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Keywords = individual tree detection

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15 pages, 3341 KiB  
Article
Geography and the Environment Shape the Landscape Genetics of the Vulnerable Species Ulmus lamellosa in Northern China
by Li Liu, Yuexin Shen, Yimeng Zhang, Ting Gao and Yiling Wang
Forests 2024, 15(12), 2190; https://doi.org/10.3390/f15122190 - 12 Dec 2024
Viewed by 313
Abstract
A comprehensive understanding of the pattern of genetic variation among populations and adaptations to environmental heterogeneity is very important for conservation and genetic improvement. Forest tree species are ideal resources for understanding population genetic differentiation and detecting signatures of selection due to their [...] Read more.
A comprehensive understanding of the pattern of genetic variation among populations and adaptations to environmental heterogeneity is very important for conservation and genetic improvement. Forest tree species are ideal resources for understanding population genetic differentiation and detecting signatures of selection due to their adaptations to heterogeneous landscapes. Ulmus lamellosa is a tree species that is endemic to northern China. In this study, using restriction-site-associated DNA sequencing (RAD-seq) data, 12,179 single-nucleotide polymorphisms were identified across 51 individuals from seven populations. There was a high level of genetic diversity and population differentiation in U. lamellosa. Population genetic structure analyses revealed a significant genetic structure related to the configuration of the mountains. Additionally, we found that the isolation-by-distance pattern explained the genetic differentiation best, and environmental heterogeneity also played a role in shaping the landscape genetics of this species inhabiting mountain ecosystems. The FST-based outlier and genotype–environment association approaches were used to explore the genomic signatures of selection and local adaptation and detected 317 candidate outlier loci. Precipitation seasonality (coefficient of variation), precipitation in the driest month, and enhanced vegetation index were important determinants of adaptive genetic variation. This study provides abundant genetic resources for U. lamellosa and insights into the genetic variation patterns among populations. Full article
(This article belongs to the Section Genetics and Molecular Biology)
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Figure 1
<p>Geographic locations across species distribution for seven <span class="html-italic">U. lamellosa</span> populations.</p>
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<p>Histogram of the ADMIXTURE (<span class="html-italic">K</span> = 2–4) assignment test for <span class="html-italic">U. lamellosa</span>. Each color represents a distinct genetic group.</p>
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<p>Results of principal component analysis (PCA) of the 51 <span class="html-italic">U. lamellosa</span> individuals.</p>
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<p>Plot of log<sub>10</sub> (<span class="html-italic">q</span>-value) and <span class="html-italic">F</span><sub>ST</sub> values from the BayeScan analysis. The vertical black line represents the cutoff of <span class="html-italic">q</span> values = 0.05. Solid dots represent 12,179 SNPs. Solid red dots with <span class="html-italic">q</span> values &lt; 0.05 represent the outlier SNPs.</p>
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<p>The first two axes of redundancy analysis (RDA) for all loci and outlier loci. The black arrows indicate the environmental variables. The colored points indicate sampling sites. Abbreviations of environmental variables and sampling sites are presented in <a href="#app1-forests-15-02190" class="html-app">Table S5</a> and <a href="#forests-15-02190-t001" class="html-table">Table 1</a>, respectively.</p>
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30 pages, 12451 KiB  
Article
A Method Coupling NDT and VGICP for Registering UAV-LiDAR and LiDAR-SLAM Point Clouds in Plantation Forest Plots
by Fan Wang, Jiawei Wang, Yun Wu, Zhijie Xue, Xin Tan, Yueyuan Yang and Simei Lin
Forests 2024, 15(12), 2186; https://doi.org/10.3390/f15122186 - 12 Dec 2024
Viewed by 239
Abstract
The combination of UAV-LiDAR and LiDAR-SLAM (Simultaneous Localization and Mapping) technology can overcome the scanning limitations of different platforms and obtain comprehensive 3D structural information of forest stands. To address the challenges of the traditional registration algorithms, such as high initial value requirements [...] Read more.
The combination of UAV-LiDAR and LiDAR-SLAM (Simultaneous Localization and Mapping) technology can overcome the scanning limitations of different platforms and obtain comprehensive 3D structural information of forest stands. To address the challenges of the traditional registration algorithms, such as high initial value requirements and susceptibility to local optima, in this paper, we propose a high-precision, robust, NDT-VGICP registration method that integrates voxel features to register UAV-LiDAR and LiDAR-SLAM point clouds at the forest stand scale. First, the point clouds are voxelized, and their normal vectors and normal distribution models are computed, then the initial transformation matrix is quickly estimated based on the point pair distribution characteristics to achieve preliminary alignment. Second, high-dimensional feature weighting is introduced, and the iterative closest point (ICP) algorithm is used to optimize the distance between the matching point pairs, adjusting the transformation matrix to reduce the registration errors iteratively. Finally, the algorithm converges when the iterative conditions are met, yielding an optimal transformation matrix and achieving precise point cloud registration. The results show that the algorithm performs well in Chinese fir forest stands of different age groups (average RMSE—horizontal: 4.27 cm; vertical: 3.86 cm) and achieves high accuracy in single-tree crown vertex detection and tree height estimation (average F-score: 0.90; R2 for tree height estimation: 0.88). This study demonstrates that the NDT-VGICP algorithm can effectively fuse and collaboratively apply multi-platform LiDAR data, providing a methodological reference for accurately quantifying individual tree parameters and efficiently monitoring 3D forest stand structures. Full article
(This article belongs to the Section Forest Inventory, Modeling and Remote Sensing)
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Figure 1
<p>Location of the study area: (<b>a</b>) Fujian Province of China; (<b>b</b>) Nanping City; (<b>c</b>) topographic map of Shunchang County; (<b>d</b>) aerial view of site distribution; (<b>e</b>) UAV-LiDAR, LiDAR-SLAM, and ground data survey.</p>
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<p>Stand conditions for (<b>a</b>) young-growth forests; (<b>b</b>) half-mature forests; (<b>c</b>) near-mature forests; (<b>d</b>) mature forests; and (<b>e</b>) over-mature forests.</p>
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<p>Technical flowchart.</p>
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<p>NDT coarse registration algorithm flowchart.</p>
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<p>Schematic of VGICP precision registration algorithm. (<b>a</b>) construct of the voxel grid; (<b>b</b>) downsampled of source and target point cloud; (<b>c</b>) calculation of voxel normal vectors; (<b>d</b>) construct point-voxel transformation field. The blue points in (<b>a</b>,<b>b</b>) are the original point clouds and the red points are the target point clouds. The red point in (<b>c</b>) is the nearest neighbor point cloud, the black point is the edge point cloud, and the yellow line is the voxel normal. The colored points in (<b>d</b>) are the matched point clouds.</p>
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<p>The technical workflow of the improved individual tree segmentation method combining the rasterized canopy height model (CHM) and point cloud clustering.</p>
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<p>Single wood segmentation process based on horizontal distance and edge distance. (<b>a</b>–<b>c</b>) represent the point cloud data extracted from the study object using rolling segmentation blocks.</p>
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<p>The registration effects of three algorithms on Chinese fir plantations across different age groups: (<b>a</b>) young-growth forests; (<b>b</b>) middle-aged forests; (<b>c</b>) near-mature forests; (<b>d</b>) mature forests; (<b>e</b>) over-mature forests. Taking plots Y-1, H-3, N-1, M-2, and O-1 as examples. Different colors represent point cloud datasets from two different platforms.</p>
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<p>The registration effects of three algorithms on individual Chinese fir trees of different age groups: (<b>a</b>) young-growth forests; (<b>b</b>) middle-aged forests; (<b>c</b>) near-mature forests; (<b>d</b>) mature forests; (<b>e</b>) vver-mature forests. Taking plots Y-1, H-3, N-1, M-2, and O-1 as examples. The white points represent the registered UAV-LiDAR data, and the color-rendered points represent the LiDAR-SLAM data. The white frame show the specific positions of the three slice angles of the local field of view.</p>
Full article ">Figure 9 Cont.
<p>The registration effects of three algorithms on individual Chinese fir trees of different age groups: (<b>a</b>) young-growth forests; (<b>b</b>) middle-aged forests; (<b>c</b>) near-mature forests; (<b>d</b>) mature forests; (<b>e</b>) vver-mature forests. Taking plots Y-1, H-3, N-1, M-2, and O-1 as examples. The white points represent the registered UAV-LiDAR data, and the color-rendered points represent the LiDAR-SLAM data. The white frame show the specific positions of the three slice angles of the local field of view.</p>
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<p>Differential analysis of individual tree crown delineation apex detection based on three registration algorithms. (<b>a</b>) NDT-ICP algorithms; (<b>b</b>) NDT-GICP algorithms; (<b>c</b>) NDT-VGICP algorithms.</p>
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<p>Differential analysis of individual tree crown delineation apex detection based on three registration algorithms. (<b>a</b>) NDT-ICP algorithms; (<b>b</b>) NDT-GICP algorithms; (<b>c</b>) NDT-VGICP algorithms.</p>
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<p>Main effects of age groups and three registration algorithms on the ITCD-F score and tree height RMSE using Tukey’s test. Panels (<b>a</b>,<b>b</b>) show the main effects of age groups and registration algorithms on the ITCD-F score, while panels (<b>c</b>,<b>d</b>) show the main effects on tree height RMSE. In panels (<b>a</b>,<b>c</b>), different colored boxes represent different age groups; in panels (<b>b</b>,<b>d</b>), different colored boxes represent different registration algorithms.</p>
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<p>Comparison of the optimized registration algorithm and the traditional algorithm across different age groups. (<b>a</b>) NDT-ICP algorithms; (<b>b</b>) NDT-GICP algorithms; (<b>c</b>) NDT-VGICP algorithms. “Y” represents young-growth forests; “H” represents half-mature forests; “N” represents near-mature forests; “M” represents mature forests; and “O” represents over-mature forests. The different colored columns in the figure represent different age groups.</p>
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<p>Accuracy evaluation of remote sensing-derived tree height at individual tree and stand scales. (<b>a</b>) Fitting results of remote sensing-derived tree height at the individual tree level and field-measured tree height; (<b>b</b>) Fitting results of remote sensing-derived stand average tree height and field-measured average tree height.</p>
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<p>Accuracy evaluation of remote sensing-derived tree height for different age groups: (<b>a</b>) young-growth forests; (<b>b</b>) middle-aged forests; (<b>c</b>) near-mature forests; (<b>d</b>) mature forests; (<b>e</b>) over-mature forests.</p>
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<p>Accuracy evaluation of remote sensing-derived tree height for different age groups: (<b>a</b>) young-growth forests; (<b>b</b>) middle-aged forests; (<b>c</b>) near-mature forests; (<b>d</b>) mature forests; (<b>e</b>) over-mature forests.</p>
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23 pages, 7403 KiB  
Article
Integrating Drone-Based LiDAR and Multispectral Data for Tree Monitoring
by Beatrice Savinelli, Giulia Tagliabue, Luigi Vignali, Roberto Garzonio, Rodolfo Gentili, Cinzia Panigada and Micol Rossini
Drones 2024, 8(12), 744; https://doi.org/10.3390/drones8120744 - 10 Dec 2024
Viewed by 426
Abstract
Forests are critical for providing ecosystem services and contributing to human well-being, but their health and extent are threatened by climate change, requiring effective monitoring systems. Traditional field-based methods are often labour-intensive, costly, and logistically challenging, limiting their use for large-scale applications. Drones [...] Read more.
Forests are critical for providing ecosystem services and contributing to human well-being, but their health and extent are threatened by climate change, requiring effective monitoring systems. Traditional field-based methods are often labour-intensive, costly, and logistically challenging, limiting their use for large-scale applications. Drones offer advantages such as low operating costs, versatility, and rapid data collection. However, challenges remain in optimising data processing and methods to effectively integrate the acquired data for forest monitoring. This study addresses this challenge by integrating drone-based LiDAR and multispectral data for forest species classification and health monitoring. We developed the methodology in Ticino Park (Italy), where intensive field campaigns were conducted in 2022 to collect tree species compositions, the leaf area index (LAI), canopy chlorophyll content (CCC), and drone data. Individual trees were first extracted from LiDAR data and classified using spectral and textural features derived from the multispectral data, achieving an accuracy of 84%. Key forest traits were then retrieved from the multispectral data using machine learning regression algorithms, which showed satisfactory performance in estimating the LAI (R2 = 0.83, RMSE = 0.44 m2 m−2) and CCC (R2 = 0.80, RMSE = 0.33 g m−2). The retrieved traits were used to track species-specific changes related to drought. The results obtained highlight the potential of integrating drone-based LiDAR and multispectral data for cost-effective and accurate forest health monitoring and change detection. Full article
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<p>(<b>a</b>) RGB image of the “La Fagiana” nature reserve. The red dots indicate the centre of the sites (15 m × 15 m) where the plant traits were sampled, and the yellow dots are the centre of the validation sites (30 m × 30 m) for the individual tree detection. The shaded areas indicate the three main forest areas classified according to the microclimatic condition of the forest: meso-hygrophilic (green), mesophilic (yellow), and xerophilic (red). The Google satellite image of the area in grey scale is used as the basemap. (<b>b</b>) The extension of Ticino Park in Northern Italy (green polygon) and the location of the Fagiana area (red polygon).</p>
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<p>Illustration of the LiDAR data processing workflow. DTM = digital terrain model; ITD = individual tree detection.</p>
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<p>(<b>a</b>) Hyperspectral reflectance spectra collected by the PRISMA satellite in correspondence of the sampling sites where the field data were collected (n = 50); (<b>b</b>) PRISMA spectra resampled to the MAIA S2 spectral bands and used for the training of the machine learning regression algorithms (n = 50).</p>
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<p>Drone-based classification of the tree species in the Fagiana Forest obtained from the MAIA S2 multispectral sensor using a random forest classifier. The Google satellite image of the area in grey scale is used as the basemap.</p>
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<p>Scatter plots showing the measured and estimated leaf area index (LAI) values obtained from the MAIA S2 sensor with different machine learning regression algorithms: (<b>a</b>) Gaussian processes regression (GPR); (<b>b</b>) support vector regression (SVR); (<b>c</b>) partial least squares regression (PLSR); (<b>d</b>) neural network (NN); and (<b>e</b>) random forest (RF). The grey shaded areas indicate the confidence intervals (0.95) of the regression lines (solid lines) using reduced major axis (RMA) regression. The dotted line represents the 1:1 line.</p>
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<p>Scatter plots showing the measured and estimated canopy chlorophyll content (CCC) values obtained from the MAIA S2 sensor with different machine learning regression algorithms: (<b>a</b>) Gaussian processes regression (GPR); (<b>b</b>) support vector regression (SVR); (<b>c</b>) partial least squares regression (PLSR); (<b>d</b>) neural network (NN); and (<b>e</b>) random forest (RF). The grey shaded areas indicate the confidence intervals (0.95) of the regression lines (solid lines) using reduced major axis (RMA) regression. The dotted line represents the 1:1 line.</p>
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<p>Drone-based maps obtained from the MAIA S2 sensor using machine learning regression algorithms: (<b>a</b>,<b>b</b>) maps of the leaf area index (LAI) and canopy chlorophyll content (CCC) obtained from drone images collected on 1 July 2022; (<b>c</b>,<b>d</b>) maps of the LAI and CCC obtained from drone images collected on 31 August 2022; and (<b>e</b>,<b>f</b>) maps of the delta LAI and CCC obtained as the difference between the LAI and CCC values retrieved from the drone images collected on 31 August 2022 and 1 July 2022.</p>
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<p>Boxplot of LAI against retrieval day (<b>a</b>) and forest microclimatic conditions (<b>b</b>). Different lowercase letters indicate statistically significant differences, while equal lowercase letters indicate no statistically significant difference.</p>
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<p>Boxplot of the CCC against retrieval day (<b>a</b>) and forest type (<b>b</b>). Different lowercase letters indicate statistical differences, while equal lowercase letters indicate no statistical difference.</p>
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22 pages, 3069 KiB  
Article
Stable Diversity but Distinct Metabolic Activity of Microbiome of Roots from Adult and Young Chinese Fir Trees
by Qingao Wang, Zhanling Wang, Wenjun Du, Yuxin Liu, Liang Hong, Pengfei Wu, Xiangqing Ma and Kai Wang
Forests 2024, 15(12), 2140; https://doi.org/10.3390/f15122140 - 4 Dec 2024
Viewed by 446
Abstract
The tree-associated microbiome is vital for both individual trees and the forest ecosystem. The microbiome is dynamic; however, it is influenced by the developmental stages and environmental stresses experienced by host trees. Chinese fir (Cunninghamia lanceolata) is an economically important tree [...] Read more.
The tree-associated microbiome is vital for both individual trees and the forest ecosystem. The microbiome is dynamic; however, it is influenced by the developmental stages and environmental stresses experienced by host trees. Chinese fir (Cunninghamia lanceolata) is an economically important tree species in the subtropical regions of China. This study investigated the diversity of microbial communities, including bacteria and fungi, in the roots and bulk soil of young (2 years old) and old (46 years old) Chinese fir. It specifically examined the functional characteristics of these microbial communities. Through a non-metric multidimensional scaling (NMDS) analysis, we examined differences in microbial community structures among root and soil samples of Chinese fir. Evaluations using α-diversity metrics (Chao1, Shannon, Pielou, etc.) confirmed significant differences in diversity and structure between soil and root samples but high similarity between young and old tree samples. A network analysis identified key bacterial and fungal genera, such as Burkholderia and Russula, which play pivotal roles in the microbiome structure. We also demonstrated significant variations in microbial metabolic functions, such as dioxin and benzoic acid degradation metabolic pathways, which might relate to stress alleviation for tree fitness. Additionally, for the detection of endophytic microorganisms in Chinese fir seeds, only small amounts (less than 10%) of fungal endophytes and bare bacterial endophytes were identified. In summary, this study revealed that the stable structure of the rhizosphere microbiome was established in the early stage of tree life in Chinese fir, which mostly originated from surrounding soil rather than seed endophytes. The associated microbial metabolic activity naturally decreased with tree aging, implicating the tree microbial dynamics and the need for the addition of an actively functional synthetic community for tree fitness. Full article
(This article belongs to the Section Forest Biodiversity)
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<p>Sample collection, NMDS analysis, and relative abundance of bacteriome and mycobiome from below-ground tissues of Chinese fir for young and old trees. (<b>A</b>) Sampling sites for old and young trees. (<b>B</b>) NMDS (non-metric multidimensional scaling) analysis of bacterial and fungal β-diversity of all samples, NMDS stress = 0.077/0.000. (<b>C</b>) Relative abundance of bacterial and fungal genera of all samples from amplicon analysis. O-Soil: Non-rhizosphere soil of old trees. Y-Soil: Non-rhizosphere soil of young trees. Y-Root: Root of young trees. O-Root: Root of old trees.</p>
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<p>Venn diagrams of OTU and genus grouping of bacterial and fungal biota. O-Soil: Non-rhizosphere soil of old trees. Y-Soil: Non-rhizosphere soil of young trees. Y-Root: Root of young trees. O-Root: Root of old trees.</p>
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<p>The indices of the α-diversity of bacterial and fungal communities in four different groups of samples. Tukey’s Honestly Significant Difference (HSD) test was implemented to calculate the difference among indices. (<b>A</b>) Diversity analysis of bacterial communities in non-rhizosphere soil and root samples, including Y-Soil (non-rhizosphere soil of young trees), O-Soil (non-rhizosphere soil of old trees), Y-Root (root of young trees), and O-Root (root of old trees). (<b>B</b>) Diversity analysis of fungal communities in the same sample groups. O-Soil: Non-rhizosphere soil of old trees. Y-Soil: Non-rhizosphere soil of young trees. Y-Root: Root of young trees. O-Root: Root of old trees. Different letter on top of bars indicate significant difference.</p>
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<p>A pairwise comparison of the metabolic activity of bacterial functions. Function prediction of the ITS amplicon was performed using PICRUSt 2.1.4. Welch’s <span class="html-italic">t</span>-test was applied to the pairwise comparison of metabolic activity from the KEGG database (level 3). Functional predictions of microbial communities based on KEGG pathway analysis. (<b>A</b>) Predicted pathways of bacterial communities in O-Root and Y-Root. (<b>B</b>) Predicted pathways of bacterial communities in Y-Root and Y-Soil. (<b>C</b>) Predicted pathways of bacterial communities in O-Root and O-Soil. The bar plots show the mean abundance of KEGG pathways, while the dot plots show differences in mean abundance with 95% confidence intervals. Pathways with significant differences (<span class="html-italic">p</span> &lt; 0.05) are highlighted. O-Soil: Non-rhizosphere soil of old trees. Y-Soil: Non-rhizosphere soil of young trees. Y-Root: Root of young trees. O-Root: Root of old trees.</p>
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<p>The relative abundance of the predicted functions of fungal communities. Function prediction of the ITS amplicon was performed using PICRUSt 2.1.4, with the top 10 abundance shown. The predicted functions involved aromatic biogenic amine degradation, glyoxylate cycle, GDP-mannose biosynthesis, and tRNA charging among four different group of samples. O-Soil: Non-rhizosphere soil of old trees. Y-Soil: Non-rhizosphere soil of young trees. Y-Root: Root of young trees. O-Root: Root of old trees.</p>
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<p>Genus-level abundance correlations of different (<b>A</b>) bacteria and (<b>B</b>) fungi within four different groups of samples. The area of the circular pattern indicates the abundance of the genus in the sample. Red lines indicate positive effects, and blue lines indicate negative effects. Names of the keystone genus were in bold.</p>
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<p>The number of observed species with the increase in tags of (<b>A</b>) fungi and (<b>B</b>) bacteria in Chinese fir seeds and four below ground groups. O-Soil: Non-rhizosphere soil of old trees. Y-Soil: Non-rhizosphere soil of young trees. Y-Root: Root of young trees. O-Root: Root of old trees. The information of the seed was highlighted in red and thick lines.</p>
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25 pages, 8832 KiB  
Article
3D-CNN with Multi-Scale Fusion for Tree Crown Segmentation and Species Classification
by Jiayao Wang, Zhen Zhen, Yuting Zhao, Ye Ma and Yinghui Zhao
Remote Sens. 2024, 16(23), 4544; https://doi.org/10.3390/rs16234544 - 4 Dec 2024
Viewed by 426
Abstract
Natural secondary forests play a crucial role in global ecological security, climate change mitigation, and biodiversity conservation. However, accurately delineating individual tree crowns and identifying tree species in dense natural secondary forests remains a challenge. This study combines deep learning with traditional image [...] Read more.
Natural secondary forests play a crucial role in global ecological security, climate change mitigation, and biodiversity conservation. However, accurately delineating individual tree crowns and identifying tree species in dense natural secondary forests remains a challenge. This study combines deep learning with traditional image segmentation methods to improve individual tree crown detection and species classification. The approach utilizes hyperspectral, unmanned aerial vehicle laser scanning data, and ground survey data from Maoershan Forest Farm in Heilongjiang Province, China. The study consists of two main processes: (1) combining semantic segmentation algorithms (U-Net and Deeplab V3 Plus) with watershed transform (WTS) for tree crown detection (U-WTS and D-WTS algorithms); (2) resampling the original images to different pixel densities (16 × 16, 32 × 32, and 64 × 64 pixels) and inputting them into five 3D-CNN models (ResNet10, ResNet18, ResNet34, ResNet50, VGG16). For tree species classification, the MSFB combined with the CNN models were used. The results show that the U-WTS algorithm achieved a recall of 0.809, precision of 0.885, and an F-score of 0.845. ResNet18 with a pixel density of 64 × 64 pixels achieved the highest overall accuracy (OA) of 0.916, an improvement of 0.049 over the original images. After incorporating MSFB, the OA improved by approximately 0.04 across all models, with only a 6% increase in model parameters. Notably, the floating-point operations (FLOPs) of ResNet18 + MSFB were only one-eighth of those of ResNet18 with 64 × 64 pixels, while achieving similar accuracy (OA: 0.912 vs. 0.916). This framework offers a scalable solution for large-scale tree species distribution mapping and forest resource inventories. Full article
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<p>Overview map of the study area: (<b>a</b>) location of Heilongjiang Province in a map of the administrative areas of China; (<b>b</b>) aerial view of Maoershan Experimental Forest Farm, the numbered areas numbered 1, 2, 3, 4, and 5 are drone flight zones.; aerial views of unmanned aerial vehicle (UAV) flight area Nos. 4 (<b>c</b>) and 5 (<b>d</b>); and aerial photos of (<b>e</b>) mixed coniferous–broadleaf forest and (<b>f</b>) mixed broadleaf forest.</p>
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<p>Flowchart of the research process. Note: CHM, canopy height model; GLCM, gray level co-occurrence matrix; RFE, recursive feature elimination; WST, watershed transform.</p>
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<p>Flowchart of the U-net + watershed transform algorithm.</p>
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<p>Mean spectral reflectance curves of seven tree species groups: birch, elm, Korean pine, Manchurian ash, Manchurian walnut, other coniferous trees, and other broadleaf trees.</p>
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<p>Relationship between tree crown images of different pixel densities and feature map sizes obtained by the convolutional neural network model; the original images were resampled to different pixel densities: (<b>a</b>) 8 × 8 pixels, (<b>b</b>) 16 × 16 pixels, (<b>c</b>) 32 × 32 pixels, and (<b>d</b>) 64 × 64 pixels.</p>
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<p>Schematic of the ResNet18 model + multi-scale fusion branch module (MSFB) structure. Note: C, channel; D, depth; W, width; and H, height.</p>
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<p>Individual tree crown delineation results of three algorithms with a 15 × 15 m plot: (<b>a</b>) the reference tree crown; the results of the (<b>b</b>) U-WST, (<b>c</b>) D-WST, and (<b>d</b>) WST algorithms. Note: CHM, canopy height model.</p>
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<p>Recursive feature elimination and feature importance ranking based on random forest model.</p>
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<p>Confusion matrix of the ResNet18 model at four pixel densities: (<b>a</b>) 8 × 8 pixels, (<b>b</b>) 16 × 16 pixels, (<b>c</b>) 32 × 32 pixels, and (<b>d</b>) 64 × 64 pixels. Note: PA represents Producer’s Accuracy, UA represents User’s Accuracy, KP represents Korean pine, BR represents birch, MA represents Manchurian ash, MW represents Manchurian walnut, OC represents Other coniferous trees, OB represents Other broad-leaved trees, the intensity of the color represents the magnitude of the value.</p>
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<p>Maps of the distribution of tree species groups in part of unmanned aerial vehicle (UAV) flight region No. 4: (<b>a</b>) UAV flight region No. 4 with a background of hyperspectral images, (<b>b</b>) enlarged view of a local area, and (<b>c</b>) map of tree species prediction results.</p>
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<p>Spatial importance and feature importance based on the Shapley Additive exPlanations (SHAP) method: (<b>a</b>) tree crown segmentation; (<b>b</b>) tree species classification; (<b>c</b>) a stack of 40 channels of the original image; (<b>d</b>) a stack of 40 channels after using the SHAP method; (<b>e</b>) SHAP feature importance based on seven tree species groups.</p>
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<p>Performance of the U-WST algorithm in identifying tree canopies in mixed broadleaf forests. Note: CHM, canopy height model.</p>
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19 pages, 6073 KiB  
Article
Effective UAV Photogrammetry for Forest Management: New Insights on Side Overlap and Flight Parameters
by Atman Dhruva, Robin J. L. Hartley, Todd A. N. Redpath, Honey Jane C. Estarija, David Cajes and Peter D. Massam
Forests 2024, 15(12), 2135; https://doi.org/10.3390/f15122135 - 2 Dec 2024
Viewed by 843
Abstract
Silvicultural operations such as planting, pruning, and thinning are vital for the forest value chain, requiring efficient monitoring to prevent value loss. While effective, traditional field plots are time-consuming, costly, spatially limited, and rely on assumptions that they adequately represent a wider area. [...] Read more.
Silvicultural operations such as planting, pruning, and thinning are vital for the forest value chain, requiring efficient monitoring to prevent value loss. While effective, traditional field plots are time-consuming, costly, spatially limited, and rely on assumptions that they adequately represent a wider area. Alternatively, unmanned aerial vehicles (UAVs) can cover large areas while keeping operators safe from hazards including steep terrain. Despite their utility, optimal flight parameters to ensure flight efficiency and data quality remain under-researched. This study evaluated the impact of forward and side overlap and flight altitude on the quality of two- and three-dimensional spatial data products from UAV photogrammetry (UAV-SfM) for assessing stand density in a recently thinned Pinus radiata D. Don plantation. A contemporaneously acquired UAV laser scanner (ULS) point cloud provided reference data. The results indicate that the optimal UAV-SfM flight parameters are 90% forward and 85% side overlap at a 120 m altitude. Flights at an 80 m altitude offered marginal resolution improvement (2.2 cm compared to 3.2 cm ground sample distance/GSD) but took longer and were more error-prone. Individual tree detection (ITD) for stand density assessment was then applied to both UAV-SfM and ULS canopy height models (CHMs). Manual cleaning of the detected ULS tree peaks provided ground truth for both methods. UAV-SfM had a lower recall (0.85 vs. 0.94) but a higher precision (0.97 vs. 0.95) compared to ULS. Overall, the F-score indicated no significant difference between a prosumer-grade photogrammetric UAV and an industrial-grade ULS for stand density assessments, demonstrating the efficacy of affordable, off-the-shelf UAV technology for forest managers. Furthermore, in addressing the knowledge gap regarding optimal UAV flight parameters for conducting operational forestry assessments, this study provides valuable insights into the importance of side overlap for orthomosaic quality in forest environments. Full article
(This article belongs to the Special Issue Image Processing for Forest Characterization)
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Graphical abstract

Graphical abstract
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<p>Location of the study site within NZ (insert), with the optimal orthomosaic overlaid on a mixed topographic/aerial image of the region. The stand boundary is indicated by the purple line, GCP locations are in orange, and the take-off location is in cyan.</p>
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<p>Image of a GCP coated with reflective material and painted in a high contrast pattern for identification in the ULS and UAV-SfM datasets.</p>
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<p>Images of the UAVs utilised in this study: (<b>a</b>) the DJI Phantom 4 Pro; (<b>b</b>) the DJI Matrice 300 RTK with a DJI L1 sensor. (<b>c</b>) Shows the flight crew operating UAVs from an MEWP to maintain VLOS.</p>
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<p>Examples of image artefacts encountered when annotating the orthomosaics: (<b>a</b>,<b>d</b>,<b>e</b>) “blurring” and “smudging” effects; (<b>b</b>,<b>d</b>) “tearing” or “breaking” discontinuities within the image; (<b>c</b>,<b>e</b>) “ghosting”, in which the displacement of ground and canopy pixels results in transparent tree canopies; (<b>d</b>,<b>f</b>) in some areas tree canopies were fragmented into smaller chunks.</p>
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<p>Bar graph plotting the percentage area of each orthomosaic free from artefacts for each flight plan, coloured by altitude. The missions are arranged by overlap with the lowest on the left and highest on the right.</p>
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<p>Comparison of flight time duration between different overlap flight missions, coloured by altitude.</p>
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<p>Correlations between (<b>a</b>) forward overlap and (<b>b</b>) side overlap with the area of each orthomosaic that was clear of artefacts. The teal line represents the linear model between variables, and point locations are jittered so that multiple points with the same value are visible.</p>
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<p>Calculated relief displacement for an object (e.g., a tree) of height (<span class="html-italic">h</span>) 20 m, within imagery captured at a flying height (<span class="html-italic">H</span>) of 80 m (purple vectors) or 120 m (yellow vectors) above ground level. The displacement vectors in the legend are scaled to an image distance of 100 mm. Relief displacement vectors are plotted on an image captured at ~80 m AGL and at image radial distances of 0, 100, 200, 300, 400, 500, 650, and 900 mm from the principal point, which for this illustration is assumed to coincide with the image centre.</p>
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<p>Demonstration of the greater impact of side (dashed purple line) than forward (dotted green line) overlap on movement of the near-nadir viewing region of an image (solid teal line). Movement values are based on P4 Pro camera at a height of 120 m, with an image footprint of 180 × 120 m.</p>
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<p>The effects of shadow and occlusions in the orthomosaics produced by flights flown at overlap of 90:85 at 80 m (<b>a</b>) and 90:90 at 80 m (<b>b</b>).</p>
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12 pages, 3229 KiB  
Article
Genomic Differences and Mutations in Epidemic Orf Virus and Vaccine Strains: Implications for Improving Orf Virus Vaccines
by Dengshuai Zhao, Yaoxu Shi, Miaomiao Zhang, Ping Li, Yuanhang Zhang, Tianyu Wang, Dixi Yu and Keshan Zhang
Vet. Sci. 2024, 11(12), 617; https://doi.org/10.3390/vetsci11120617 - 2 Dec 2024
Viewed by 513
Abstract
Orf (ORF) is an acute disease caused by the Orf virus (ORFV), and poses a certain threat to animal and human health. Live attenuated vaccines play an important role in the prevention and control of ORF. The effectiveness of the live attenuated Orf [...] Read more.
Orf (ORF) is an acute disease caused by the Orf virus (ORFV), and poses a certain threat to animal and human health. Live attenuated vaccines play an important role in the prevention and control of ORF. The effectiveness of the live attenuated Orf virus vaccine is influenced by several factors, including the genomic match between the vaccine strain and circulating epidemic strains. Genomic differences between an ORFV epidemic strain (ORFV-2W) and a vaccine strain (ORFV-1V) were identified in this study via analysis of multiple sequence alignments, phylogenetic trees, and single nucleotide polymorphisms. Phylogenetic analysis revealed that ORFV-2W and ORFV-1V were closely related, with a whole genome homology of 99.8%. Furthermore, a deletion in the non-coding region at the end of the whole genome of ORFV-1V was detected. Such non-essential genes in the terminal regions are usually unnecessary for virus replication but may play important roles in pathogenicity, host and tissue tropism. Single nucleotide polymorphism analysis identified three missense mutations in ORF067, ORF072, and the terminal non-coding region of ORFV-1V. Moreover, a frameshift mutation in ORF102 of ORFV-1V was detected. Mutations in individual genes and deletion of terminal non-coding regions may be related to the attenuation of the vaccine strain. These results provide useful context for improving ORFV vaccines. Full article
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<p>Whole genome maps of ORFV-1V and ORFV-2W. (<b>A</b>) Whole genome map of ORFV-1V. (<b>B</b>) Whole genome map of ORFV-2W.</p>
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<p>Whole genome nucleotide sequence alignment analysis. The deleted region of ORFV-1V is represented by the red box.</p>
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<p>Alignment of ITR sequences from the ORFV-1V and ORFV-2W genomes with those from other isolates. The left terminal 5’-ITR sequences of eleven ORFV isolates were compared using MEGA version 11. The BamHI terminal region (GGATCC) and the telomere resolution sequence (ATT TTTT-N(8)-TAAAT) are indicated as yellow and blue boxes, respectively. The deletion region of ORFV-1V is indicated as a black box.</p>
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<p>Phylogenetic analysis based on two genes (i.e., ORF011 and ORF059) and whole genome sequence data. Phylogenetic trees were constructed using the neighbor-joining method in MEGA version 11. Numbers above or below branch points indicate the bootstrap support calculated for 1000 replicates. Shown are trees using sequence data for: (<b>A</b>) B2L (<span class="html-italic">ORF011</span>) and (<b>B</b>) F1L (<span class="html-italic">ORF059</span>). Here, ORFV-1V and ORFV-2W are represented by red triangles and red squares, respectively. Also shown is a tree using (<b>C</b>) whole genome sequence data. ORFV-1V and ORFV-2W are shown in red font.</p>
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<p>Alignment of amino acid sequences of <span class="html-italic">ORF067</span>, <span class="html-italic">ORF072</span>, and <span class="html-italic">ORF102</span>. The sequences of ORFV-1V and other isolates were aligned using MEGA version 11. (<b>A</b>) <span class="html-italic">ORF067</span>. (<b>B</b>) <span class="html-italic">ORF072</span>. (<b>C</b>) <span class="html-italic">ORF102</span>. ORFV-1V is highlighted with a red box for emphasis. Amino acid mutation sites are represented by yellow boxes.</p>
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<p>Prediction of the tertiary structures of proteins encoded by <span class="html-italic">ORF067</span>, <span class="html-italic">ORF072</span>, and <span class="html-italic">ORF102</span> of the ORFV-1V and ORFV-2W genomes. Tertiary protein structures were predicted using SWISS-MODEL. The template coverage of each of the above proteins is &gt;50%, and all GMQE &gt; 0.2, which indicates that the prediction results are reliable. (<b>A</b>) ORFV-1V <span class="html-italic">ORF067</span>. (<b>B</b>) ORFV-2W <span class="html-italic">ORF067</span>. (<b>C</b>) ORFV-1V <span class="html-italic">ORF072</span>. (<b>D</b>) ORFV-2W <span class="html-italic">ORF072</span>. (<b>E</b>) ORFV-1V <span class="html-italic">ORF102</span>. (<b>F</b>) ORFV-2W <span class="html-italic">ORF102</span>. Amino acid sites are indicated by black arrows. D196H indicates the mutation of amino acid 196 from aspartic acid (Asp) to histidine (His). I113V shows the mutation of isoleucine (Ile) to valine (Val) at position 113. N148 shows the mutation of amino acid 148 to asparagine (Asn).</p>
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14 pages, 5943 KiB  
Article
Comparative Analysis of Force-Sensitive Resistors and Triaxial Accelerometers for Sitting Posture Classification
by Zhuofu Liu, Zihao Shu, Vincenzo Cascioli and Peter W. McCarthy
Sensors 2024, 24(23), 7705; https://doi.org/10.3390/s24237705 - 2 Dec 2024
Viewed by 394
Abstract
Sedentary behaviors, including poor postures, are significantly detrimental to health, particularly for individuals losing motion ability. This study presents a posture detection system utilizing four force-sensitive resistors (FSRs) and two triaxial accelerometers selected after rigorous assessment for consistency and linearity. We compared various [...] Read more.
Sedentary behaviors, including poor postures, are significantly detrimental to health, particularly for individuals losing motion ability. This study presents a posture detection system utilizing four force-sensitive resistors (FSRs) and two triaxial accelerometers selected after rigorous assessment for consistency and linearity. We compared various machine learning algorithms based on classification accuracy and computational efficiency. The k-nearest neighbor (KNN) algorithm demonstrated superior performance over Decision Tree, Discriminant Analysis, Naive Bayes, and Support Vector Machine (SVM). Further analysis of KNN hyperparameters revealed that the city block metric with K = 3 yielded optimal classification results. Triaxial accelerometers exhibited higher accuracy in both training (99.4%) and testing (99.0%) phases compared to FSRs (96.6% and 95.4%, respectively), with slightly reduced processing times (0.83 s vs. 0.85 s for training; 0.51 s vs. 0.54 s for testing). These findings suggest that, apart from being cost-effective and compact, triaxial accelerometers are more effective than FSRs for posture detection. Full article
(This article belongs to the Special Issue Advanced Sensing and Measurement Control Applications)
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<p>FSR performance verification using sandbags to simulate the loading force.</p>
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<p>Accelerometer evaluation test using a custom-made rotating device placed on the optical platform.</p>
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<p>Configuration of the sitting posture detection system consisting of four FSRs and two triaxial accelerometers (sensors have been labeled numerically and ACC refers to accelerometer).</p>
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<p>Normalized data from four FSR sensors (abbreviated by FSR1 to FSR4 in accordance with the numerical labels in <a href="#sensors-24-07705-f003" class="html-fig">Figure 3</a>) in response to the loading force simulated by sandbags, along with linear fitting functions (from y1 to y4) and corresponding correlation coefficients.</p>
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<p>Normalized accelerometer data collected during rotation from 0 to 180° around each of the three axes in 5° intervals. According to the numerical labels in <a href="#sensors-24-07705-f003" class="html-fig">Figure 3</a>, accX1 indicates the <span class="html-italic">x</span>-axis output of the first accelerometer, accX2 is the <span class="html-italic">x</span>-axis output of the second accelerometer, accY1 and accY2 correspond to <span class="html-italic">y</span>-axis outputs of the two accelerometers, and accZ1 and accZ2 are the <span class="html-italic">z</span>-axis outputs.</p>
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<p>Variations in the normalized readings of four FSRs and two accelerometers as a randomly selected participant transitions through a series of sitting postures: (<b>a</b>) vacant (<b>b</b>) sitting upright, (<b>c</b>) leaning left, (<b>d</b>) leaning right, (<b>e</b>) leaning forward, (<b>f</b>) leaning backward, (<b>g</b>) crossing the left leg, and (<b>h</b>) crossing the right leg.</p>
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<p>Illustration of the normalized curves of FSRs and accelerometers corresponding to different sitting postures and the maximum correlation coefficients between them. (<b>a</b>) Normalized curves of the FSRs. (<b>b</b>) Normalized curves of the accelerometers. (<b>c</b>) The maximum correlation coefficients between FSRs and accelerometers. FSR1 to FSR4 represent the four FSRs, while accX1 indicates the <span class="html-italic">x</span>-axis output of the first accelerometer, accX2 is the <span class="html-italic">x</span>-axis output of the second accelerometer, and accY1 and accY2 correspond to the <span class="html-italic">y</span>-axis outputs of the two accelerometers.</p>
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<p>Comparison of various hyperparameters (k-values and metric functions) for K-Nearest Neighbors (KNN). Classification results for FSRs: (<b>a</b>) training data results displayed and (<b>b</b>) testing data results. Classification results for the accelerometers, (<b>c</b>) training data results, and (<b>d</b>) testing data results. The ‘solid line’ represents results using the City Block metric, the ‘dashed line’ corresponds to the Euclidean metric, and the ‘dotted line’ indicates the Cubic metric. Blue is used to depict accuracy comparisons, while magenta represents running time.</p>
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<p>Comparison of various hyperparameters (k-values and metric functions) for K-Nearest Neighbors (KNN). Classification results for FSRs: (<b>a</b>) training data results displayed and (<b>b</b>) testing data results. Classification results for the accelerometers, (<b>c</b>) training data results, and (<b>d</b>) testing data results. The ‘solid line’ represents results using the City Block metric, the ‘dashed line’ corresponds to the Euclidean metric, and the ‘dotted line’ indicates the Cubic metric. Blue is used to depict accuracy comparisons, while magenta represents running time.</p>
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<p>Confusion matrix in which 0—vacant, 1—sitting upright, 2—leaning left, 3—leaning right, 4—leaning forward, 5—leaning backward, 6—fidgeting left leg, 7—fidgeting right leg, 8—crossing left leg, 9—crossing right leg. (<b>a</b>) FSR training data, (<b>b</b>) FSR testing data, (<b>c</b>) accelerometer training data, and (<b>d</b>) accelerometer testing data. For all the comparisons, hyperparameters of KNN are city block metric function and K = 3.</p>
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18 pages, 8779 KiB  
Article
Customized Weighted Ensemble of Modified Transfer Learning Models for the Detection of Sugarcane Leaf Diseases
by Kaiwen Hu, Honghui Li, Xueliang Fu and Shuncheng Zhou
Electronics 2024, 13(23), 4715; https://doi.org/10.3390/electronics13234715 - 28 Nov 2024
Viewed by 358
Abstract
Sugarcane is the primary crop in the global sugar industry, yet it remains highly susceptible to a wide range of diseases that significantly impact its yield and quality. An effective solution is required to address the issues caused by the manual identification of [...] Read more.
Sugarcane is the primary crop in the global sugar industry, yet it remains highly susceptible to a wide range of diseases that significantly impact its yield and quality. An effective solution is required to address the issues caused by the manual identification of plant diseases, which is time-consuming and has low detection accuracy. This paper proposes the development of a robust Deep Ensemble Convolutional Neural Network (DECNN) model for the accurate detection of sugarcane leaf diseases. Initially, several transfer learning (TL) models, including EfficientNetB0, MobileNetV2, DenseNet121, NASNetMobile, and EfficientNetV2B0, were enhanced through the addition of specific layers. A comparative analysis was then conducted on the enlarged dataset of sugarcane leaf diseases, which was divided into six categories and 4800 images. The application of data augmentation, along with the addition of dense layers, batch normalization layers, and dropout layers, led to improved detection accuracy, precision, recall, and F1 scores for each model. Among the five enhanced transfer learning models, the modified EfficientNetB0 model demonstrated the highest detection accuracy, ranging from 97.08% to 98.54%. In conclusion, the DECNN model was developed by integrating the modified EfficientNetB0, MobileNetV2, and DenseNet121 models using a distinctive performance-based custom-weighted ensemble method, with weight optimization carried out using the Tree-structured Parzen Estimator (TPE) technique. This resulted in a model that achieved a detection accuracy of 99.17%, which outperformed the individual performance of the modified EfficientNetB0, MobileNetV2, and DenseNet121 models in detecting sugarcane leaf diseases. Full article
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<p>Some examples of sugarcane diseases.</p>
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<p>Flow diagram of the proposed DECNN model.</p>
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<p>The concept of transfer learning.</p>
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<p>Proposed DECNN model.</p>
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<p>Accuracies of the modified models versus the number of epochs.</p>
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<p>ROC curves of modified TL models.</p>
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<p>Confusion matrices of the modified TL models.</p>
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<p>ROC curves and confusion matrix of proposed the DECNN model.</p>
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<p>Final predicted outputs.</p>
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11 pages, 2798 KiB  
Article
Genetic Diversity Analysis and Core Collection Construction of Ancient Sophora japonica L. Using SSR Markers
by Yinyin Fu, Shuangyun Li, Bingyao Ma, Cuilan Liu, Yukun Qi and Caihong Pang
Int. J. Mol. Sci. 2024, 25(23), 12776; https://doi.org/10.3390/ijms252312776 - 28 Nov 2024
Viewed by 319
Abstract
Sophora japonica is an important native tree species in northern China, with high ornamental, medicinal, and ecological value. In order to elucidate the genetic resources of ancient S. japonica, 16 simple sequence repeat (SSR) markers were used to evaluate its genetic diversity [...] Read more.
Sophora japonica is an important native tree species in northern China, with high ornamental, medicinal, and ecological value. In order to elucidate the genetic resources of ancient S. japonica, 16 simple sequence repeat (SSR) markers were used to evaluate its genetic diversity and population structure and build a core collection of 416 germplasms from the Shandong, Shanxi, and Hebei provinces. A total of 160 alleles were detected, the mean major allele frequency (MAF)was 0.39, and the mean effective number of alleles (Ne) was 4.08. Shannon’s information index (I), the observed heterozygosity (Ho), the expected heterozygosity (He), and the polymorphism information content (PIC) were 1.58, 0.64, 0.74, and 0.70, respectively, indicating relatively high genetic diversity in ancient S. japonica germplasms. Low genetic differentiation coefficient (Fst = 0.04) and frequent gene flow (Nm = 9.74) were found in the tested S. japonica populations, and an analysis of molecular variance (AMOVA) indicated that the genetic variation mainly came from within individuals (84%). A genetic structure and cluster analysis indicated that 416 ancient S. japonica germplasms could be divided into five subgroups, and there were obvious genetic exchanges among different subgroups. A core collection consisting of 104 (25% of the original collection) germplasms was constructed using the R language package Genetic Subsetter version 0.8 based on the stepwise regression method. The retention rates of the number of alleles (Na), Ne, I, He, and PIC were 87.50%, 106.24%, 103.02%, 102.50%, and 102.74%, respectively. The t-test analysis suggested that there were no significant differences between the core collection and the original collection. The principal coordinate analysis (PCoA) showed that the core collection was uniformly distributed within the initial collection and was able to fully represent the genetic diversity of the original collection. These results provide a scientific basis for the conservation and utilization of ancient S. japonica germplasms. Full article
(This article belongs to the Special Issue Functional Genomics of Energy Crops 2.0)
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<p>UPGMA clustering analysis of 416 ancient <span class="html-italic">S. japonica</span> germplasm resources.</p>
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<p>The optimal population number of <span class="html-italic">S</span>. <span class="html-italic">japonica</span> field populations detected using Structure software (K). (<b>A</b>) The average Lnp (D) value of each K value based on 10 repetitions; (<b>B</b>) the K value plot as it changed with ΔK.</p>
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<p>Population structure of 416 ancient <span class="html-italic">S. japonica</span> germplasms based on 16 SSR markers at k = 5.</p>
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<p>The principal coordinate distribution of the core collection and the original collection of ancient <span class="html-italic">S. japonica.</span></p>
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49 pages, 45431 KiB  
Article
Concepts Towards Nation-Wide Individual Tree Data and Virtual Forests
by Matti Hyyppä, Tuomas Turppa, Heikki Hyyti, Xiaowei Yu, Hannu Handolin, Antero Kukko, Juha Hyyppä and Juho-Pekka Virtanen
ISPRS Int. J. Geo-Inf. 2024, 13(12), 424; https://doi.org/10.3390/ijgi13120424 - 26 Nov 2024
Viewed by 1073
Abstract
Individual tree data could offer potential uses for both forestry and landscape visualization but has not yet been realized on a large scale. Relying on 5 points/m2 Finnish national laser scanning, we present the design and implementation of a system for producing, [...] Read more.
Individual tree data could offer potential uses for both forestry and landscape visualization but has not yet been realized on a large scale. Relying on 5 points/m2 Finnish national laser scanning, we present the design and implementation of a system for producing, storing, distributing, querying, and viewing individual tree data, both in a web browser and in a game engine-mediated interactive 3D visualization, “virtual forest”. In our experiment, 3896 km2 of airborne laser scanning point clouds were processed for individual tree detection, resulting in over 100 million trees detected, but the developed technical infrastructure allows for containing 10+ billion trees (a rough number of log-sized trees in Finland) to be visualized in the same system. About 92% of trees wider than 20 cm in diameter at breast height (corresponding to industrial log-size trees) were detected using national laser scanning data. Obtained relative RMSE for height, diameter, volume, and biomass (stored above-ground carbon) at individual tree levels were 4.5%, 16.9%, 30.2%, and 29.0%, respectively. The obtained RMSE and bias are low enough for operational forestry and add value over current area-based inventories. By combining the single-tree data with open GIS datasets, a 3D virtual forest was produced automatically. A comparison against georeferenced panoramic images was performed to assess the verisimilitude of the virtual scenes, with the best results obtained from sparse grown forests on sites with clear landmarks. Both the online viewer and 3D virtual forest can be used for improved decision-making in multifunctional forestry. Based on the work, individual tree inventory is expected to become operational in Finland in 2026 as part of the third national laser scanning program. Full article
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<p>The area for which the ITD was performed with coordinates for the corner points given in ETRS-TM35FIN. The location of the virtual forest test site (within the ITD area) is denoted as red dot. The utilized sample plots of the SCAN FOREST research infrastructure are located in the same area as the virtual forest test site, on an approx 5 by 5 km area. Background map © National Land Survey of Finland.</p>
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<p>The chosen test area, with dimensions of 1 by 1 km, with coordinates for the corner points given in ETRS-TM35FIN. Background map © National Land Survey of Finland.</p>
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<p>Overview of the software components applied.</p>
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<p>A pipeline for rendering raster map tiles into an image pyramid.</p>
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<p>The terrain area is divided into a grid of bounding boxes (white) that receive in scene initiation their individual tree counts from the server. The user’s (top left) current view is visualized by the frustum. The real time tree loading sequence has finalized the green outlined boxes while blue ones are currently being loaded and magenta ones wait in the stack.</p>
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<p>Found tree counts for both 2D and 3D methods as a function of DBH classes, compared to the reference.</p>
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<p>Relative bias (%) and relative RMSE (%) of attribute estimation as a function of DBH classes for trees over 20 cm in DBH, given for height (H), diameter (DBH), volume (V) and above ground biomass (AGB).</p>
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<p>Relative bias (%) and relative RMSE (%) of attribute estimation as a function of tree species for trees over 20 cm in DBH, given for height (H), diameter (DBH), volume (V), and above ground biomass (AGB).</p>
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<p>Individual trees drawn on the map with the following color codes: pine = brown, spruce = green and deciduous tree = yellow. The taller the tree, the darker the color of the circle marker. By clicking the tree, the most important characteristics of the tree, such as the species, height, diameter, volume, and biomass, are given in the info box.</p>
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<p>The user has selected a property on the map to query statistical data of the trees belonging to the property. The property has been selected by placing a blue marker on the map after which the boundaries of the selected property have become highlighted with blue color. The topographic map underneath the trees was obtained from the API of the National Land Survey of Finland. Individual trees drawn on the map with the following color codes: pine = brown, spruce = green and deciduous tree = yellow. The taller the tree, the darker the color of the circle marker.</p>
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<p>Dashboard visualizing the statistics of the trees from the selected area. Height and DBH histograms of the trees in the selected area are displayed on the right in addition to an estimation of the amount of carbon dioxide the trees have absorbed during their lifespan. Descriptive statistics for key attributes, such as mean diameter, total volume, biomass, basal area and the number of stems per hectare, have been presented on the left with tables in addition to an estimation of the value of the forest.</p>
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<p>User querying tree properties while filtering the virtual environment to show only trees less than 15 m tall.</p>
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<p>User querying tree properties while filtering the virtual environment to hide birches.</p>
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<p>Test site F on site (<b>left</b>) and as virtual scene (<b>right</b>). Correctly represented dominant trees almost begin to function as landmarks.</p>
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<p>Test site P on site (<b>left</b>) and as virtual scene (<b>right</b>). Absence of smaller trees in the virtual scene, species errors, and position errors of leaning trees lead to poor visual correspondence between the real and virtual forest. The waterbody and road however act as potential landmarks.</p>
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<p>Legend used in all comparison image pairs in this Appendix.</p>
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<p>Test site A, a mixed-species forest by the river flowing into a lake, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,786,021 E = 398,869.</p>
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<p>Test site B, an uneven-aged mixed-species forest around a ditch and a forest road, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,854 E = 398,919.</p>
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<p>Test site C, an open field in the middle of a mixed forest, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,778 E = 399,079.</p>
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<p>Test site D, a hilly full-grown spruce forest, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,759 E = 398,994.</p>
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<p>Test site E, a hilly pine forest growing also young spruces, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,700 E = 398,893.</p>
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<p>Test site F, a thinned pine forest, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,537 E = 398,805.</p>
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<p>Test site G, a full-grown spruce forest, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,617 E = 398,869.</p>
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<p>Test site H, a pine-forest next to an overflown lake, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,783 E = 399,513.</p>
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<p>Test site I, a stony hill in a pine forest, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,688 E = 399,538.</p>
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<p>Test site J, a young thinned spruce forest on a slope, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,686 E = 399,364.</p>
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<p>Test site K, a forest road going through a mixed species forest, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,579 E = 399,550.</p>
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<p>Test site L, large glacially deposited rocks on a pine forest, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,523 E = 399,537.</p>
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<p>Test site M, an opening in a dense young spruce forest, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,548 E = 399,603.</p>
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<p>Test site N, an old abandoned field surrounded by mixed-species forests, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,416 E = 399,275.</p>
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<p>Test site O, a paved road running between overflowing lakes with dead trees, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,774 E = 399,163.</p>
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<p>Test site P, a river bank with a forest road and mixed species forest, showing the virtual scene (<b>top</b>) and on-site image (<b>bottom</b>). GNSS Position (TM-GK35FIN): N = 6,785,883 E = 398,913.</p>
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15 pages, 6614 KiB  
Article
Advancing Forest Plot Surveys: A Comparative Study of Visual vs. LiDAR SLAM Technologies
by Tianshuo Guan, Yuchen Shen, Yuankai Wang, Peidong Zhang, Rui Wang and Fei Yan
Forests 2024, 15(12), 2083; https://doi.org/10.3390/f15122083 - 26 Nov 2024
Viewed by 523
Abstract
Forest plot surveys are vital for monitoring forest resource growth, contributing to their sustainable development. The accuracy and efficiency of these surveys are paramount, making technological advancements such as Simultaneous Localization and Mapping (SLAM) crucial. This study investigates the application of SLAM technology, [...] Read more.
Forest plot surveys are vital for monitoring forest resource growth, contributing to their sustainable development. The accuracy and efficiency of these surveys are paramount, making technological advancements such as Simultaneous Localization and Mapping (SLAM) crucial. This study investigates the application of SLAM technology, utilizing LiDAR (Light Detection and Ranging) and monocular cameras, to enhance forestry plot surveys. Conducted in three 32 × 32 m plots within the Tibet Autonomous Region of China, the research compares the efficacy of LiDAR-based and visual SLAM algorithms in estimating tree parameters such as diameter at breast height (DBH), tree height, and position, alongside their adaptability to forest environments. The findings revealed that both types of algorithms achieved high precision in DBH estimation, with LiDAR SLAM presenting a root mean square error (RMSE) range of 1.4 to 1.96 cm and visual SLAM showing a slightly higher precision, with an RMSE of 0.72 to 0.85 cm. In terms of tree position accuracy, the three methods can achieve tree location measurements. LiDAR SLAM accurately represents the relative positions of trees, while the traditional and visual SLAM systems exhibit slight positional offsets for individual trees. However, discrepancies arose in tree height estimation accuracy, where visual SLAM exhibited a bias range from −0.55 to 0.19 m and an RMSE of 1.36 to 2.34 m, while LiDAR SLAM had a broader bias range and higher RMSE, especially for trees over 25 m, attributed to scanning angle limitations and branch occlusion. Moreover, the study highlights the comprehensive point cloud data generated by LiDAR SLAM, useful for calculating extensive tree parameters such as volume and carbon storage and Tree Information Modeling (TIM) through digital twin technology. In contrast, the sparser data from visual SLAM limits its use to basic parameter estimation. These insights underscore the effectiveness and precision of SLAM-based approaches in forestry plot surveys while also indicating distinct advantages and suitability of each method to different forest environments. The findings advocate for tailored survey strategies, aligning with specific forest conditions and requirements, enhancing the application of SLAM technology in forestry management and conservation efforts. Full article
(This article belongs to the Special Issue Integrated Measurements for Precision Forestry)
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<p>Study area.</p>
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<p>Handheld laser scanning device.</p>
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<p>The measurement process of the LiDAR SLAM method.</p>
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<p>Visual SLAM tree measurement system.</p>
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<p>The measurement process of the visual SLAM tree measurement system.</p>
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<p>Reference measurement tools for plot data. (<b>a</b>) is the diameter at breast height (DBH) tape; (<b>b</b>) is ultrasonic tree height and range finder (Vertex III).</p>
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<p>Estimation of DBH using the different SLAM methods. The <span class="html-italic">x</span>-axis represents the measured reference data, and the <span class="html-italic">y</span>-axis represents the fitted data corresponding to each reference data point. (<b>a</b>) represents the fitting results for Plot 1; (<b>b</b>) represents the fitting results for Plot 2; (<b>c</b>) represents the fitting results for Plot 3.</p>
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<p>The errors of DBH observations for different DBH values. (<b>a</b>) is the error box plot for visual SLAM; (<b>b</b>) is the error box plot for LiDAR SLAM.</p>
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<p>Scatter plot of DBH errors using the different SLAM methods.</p>
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<p>Scatter plot of position distribution.</p>
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<p>Tree height estimates error statistics.</p>
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<p>Scatter plot of tree height error distribution. (<b>a</b>) is the error distribution of tree height measurements obtained from the visual SLAM method; (<b>b</b>) is the error distribution of tree height measurements obtained from the LiDAR SLAM method.</p>
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<p>Survey duration of each method.</p>
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<p>Tree point cloud based on LiDAR SLAM algorithm. (<b>a</b>) Point cloud characteristics at the tree canopy, (<b>b</b>) Point cloud characteristics at DBH of the trunk, and (<b>c</b>) point cloud characteristics of branches and leaves in the undertree layer.</p>
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<p>Point cloud modeling effect based on AdQSM.</p>
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<p>Point cloud modeling effect based on AdQSM.</p>
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14 pages, 4975 KiB  
Article
Assessment of Tree Species Classification by Decision Tree Algorithm Using Multiwavelength Airborne Polarimetric LiDAR Data
by Zhong Hu and Songxin Tan
Electronics 2024, 13(22), 4534; https://doi.org/10.3390/electronics13224534 - 19 Nov 2024
Viewed by 695
Abstract
Polarimetric measurement has been proven to be of great importance in various applications, including remote sensing in agriculture and forest. Polarimetric full waveform LiDAR is a relatively new yet valuable active remote sensing tool. This instrument offers the full waveform data and polarimetric [...] Read more.
Polarimetric measurement has been proven to be of great importance in various applications, including remote sensing in agriculture and forest. Polarimetric full waveform LiDAR is a relatively new yet valuable active remote sensing tool. This instrument offers the full waveform data and polarimetric information simultaneously. Current studies have primarily used commercial non-polarimetric LiDAR for tree species classification, either at the dominant species level or at the individual tree level. Many classification approaches combine multiple features, such as tree height, stand width, and crown shape, without utilizing polarimetric information. In this work, a customized Multiwavelength Airborne Polarimetric LiDAR (MAPL) system was developed for field tree measurements. The MAPL is a unique system with unparalleled capabilities in vegetation remote sensing. It features four receiving channels at dual wavelengths and dual polarization: near infrared (NIR) co-polarization, NIR cross-polarization, green (GN) co-polarization, and GN cross-polarization, respectively. Data were collected from several tree species, including coniferous trees (blue spruce, ponderosa pine, and Austrian pine) and deciduous trees (ash and maple). The goal was to improve the target identification ability and detection accuracy. A machine learning (ML) approach, specifically a decision tree, was developed to classify tree species based on the peak reflectance values of the MAPL waveforms. The results indicate a re-substitution error of 3.23% and a k-fold loss error of 5.03% for the 2106 tree samples used in this study. The decision tree method proved to be both accurate and effective, and the classification of new observation data can be performed using the previously trained decision tree, as suggested by both error values. Future research will focus on incorporating additional LiDAR data features, exploring more advanced ML methods, and expanding to other vegetation classification applications. Furthermore, the MAPL data can be fused with data from other sensors to provide augmented reality applications, such as Simultaneous Localization and Mapping (SLAM) and Bird’s Eye View (BEV). Its polarimetric capability will enable target characterization beyond shape and distance. Full article
(This article belongs to the Special Issue Image Analysis Using LiDAR Data)
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<p>Schematic diagram of the MAPL system (<b>a</b>), and a photograph of the receiver package (<b>b</b>).</p>
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<p>A flowchart of the proposed decision tree classification using MAPL data.</p>
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<p>Sample LiDAR waveforms of an Austrian pine tree captured by four different polarimetric channels of the MAPL system, with <span class="html-italic">x</span>-axis representing the relative range in pixels and <span class="html-italic">y</span>-axis representing the relative reflectance in arbitrary unit (Ch1: NIR co-polarized, Ch2: NIR cross-polarized, Ch3: GN co-polarized, and Ch4: GN cross-polarized).</p>
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<p>Sample LiDAR waveforms of an Austrian pine tree captured by four different polarimetric channels of the MAPL system, with <span class="html-italic">x</span>-axis representing the relative range in pixels and <span class="html-italic">y</span>-axis representing the relative reflectance in arbitrary unit (Ch1: NIR co-polarized, Ch2: NIR cross-polarized, Ch3: GN co-polarized, and Ch4: GN cross-polarized).</p>
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<p>Matrix graphs of scatter plots grouped by different tree species. The horizontal axes from left to right blocks and vertical axes from top to bottom blocks represent Ch1, Ch2, Ch3, and Ch4, respectively. Both the <span class="html-italic">x</span> axes and <span class="html-italic">y</span> axes are peak intensity with arbitrary units.</p>
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<p>Scatter plot of Ch1 vs. Ch2 grouped by different tree species.</p>
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<p>Graphical description of the decision-making process.</p>
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11 pages, 4689 KiB  
Proceeding Paper
Anxiety Detection Using Consumer Heart Rate Sensors
by Soraya Sinche, Jefferson Acán and Pablo Hidalgo
Eng. Proc. 2024, 77(1), 10; https://doi.org/10.3390/engproc2024077010 - 18 Nov 2024
Viewed by 251
Abstract
Increasingly, humans are exposed to different activities at work, at home, and in general in their daily lives that generate episodes of stress. In many cases, these episodes could produce disorders in their health and reduce their quality of life. For this reason, [...] Read more.
Increasingly, humans are exposed to different activities at work, at home, and in general in their daily lives that generate episodes of stress. In many cases, these episodes could produce disorders in their health and reduce their quality of life. For this reason, it is crucial to implement mechanisms that can detect stress in individuals and develop applications that provide feedback through various activities to help reduce stress levels. Physiological parameters, such as galvanic skin response (GSR) and heart rate (HR) are indicative of stress-related changes. There exist methodologies that use wearable sensors to measure these stress levels. In this study, a sensor of blood volume pulse (BVP) and an electrocardiography (ECG) sensor were utilized to obtain metrics like heart rate variability (HRV) and pulse arrival time (PAT). Their features were extracted, processed, and analyzed for anxiety detection. The classification performance was evaluated using decision trees, a support vector machine (SVM), and meta-classifiers to accurately distinguish between “stressed” and “non-stressed” states. We obtained the best results with the SVM classifier using all the features. Additionally, we found that the ECG AD8232 sensor provided more reliable data compared to the photoplethysmography (PPG) signal obtained from the MAX30100 sensor. Therefore, the ECG is a more accurate tool for assessing emotional states related to stress and anxiety. Full article
(This article belongs to the Proceedings of The XXXII Conference on Electrical and Electronic Engineering)
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<p>Measuring with a triode ECG sensor.</p>
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<p>Sample density distribution function [<a href="#B11-engproc-77-00010" class="html-bibr">11</a>].</p>
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<p>Connections with MAX-30100, AD8232, and ESP32.</p>
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<p>Wiring diagram implemented for data acquisition.</p>
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<p>(<b>a</b>) R–R interval in the ECG signal; (<b>b</b>) IBI in the BVP signal [<a href="#B16-engproc-77-00010" class="html-bibr">16</a>].</p>
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<p>Representation of pulse arrival time [<a href="#B16-engproc-77-00010" class="html-bibr">16</a>].</p>
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<p>(<b>a</b>) HR of each student before and after the activity evaluation related to the score of tests.; (<b>b</b>) Mean of PAT related to the score of the test.</p>
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<p>Relation between HR calculated with ECG and PPG signals.</p>
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17 pages, 4689 KiB  
Article
Development of a Methodology Based on ALS Data and Diameter Distribution Simulation to Characterize Management Units at Tree Level
by Jean A. Magalhães, Juan Guerra-Hernández, Diogo N. Cosenza, Susete Marques, José G. Borges and Margarida Tomé
Remote Sens. 2024, 16(22), 4238; https://doi.org/10.3390/rs16224238 - 14 Nov 2024
Viewed by 455
Abstract
Characterizing Management Units (MUs) with tree-level data is instrumental for a comprehensive understanding of forest structure and for providing information needed to support forest management decision-making. Airborne Laser Scanning (ALS) data may enhance this characterization. While some studies rely on Individual Tree Detection [...] Read more.
Characterizing Management Units (MUs) with tree-level data is instrumental for a comprehensive understanding of forest structure and for providing information needed to support forest management decision-making. Airborne Laser Scanning (ALS) data may enhance this characterization. While some studies rely on Individual Tree Detection (ITD) methods using ALS data to estimate tree diameters within stands, these methods often face challenges when the goal is to characterize MUs in dense forests. This study proposes a methodology that simulates diameter distributions from LiDAR data using an Area-Based Approach (ABA) to overcome these limitations. Focusing on maritime pine (Pinus pinaster Ait.) MUs within a forest intervention zone in northern Portugal, the research initially assesses the suitability of two highly flexible Probability Density Functions (PDFs), Johnson’s SB and Weibull, for simulating diameter distribution in maritime pine stands in Portugal using the PINASTER database. The selected PDF is then used in conjunction with ABA to derive the variables needed for parameter recovery, enabling the simulation of diameter distributions within each MU. Monte Carlo Simulation (MCS) is applied to generate a sample list of tree diameters from the simulated distributions. The results indicate that this methodology is appropriate to estimate diameter distributions within maritime pine MUs by using ABA combined with Johnson’s SB and Weibull PDFs. Full article
(This article belongs to the Section Forest Remote Sensing)
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<p>Flowchart of the methodological process for generating a tree list for each Management Unit.</p>
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<p>Maritime pine Management Units (MUs) within an aggregated management forest area in northern Portugal.</p>
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<p>Median diameter (dmedian), quadratic mean diameter (dg), and tree density (N) in the Management Units.</p>
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<p>Examples of the variations in shapes and scale of the simulated diameter distribution across different Management Units.</p>
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