No abnormality in the trachea. (<b>k</b>–<b>m</b>) Broken villi, dropout of epithelium, hemorrhage, and lamina propria inflammatory reaction in the intestine. (<b>n</b>) No abnormality in the intestine.</p>
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<p>Investigating Pigeon Newcastle Disease Virus using Molecular Epidemiology. (<b>a</b>) Worldwide genotypic classification and statistics of pigeon Newcastle disease virus are essential for understanding the spread of the virus. (<b>b</b>) Genotypic classification and statistics of pigeon Newcastle disease virus in China are as follows. (<b>c</b>) Statistics on the isolation time of Chinese genotype 6 pigeon Newcastle disease virus. The numbers and colors on each column represent the number of different sub-genotype strains, with green representing genotype VI.1, orange representing genotype VI.2.2.2, blue representing genotype VI.2.1.1.2.1, and red representing genotype VI.2.1.1.2.2.</p>
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28 pages, 16606 KiB  
Article
Research on Improvement Methods for Driven System of Bio-Inspired Aircraft to Increase Flight Speed
by Dong Xue, Runkang Li and JiaYuan Liu
Drones 2024, 8(4), 133; https://doi.org/10.3390/drones8040133 - 1 Apr 2024
Viewed by 1052
Abstract
The flapping-wing ornithopter is an aircraft that imitates the flight of birds in nature. It has significant potential and value in various fields such as surveying, search and rescue, military reconnaissance, and unmanned warfare, due to its biomimetic stealth and high efficiency in [...] Read more.
The flapping-wing ornithopter is an aircraft that imitates the flight of birds in nature. It has significant potential and value in various fields such as surveying, search and rescue, military reconnaissance, and unmanned warfare, due to its biomimetic stealth and high efficiency in low Reynolds number flight. However, the cruising speed of current flapping-wing ornithopters is generally lower than that of birds of the same size, which seriously affects biomimicry, mission capability, and wind resistance. Increasing the cruising speed can make the aircraft fly more like a bird, improve the efficiency of reconnaissance missions and wind resistance per unit time, and has important research significance. However, the methods to increase the cruising speed of flapping-wing ornithopters are currently lacking. Firstly, this paper presents improvements to the propulsion system based on the team’s “Dove” aircraft to meet the speed requirements. The actual flapping frequency and rocking arm end torque of the “Dove” aircraft under different voltages are tested. To select and match the motor and gearbox in the propulsion system, a method for matching and selection among the motor, gearbox, and load is proposed. Finally, wind tunnel experiments and flight validations are conducted on the improved flight prototype. The wind tunnel experiments show that the increase in flapping frequency has a significant impact on thrust. The trimmed states at different speeds are obtained. The flight validation demonstrates the sustained high-speed flight capability of the aircraft. At a flapping frequency of approximately 15 Hz, the average flight speed of the aircraft is 13.3 m/s within a 15 min duration, which is close to the actual flight speed of pigeons. The duration of high-speed flight is tripled compared to the initial duration. The speed improvement successfully enhances the biomimicry and efficiency of reconnaissance missions per unit time for the aircraft. Full article
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<p>Design process of mechanical transmission flapping mechanism.</p>
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<p>The propulsion system of the “Dove” aircraft.</p>
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<p>Testing of wing-flapping frequency in the “Dove” mechanism.</p>
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<p>Actual wing-flapping frequency of the “Dove” at different voltages.</p>
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<p>The relationship between motor voltage, motor current, and wing-flapping frequency.</p>
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<p>Power transmission flowchart of the drive system.</p>
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<p>Motor efficiency of different motors at various voltages.</p>
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<p>Torque transmission process diagram.</p>
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<p>Feasible range for gear ratio selection of GTS V3 2104 motor.</p>
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<p>Flight test prototype’s drive system.</p>
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<p>Aircraft test prototype.</p>
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<p>Specialized wind tunnel for flapping-wing aircraft.</p>
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<p>Current sampling system.</p>
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<p>Wind tunnel load test diagram of the flight test prototype.</p>
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<p>Variation of lift and thrust with angle of attack at different throttle settings.</p>
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<p>Variation of angle of attack at zero thrust and corresponding lift with flapping frequency.</p>
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<p>At a wind speed of 10 m/s, the variation of lift with flapping frequency is studied for different motors and different angles of attack. (<b>a</b>) The variation of lift with angle of attack is studied for the GTS V3 2104 motor at different flapping frequencies. (<b>b</b>) The variation of lift with angle of attack is studied for the Aeolus 2105.5 motor at different flapping frequencies.</p>
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<p>At a wind speed of 10 m/s, the variation of thrust with flapping frequency is studied for different motors and different angles of attack. (<b>a</b>) The variation of thrust with angle of attack is studied for the GTS V3 2104 motor at different flapping frequencies. (<b>b</b>) The variation of thrust with angle of attack is studied for the Aeolus 2105.5 motor at different flapping frequencies.</p>
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<p>The variation of lift and thrust with angle of attack is analyzed at a wind speed of 10 m/s for different motors and flapping frequencies. (<b>a</b>) The variation of lift with angle of attack is analyzed at a wind speed of 10 m/s for different motors and flapping frequencies. (<b>b</b>) The variation of thrust with angle of attack is analyzed at a wind speed of 10m/s for different motors and flapping frequencies.</p>
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<p>At a wind speed of 12.5 m/s, the variation of lift with flapping frequency is studied for different motors and different angles of attack. (<b>a</b>) The variation of lift with angle of attack is studied for the GTS V3 2104 motor at different flapping frequencies. (<b>b</b>) The variation of lift with angle of attack is studied for the Aeolus 2105.5 motor at different flapping frequencies.</p>
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<p>At a wind speed of 12.5 m/s, the variation of thrust with flapping frequency is studied for different motors and different angles of attack. (<b>a</b>) The variation of thrust with angle of attack is studied for the GTS V3 2104 motor at different flapping frequencies. (<b>b</b>) The variation of thrust with angle of attack is studied for the Aeolus 2105.5 motor at different flapping frequencies.</p>
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<p>The curves depicting the variation of lift and thrust with angle of attack are analyzed at a wind speed of 12.5 m/s for different motors and flapping frequencies. (<b>a</b>) The variation of lift with angle of attack is analyzed at a wind speed of 10 m/s for different motors and flapping frequencies. (<b>b</b>) The variation of thrust with angle of attack is analyzed at a wind speed of 10m/s for different motors and flapping frequencies.</p>
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<p>The curves depicting the variation of lift and thrust with angle of attack are analyzed for the GTS V3 2104 motor at different wind speeds and flapping frequencies. (<b>a</b>) The variation of lift with angle of attack is studied at different wind speeds and flapping frequencies. (<b>b</b>) The variation of thrust with angle of attack is studied at different wind speeds and flapping frequencies.</p>
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<p>The curves depicting the variation of lift and thrust with angle of attack are analyzed for the Aeolus 2105.5 motor at different wind speeds and flapping frequencies. (<b>a</b>) The variation of lift with angle of attack is studied at different wind speeds and flapping frequencies. (<b>b</b>) The variation of thrust with angle of attack is studied at different wind speeds and flapping frequencies.</p>
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<p>The power output of the GTS V3 2104 motor varies with angle of attack at different wind speeds and flapping frequencies.</p>
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<p>The power output of the Aeolus 2105.5 motor varies with angle of attack at different wind speeds and flapping frequencies.</p>
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<p>Curves depicting the variation of input power with angle of attack for the GTS V3 2104 motor flight test prototype at different wind speeds and flapping frequencies.</p>
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<p>Curves depicting the variation of input power with angle of attack for the Aeolus 2105.5 motor flight test prototype at different wind speeds and flapping frequencies.</p>
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<p>Curve depicting the variation of the angle of attack at zero thrust and the corresponding lift with respect to the flapping frequency at a wind speed of 12.5 m/s.</p>
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<p>Curve depicting the variation of the angle of attack at zero thrust and the corresponding lift with respect to the flapping frequency at a wind speed of 10 m/s.</p>
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<p>Curves depicting the variation of trimmed flapping frequency and angle of attack with respect to velocity.</p>
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<p>Initial pitch angle of the aircraft.</p>
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<p>(<b>a</b>) Variation of pitch angle, velocity, and altitude of the aircraft over time during the interval of 180 s~181 s. (<b>b</b>) Variation of pitch angle, velocity, and altitude of the aircraft over time during the interval of 184 s~185 s. (<b>c</b>) Variation of pitch angle, velocity, and altitude of the aircraft over time during the interval of 262 s~263 s.</p>
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<p>Flight spectrum plot.</p>
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<p>Variation of aircraft pitch angle over time during the flight phase.</p>
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<p>Curve depicting the variation of aircraft speed with flight time.</p>
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14 pages, 271 KiB  
Article
The Genealogy of Play
by Pam Jarvis
Genealogy 2024, 8(2), 38; https://doi.org/10.3390/genealogy8020038 - 1 Apr 2024
Viewed by 3497
Abstract
In 1924, exactly a century ago, the world-famous children’s author Alan Milne wrote this much-loved rhyme about the play activities of his young son: Where am I going? I don’t quite know. Down to the stream where the king-cups grow-Up on the hill [...] Read more.
In 1924, exactly a century ago, the world-famous children’s author Alan Milne wrote this much-loved rhyme about the play activities of his young son: Where am I going? I don’t quite know. Down to the stream where the king-cups grow-Up on the hill where the pine-trees blow-Anywhere, anywhere. I don’t know…Where am I going? The high rooks call: “It’s awful fun to be born at all”. Where am I going? The ring-doves coo: “We do have beautiful things to do”. But in 2024, in much of the Western world, allowing a young child to wander in this manner would be seen by many as dangerous, reckless and negligent. For example, in 2019, Renee Umstattd Meyer and her colleagues found that a large proportion of children in the post-industrial world did not take the recommended amount of exercise in the outdoor environment, and even where spaces were specifically made available to them, parents feared that they would be infiltrated by crime and violence. This article considers the emergent effects of significant cultural change in children’s independent and collaborative free play opportunities. It draws on an ethological and biocultural perspective to argue why independent, active free play, particularly involving peer collaboration, is so important to human development. Full article
17 pages, 5313 KiB  
Article
Monitoring Water Quality Parameters in Small Rivers Using SuperDove Imagery
by Katerina Vatitsi, Sofia Siachalou, Dionissis Latinopoulos, Ifigenia Kagalou, Christos S. Akratos and Giorgos Mallinis
Water 2024, 16(5), 758; https://doi.org/10.3390/w16050758 - 2 Mar 2024
Cited by 1 | Viewed by 2039
Abstract
Freshwater ecosystems provide an array of provisioning, regulating/maintenance, and cultural ecosystem services. Despite their crucial role, freshwater ecosystems are exceptionally vulnerable due to changes driven by both natural and human factors. Water quality is essential for assessing the condition and ecological health of [...] Read more.
Freshwater ecosystems provide an array of provisioning, regulating/maintenance, and cultural ecosystem services. Despite their crucial role, freshwater ecosystems are exceptionally vulnerable due to changes driven by both natural and human factors. Water quality is essential for assessing the condition and ecological health of freshwater ecosystems, and its evaluation involves various water quality parameters. Remote sensing has become an efficient approach for retrieving and mapping these parameters, even in optically complex waters such as small rivers. This study specifically focuses on modelling two non-optically active water quality parameters, dissolved oxygen (DO) and electrical conductivity (EC), by integrating 3 m PlanetScope satellite imagery with data from real-time in situ remote monitoring sensors across two small rivers in Thrace, Northeast Greece. We employed three different experimental setups using a support vector regression (SVR) algorithm: ‘Multi-seasonal by Individual Sensor’ (M-I-S) for individual sensor analysis across two seasons, ‘Multi-seasonal—All Sensors’ (M-A-S) integrating data across all seasons and sensors, and ‘Seasonal—All Sensors’ (S-A-S) focusing on per-season sensor data. The models incorporating multiple seasons and all in situ sensors resulted in R2 values of 0.549 and 0.657 for DO and EC, respectively. A multi-seasonal approach per in situ sensor resulted in R2 values of 0.885 for DO and 0.849 for EC. Meanwhile, the seasonal approach, using all in situ sensors, achieved R2 values of 0.805 for DO and 0.911 for EC. These results underscore the significant potential of combining PlanetScope data and machine learning to model these parameters and monitor the condition of ecosystems over small river surfaces. Full article
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<p>Laspias River and Lissos River basins, and locations of the four real-time remote monitoring in situ sensors.</p>
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<p>Taylor diagrams of DO (<b>a</b>) and EC (<b>b</b>) of ‘Multi-seasonal by Individual Sensor’ (M-I-S) models. Distance between model and reference point is a measure of how realistically each model reproduces observations. The azimuthal angle represents the correlation between predicted and observed values, and RMSE is shown by the blue contours. The radial distance from the origin (black contours) refers to the standard deviation.</p>
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<p>Scatter plots (<b>a</b>,<b>c</b>) and Taylor diagrams (<b>b</b>,<b>d</b>) of M-A-S DO and EC models, respectively. The red dashed line is the 1:1 reference line, and the blue dotted line is the trend line considering the relationship between predicted and observed values.</p>
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<p>Scatter plots of S-A-S DO (<b>a</b>,<b>b</b>) and EC models (<b>c</b>,<b>d</b>). Plots (<b>a</b>,<b>c</b>) refer to the spring period, and plots (<b>b</b>,<b>d</b>) refer to the summer period. The red dashed line is the 1:1 reference line, and the blue dotted line is the trend line considering the relationship between predicted and observed values.</p>
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<p>Electrical conductivity distribution maps around the Lis-1 (<b>a</b>,<b>d</b>,<b>g</b>), Lis-2 (<b>b</b>,<b>e</b>,<b>h</b>), and Lis-3 (<b>c</b>,<b>f</b>,<b>i</b>) sites in the Lissos River on 25 March 2022 (<b>a</b>–<b>c</b>), 22 June 2022 (<b>d</b>–<b>f</b>), and 29 October 2022 (<b>g</b>–<b>i</b>) based on the M-A-S models.</p>
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<p>Dissolved oxygen distribution maps around the Lis-1 (<b>a</b>,<b>d</b>,<b>g</b>), Lis-2 (<b>b</b>,<b>e</b>,<b>h</b>), and Lis-3 (<b>c</b>,<b>f</b>,<b>i</b>) sites in the Lissos River on 25 March 2022 (<b>a</b>–<b>c</b>), 22 June 2022 (<b>d</b>–<b>f</b>), and 29 October 2022 (<b>g</b>–<b>i</b>) based on the M-A-S models.</p>
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<p>Electrical conductivity distribution maps around the Las-1 site in the Laspias River on 25 March 2022 (<b>a</b>), 27 June 2022 (<b>b</b>), and 28 October 2022 (<b>c</b>) based on the M-I-S models.</p>
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<p>Dissolved oxygen distribution maps around the Las-1 site in the Laspias River on 25 March 2022 (<b>a</b>), 27 June 2022 (<b>b</b>), and 28 October 2022 (<b>c</b>) based on the M-I-S models.</p>
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