Nothing Special   »   [go: up one dir, main page]

You seem to have javascript disabled. Please note that many of the page functionalities won't work as expected without javascript enabled.
 
 
Sign in to use this feature.

Years

Between: -

Subjects

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Journals

remove_circle_outline
remove_circle_outline
remove_circle_outline

Article Types

Countries / Regions

remove_circle_outline
remove_circle_outline

Search Results (148)

Search Parameters:
Keywords = dove

Order results
Result details
Results per page
Select all
Export citation of selected articles as:
21 pages, 4875 KiB  
Article
Proteome and Metabolome Analyses of Albino Bracts in Davidia involucrata
by Qinsong Liu, Jinqiu Wang, Yuying Li, Lei Xu, Wenjuan Xu, Ramesh R. Vetukuri and Xiao Xu
Plants 2025, 14(4), 549; https://doi.org/10.3390/plants14040549 - 11 Feb 2025
Viewed by 340
Abstract
Although the mechanisms underlying albino phenotypes have been examined in model plants and major crops, our knowledge of bract albinism is still in its infancy. Davidia involucrata, a relic plant called dove tree, is best known for the intriguing trait with a [...] Read more.
Although the mechanisms underlying albino phenotypes have been examined in model plants and major crops, our knowledge of bract albinism is still in its infancy. Davidia involucrata, a relic plant called dove tree, is best known for the intriguing trait with a pair of white bracts covering the capitula. Here, comparative physiological, cytological, proteomic, and metabolomic analyses were performed to dissect the albinism mechanism of D. involucrata bracts. The bracts exhibited low chlorophyll and carotenoid contents, reduced photosynthetic efficiency, and impaired chloroplast structure. The severe deficiency of photosynthetic pigments and the substantial decrease in cuticle thickness made the bracts light-sensitive. In total, 1134 differentially expressed proteins (DEPs) were obtained between bracts and leaves. Pathway enrichment analysis of DEPs revealed that photosynthetic pigment biosynthesis and photosynthesis were suppressed, whereas protein processing in endoplasmic reticulum, flavonoid biosynthesis, and the ubiquitin–proteasome system (UPS) were activated in bracts. Strikingly, DEPs implicated in chloroplast development, including PPR and AARS proteins, were mainly down-regulated in bracts. We further investigated albinism-induced metabolic changes and detected 412 differentially abundant metabolites (DAMs). Among them, enhanced flavonoids accumulation can plausibly explain the role of bracts in pollinator attraction. Amino acids and their derivatives in bracts showed remarkably increased abundance, which might be causally linked to enhanced UPS function. Our work could lay foundations for understanding albinism mechanisms and adaptive significance of plant bracts and facilitate future utilization of D. involucrata resources. Full article
(This article belongs to the Section Plant Molecular Biology)
Show Figures

Figure 1

Figure 1
<p>Phenotype and photosynthetic pigment contents of <span class="html-italic">D. involucrata</span> leaves and bracts. (<b>A</b>) Photo of <span class="html-italic">D. involucrata</span>. (<b>B</b>) Leaves, bracts, and flower of <span class="html-italic">D. involucrata</span>. (<b>C</b>) Contents of Chl a, Chl b, Chl a + b, and carotenoids in leaf samples (LEAF) and bract samples (BRAC). Values represent means ± SD (<span class="html-italic">n</span> = 4). Statistical significance (**** <span class="html-italic">p</span> &lt; 0.0001) was revealed by Student’s <span class="html-italic">t</span>-test.</p>
Full article ">Figure 2
<p>Photosynthetic characteristics of <span class="html-italic">D. involucrata</span> leaves and bracts. (<b>A</b>) Net photosynthetic rate (Pn). (<b>B</b>) Stomatal conductance (Gs). (<b>C</b>) Intercellular CO<sub>2</sub> concentration (Ci). (<b>D</b>) Transpiration rate (Tr). (<b>E</b>) Maximum quantum yield of photosystem II (PSII) (Fv/Fm). (<b>F</b>) Effective quantum yield of PSII [Y(II)]. (<b>G</b>) Electron transport rate (ETR). (<b>H</b>) Photochemical quenching (qP). Values represent means ± SD (<span class="html-italic">n</span> = 4). Statistical significance (** <span class="html-italic">p</span> &lt; 0.01, **** <span class="html-italic">p</span> &lt; 0.0001) was revealed by Student’s <span class="html-italic">t</span>-test.</p>
Full article ">Figure 3
<p>TEM analysis of <span class="html-italic">D. involucrata</span> leaves and bracts. (<b>A</b>–<b>C</b>) Electron micrographs of <span class="html-italic">D. involucrata</span> leaves. (<b>D</b>–<b>F</b>) Electron micrographs of <span class="html-italic">D. involucrata</span> bracts. Cp, chloroplast; S, starch granule; SL, stroma lamella; GL, grana lamella; PG, plastoglobule. Bars in (<b>A</b>,<b>D</b>), 5 μm; bars in (<b>B</b>,<b>C</b>,<b>E</b>,<b>F</b>), 1 μm.</p>
Full article ">Figure 4
<p>Proteomic alterations between <span class="html-italic">D. involucrata</span> bracts and leaves. (<b>A</b>) Volcano plot showing differential expression levels. Orange and green dots represent significantly up- and down-regulated DEPs, respectively. (<b>B</b>) Subcellular location of DEPs.</p>
Full article ">Figure 5
<p>Go enrichment analysis of DEPs between <span class="html-italic">D. involucrata</span> bracts and leaves. (<b>A</b>) Distribution of up-regulated DEPs with GO annotation. (<b>B</b>) Distribution of down-regulated DEPs with GO annotation. The results were summarized in three categories, including biological process, molecular function, and cellular component. The number of DEPs in each GO term was displayed in a pie chart.</p>
Full article ">Figure 6
<p>KEGG pathway classification for up-regulated DEPs (<b>A</b>) and down-regulated DEPs (<b>B</b>) between <span class="html-italic">D. involucrata</span> bracts and leaves.</p>
Full article ">Figure 7
<p>Heatmap of DEPs implicated in chlorophyll metabolism, carotenoid biosynthesis, photosynthetic metabolism, and protein quality control. Heatmap was generated based on the log<sub>2</sub> fold change values (BRAC vs. LEAF). Detailed annotation information of these DEPs can be found in <a href="#app1-plants-14-00549" class="html-app">Table S2</a>.</p>
Full article ">Figure 8
<p>Analysis of DAMs between <span class="html-italic">D. involucrata</span> bracts and leaves. (<b>A</b>) PCA analysis. (<b>B</b>) Volcano plot of DAMs. Red and green dots represent significantly up- and down-regulated DAMs, respectively. (<b>C</b>) KEGG analysis of DAMs. (<b>D</b>) Classification of DAMs.</p>
Full article ">Figure 9
<p>Integrated proteomic and metabolomic analyses of the flavonoid biosynthetic pathway. Red solid circles indicate up-regulation of DAMs, green solid circles indicate down-regulation of DAMs, and values on the right side represent the log<sub>2</sub> fold change of DAMs (BRAC vs. LEAF). Heatmap represents the expression difference of DEPs and was generated based on the log<sub>2</sub> fold change values (bracts vs. leaves). Detailed annotation information of these DEPs can be found in <a href="#app1-plants-14-00549" class="html-app">Table S4</a>.</p>
Full article ">Figure 10
<p>Relative electrolyte leakage (<b>A</b>), SOD activity (<b>B</b>), POD activity (<b>C</b>), and GSH content (<b>D</b>) in <span class="html-italic">D. involucrata</span> leaves and bracts. Values represent means ± SD (<span class="html-italic">n</span> = 4). Statistical significance (*** <span class="html-italic">p</span> &lt; 0.001, **** <span class="html-italic">p</span> &lt; 0.0001) was revealed by Student’s <span class="html-italic">t</span>-test.</p>
Full article ">Figure 11
<p>Schematic overview of potential albinism mechanism as well as metabolic and molecular adaptation in <span class="html-italic">D. involucrata</span> bracts. Red text represents up-regulation or enhancement, while green text represents down-regulation or impairment.</p>
Full article ">
13 pages, 206 KiB  
Article
‘I Heard Music’: Mansfield Park, an Opera by Jonathan Dove and Alasdair Middleton
by Gillian Dooley
Humanities 2025, 14(2), 26; https://doi.org/10.3390/h14020026 - 7 Feb 2025
Viewed by 643
Abstract
When composer Jonathan Dove first read Jane Austen’s novel Mansfield Park, he immediately saw its operatic potential. In a newspaper interview, he is quoted as saying that the novel ‘haunted me for years’. He was particularly affected by Fanny Price and her [...] Read more.
When composer Jonathan Dove first read Jane Austen’s novel Mansfield Park, he immediately saw its operatic potential. In a newspaper interview, he is quoted as saying that the novel ‘haunted me for years’. He was particularly affected by Fanny Price and her predicament. When the opportunity came to write the opera, Dove worked with librettist Alasdair Middleton to create an operatic work that builds on and reinterprets Austen’s novel. It is a chamber opera, originally scored for piano duet, and although Dove later made an arrangement for a chamber ensemble, he retained the piano, identifying it as a sound world with which Austen was intimately familiar. In this paper, I track the transition from the printed page via the score and the libretto to the opera, and analyse the means by which Dove and Middleton create this popular adaptation, including telescoping the plot, using and adapting Austen’s own language, incorporating music inspired by eighteenth-century glees, and using characters as a chorus, with music that enhances the impact and translates the powerful emotions on Austen’s page into raw and urgent feelings. Full article
(This article belongs to the Special Issue Music and the Written Word)
19 pages, 6533 KiB  
Article
Robustness of Actual Evapotranspiration Predicted by Random Forest Model Integrating Remote Sensing and Meteorological Information: Case of Watermelon (Citrullus lanatus, (Thunb.) Matsum. & Nakai, 1916)
by Simone Pietro Garofalo, Francesca Ardito, Nicola Sanitate, Gabriele De Carolis, Sergio Ruggieri, Vincenzo Giannico, Gianfranco Rana and Rossana Monica Ferrara
Water 2025, 17(3), 323; https://doi.org/10.3390/w17030323 - 23 Jan 2025
Viewed by 526
Abstract
Water scarcity, exacerbated by climate change and increasing agricultural water demands, highlights the necessity for efficient irrigation management. This study focused on estimating actual evapotranspiration (ETa) in watermelons under semi-arid Mediterranean conditions by integrating high-resolution satellite imagery and agro-meteorological data. Field experiments were [...] Read more.
Water scarcity, exacerbated by climate change and increasing agricultural water demands, highlights the necessity for efficient irrigation management. This study focused on estimating actual evapotranspiration (ETa) in watermelons under semi-arid Mediterranean conditions by integrating high-resolution satellite imagery and agro-meteorological data. Field experiments were conducted in Rutigliano, southern Italy, over a 2.80 ha area. ETa was measured with the eddy covariance (EC) technique and predicted using machine learning models. Multispectral reflectance data from Planet SuperDove satellites and local meteorological records were used as predictors. Partial least squares, the generalized linear model and three machine learning algorithms (Random Forest, Elastic Net, and Support Vector Machine) were evaluated. Random Forest yielded the highest predictive accuracy with an average R2 of 0.74, RMSE of 0.577 mm, and MBE of 0.03 mm. Model interpretability was performed through permutation importance and SHAP, identifying the near-infrared and red spectral bands, average daily temperature, and relative humidity as key predictors. This integrated approach could provide a scalable, precise method for watermelon ETa estimation, supporting data-driven irrigation management and improving water use efficiency in Mediterranean horticultural systems. Full article
Show Figures

Figure 1

Figure 1
<p>(<b>A</b>) Rutigliano, southern Italy (OpenStreetMap contributors); (<b>B</b>) aerial view of the experimental field where watermelon was cultivated in 2023.</p>
Full article ">Figure 2
<p>(<b>a</b>) Trend of mean temperature and relative humidity during the growing season; (<b>b</b>) daily rainfall and irrigation water applied during the growing season.</p>
Full article ">Figure 3
<p>Comparison between the complete set of daily watermelon actual evapotranspiration data collected throughout the study season by eddy covariance method (black circles) and the subset corresponding to dates with available satellite imagery used in the analyses (red triangles).</p>
Full article ">Figure 4
<p>Heatmap of the correlation matrix among the dataset variables. The values within the cells represent Pearson correlation coefficients. ETa = actual evapotranspiration after pre-processing, T_mean = mean air temperature, RH = air relative humidity.</p>
Full article ">Figure 5
<p>Trend of field-measured daily watermelon evapotranspiration (observed ETa) and the predicted watermelon ETa using the Random Forest-based model. The trend of watermelon leaf area index (LAI, m<sup>2</sup> m<sup>−2</sup>).</p>
Full article ">Figure 6
<p>Permutation-based feature importance for the Random Forest model predicting watermelon actual evapotranspiration. Error bars indicate the standard deviation of feature importance across permutations.</p>
Full article ">Figure 7
<p>SHAP summary plot showing the impact of each feature on the Random Forest model’s predictions for watermelon actual evapotranspiration.</p>
Full article ">Figure 8
<p>LIME explanation for the most accurate prediction. The bar plot highlights the contribution of specific feature ranges to the Random Forest prediction, showing their positive impact on model accuracy.</p>
Full article ">
23 pages, 25322 KiB  
Article
Prediction of Winter Wheat Parameters with Planet SuperDove Imagery and Explainable Artificial Intelligence
by Gabriele De Carolis, Vincenzo Giannico, Leonardo Costanza, Francesca Ardito, Anna Maria Stellacci, Afwa Thameur, Sergio Ruggieri, Sabina Tangaro, Marcello Mastrorilli, Nicola Sanitate and Simone Pietro Garofalo
Agronomy 2025, 15(1), 241; https://doi.org/10.3390/agronomy15010241 - 19 Jan 2025
Viewed by 923
Abstract
This study investigated the application of high-resolution satellite imagery from SuperDove satellites combined with machine learning algorithms to estimate the spatiotemporal variability of some winter wheat parameters, including the relative leaf chlorophyll content (RCC), relative water content (RWC), and aboveground dry matter (DM). [...] Read more.
This study investigated the application of high-resolution satellite imagery from SuperDove satellites combined with machine learning algorithms to estimate the spatiotemporal variability of some winter wheat parameters, including the relative leaf chlorophyll content (RCC), relative water content (RWC), and aboveground dry matter (DM). The research was carried out within an experimental field in Southern Italy during the 2024 growing season. Different machine learning (ML) algorithms were trained and compared using spectral band data and calculated vegetation indices (VIs) as predictors. Model performance was assessed using R2 and RMSE. The ML models tested were random forest (RF), support vector regressor (SVR), and extreme gradient boosting (XGB). RF outperformed the other ML algorithms in the prediction of RCC when using VIs as predictors (R2 = 0.81) and in the prediction of the RWC and DM when using spectral bands data as predictors (R2 = 0.71 and 0.87, respectively). Model explainability was assessed with the SHAP method. A SHAP analysis highlighted that GNDVI, Cl1, and NDRE were the most important VIs for predicting RCC, while yellow and red bands were the most important for DM prediction, and yellow and nir bands for RWC prediction. The best model found for each target was used to model its seasonal trend and produce a variability map. This approach highlights the potential of integrating ML and high-resolution satellite imagery for the remote monitoring of wheat, which can support sustainable farming practices. Full article
(This article belongs to the Section Precision and Digital Agriculture)
Show Figures

Figure 1

Figure 1
<p>The location of the experimental farm, south of Italy (<b>A</b>); random points (green dots) where the relative leaf chlorophyll content, relative water content, and aboveground dry matter were determined within the field (red line) (<b>B</b>) (OpenStreetMap Contributors, 2024; Map data© 2015 Google).</p>
Full article ">Figure 2
<p>Frequency distributions for the ground truth data acquired for this study (relative leaf chlorophyll content, RCC; relative water content, RWC; aboveground dry matter, DM) with their respective kurtosis (K) and skewness (S) values.</p>
Full article ">Figure 3
<p>The framework of the study for the prediction of the relative leaf chlorophyll content, relative water content, and aboveground dry matter.</p>
Full article ">Figure 4
<p>Variation in air vapor pressure deficit (air VPD), minimum, mean, and maximum temperatures during wheat growing season (<b>A</b>); variation in crop evapotranspiration (ETc) and rainfall during wheat growing season (<b>B</b>).</p>
Full article ">Figure 5
<p>A map (<b>A</b>) and frequency plot of the pixel value (<b>B</b>) of the Brightness Index of the field before sowing (19 November 2023).</p>
Full article ">Figure 6
<p>SHAP summary plots for the random forest model for the prediction of the relative leaf chlorophyll content (RCC, <b>A</b>); aboveground dry matter (DM, <b>B</b>); and relative water content (RWC, <b>C</b>). The graphs report the distribution of SHAP values for each feature, with the dots’ colors changing depending on the features’ values. A positive SHAP value indicates a positive impact on the model, and a negative SHAP value indicates a negative impact on the model.</p>
Full article ">Figure 7
<p>The trends in the mean and standard deviation of the observed and predicted variables: (<b>A</b>) the relative chlorophyll content, (<b>B</b>) aboveground dry matter, and (<b>C</b>) relative water content. The observed and predicted values are compared on the same DOYs for each parameter. Moreover, predictions were extended to additional DOYs, namely 61, 73, and 104 in the case of RCC and 104 in the case of DM and RWC.</p>
Full article ">Figure 8
<p>Predictive maps of the relative leaf chlorophyll content for the DOY (day of the year) of ground measurements, obtained by applying the random forest model trained with vegetation indices.</p>
Full article ">Figure 9
<p>Predictive maps of the aboveground dry matter for the DOY (day of the year) of ground measurements, obtained by applying the random forest model trained with SuperDove spectral bands.</p>
Full article ">Figure 10
<p>Predictive maps of the relative water content for the DOY (day of the year) of ground measurements, obtained by applying the random forest model trained with SuperDove spectral bands.</p>
Full article ">
16 pages, 41766 KiB  
Article
Methodology for Removing Striping Artifacts Encountered in Planet SuperDove Ocean-Color Products
by Brittney Slocum, Sherwin Ladner, Adam Lawson, Mark David Lewis and Sean McCarthy
Remote Sens. 2024, 16(24), 4707; https://doi.org/10.3390/rs16244707 - 17 Dec 2024
Viewed by 696
Abstract
The Planet SuperDove sensors produce eight-band, three-meter resolution images covering the blue, green, red, red-edge, and NIR spectral bands. Variations in spectral response in the data used to perform atmospheric correction combined with low signal-to-noise over ocean waters can lead to visible striping [...] Read more.
The Planet SuperDove sensors produce eight-band, three-meter resolution images covering the blue, green, red, red-edge, and NIR spectral bands. Variations in spectral response in the data used to perform atmospheric correction combined with low signal-to-noise over ocean waters can lead to visible striping artifacts in the downstream ocean-color products. It was determined that the striping artifacts could be removed from these products by filtering the top of the atmosphere radiance in the red and NIR bands prior to selecting the aerosol models, without sacrificing high-resolution features in the imagery. This paper examines an approach that applies this filtering to the respective bands as a preprocessing step. The outcome and performance of this filtering technique are examined to assess the success of removing the striping effect in atmospherically corrected Planet SuperDove data. Full article
Show Figures

Figure 1

Figure 1
<p>SuperDove 3 m true-color of the West Florida Shelf, 30 September 2022 15:07:50 GMT (<b>left</b>), and Venice 14 April 2020 09:15:21 GMT (<b>right</b>), overlaid onto a VIIRS 750 m resolution scene for spatial comparison.</p>
Full article ">Figure 2
<p>West Florida Shelf <span class="html-italic">L<sub>t</sub></span> product for (<b>a</b>) 491 nm, (<b>b</b>) 708 nm, and (<b>c</b>) 867 nm.</p>
Full article ">Figure 3
<p>Venice <span class="html-italic">L<sub>t</sub></span> product for (<b>a</b>) 491 nm, (<b>b</b>) 708 nm, and (<b>c</b>) 867 nm.</p>
Full article ">Figure 4
<p>West Florida Shelf <span class="html-italic"><sub>n</sub>L<sub>w</sub></span> product for (<b>a</b>) 491 nm, (<b>b</b>) 708 nm, and (<b>c</b>) 867 nm.</p>
Full article ">Figure 5
<p>Venice <span class="html-italic"><sub>n</sub>L<sub>w</sub></span> product for (<b>a</b>) 491 nm, (<b>b</b>) 708 nm, and (<b>c</b>) 867 nm.</p>
Full article ">Figure 6
<p><span class="html-italic">L<sub>a</sub></span> product for the West Florida Shelf: (<b>a</b>) 491 nm, (<b>b</b>) 708 nm, and (<b>c</b>) 867 nm.</p>
Full article ">Figure 7
<p>Aerosol model product for Venice: (<b>a</b>) 491 nm, (<b>b</b>) 708 nm, and (<b>c</b>) 867 nm.</p>
Full article ">Figure 8
<p>Log-scaled power spectrum of the above average power components in the West Florida Shelf data (<b>left</b>) and Venice data (<b>right</b>).</p>
Full article ">Figure 9
<p>Masked Frequency components for the middle 400 frequencies of the spectrum after the application of the notch and low-pass filters.</p>
Full article ">Figure 10
<p>Application of SciPy Uniform filter with kernel size 301 vs. 601 for 5 iterations on the <span class="html-italic">L<sub>t</sub></span> (top) and resulting <span class="html-italic">L<sub>a</sub></span> (bottom) at 708 nm where (<b>a</b>,<b>d</b>) are the original, striped, images; (<b>b</b>,<b>e</b>) are the 301 × 301 kernel filtered images; and (<b>c</b>,<b>f</b>) are the 601 × 601 kernel filtered images.</p>
Full article ">Figure 11
<p>Application of SciPy Uniform filter with kernel size 301 vs. 601 for 5 iterations on the <span class="html-italic">L<sub>t</sub></span> (top) and resulting <span class="html-italic">L<sub>a</sub></span> (bottom) at 867 where (<b>a</b>,<b>d</b>) are the original, striped, image; (<b>b</b>,<b>e</b>) are the 301 × 301 kernel filtered images; and (<b>c</b>,<b>f</b>) are the 601 × 601 kernel filtered images.</p>
Full article ">Figure 12
<p><span class="html-italic"><sub>n</sub>L<sub>w</sub></span> at 491 nm after application of SciPy Uniform filter with kernel size 301 for up to 5 iterations to the West Florida Shelf data.</p>
Full article ">Figure 13
<p><span class="html-italic"><sub>n</sub>L<sub>w</sub></span> at 491 nm after application of SciPy Uniform filter with kernel size 301 for up to 5 iterations to the Venice data.</p>
Full article ">Figure 14
<p><span class="html-italic"><sub>n</sub>L<sub>w</sub></span> at 491 nm after application of SciPy Uniform filter with kernel size 601 for up to 5 iterations to the West Florida Shelf data.</p>
Full article ">Figure 15
<p><span class="html-italic"><sub>n</sub>L<sub>w</sub></span> at 491 nm after application of SciPy Uniform filter with kernel size 601 for up to 5 iterations to the Venice data.</p>
Full article ">Figure 16
<p><span class="html-italic">L<sub>t</sub></span>, <span class="html-italic">L<sub>a</sub></span>, and <span class="html-italic"><sub>n</sub>L<sub>w</sub></span> after the application of the notch filter to the <span class="html-italic">L<sub>t</sub></span> for the West Florida Shelf (<b>top</b>) and Venice (<b>bottom</b>) scenes.</p>
Full article ">
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 1028
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
Show Figures

Figure 1

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>
Full article ">Figure 2
<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>
Full article ">
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 1423
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
Show Figures

Figure 1

Figure 1
<p>Location of the study area.</p>
Full article ">Figure 2
<p>Schematic flowchart of the steps for the radiometric normalization of the PS constellation.</p>
Full article ">Figure 3
<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>
Full article ">Figure 4
<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>
Full article ">Figure 5
<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>
Full article ">Figure 6
<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>
Full article ">Figure 7
<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>
Full article ">
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
Cited by 1 | Viewed by 969
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)
Show Figures

Figure 1

Figure 1
<p>Geographic distribution of the study area.</p>
Full article ">Figure 2
<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>
Full article ">Figure 3
<p>Technical workflow for satellite-derived bathymetry.</p>
Full article ">Figure 4
<p>Distribution of sample pixels: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
Full article ">Figure 5
<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>
Full article ">Figure 6
<p>Bathymetry maps derived from the IPDB model: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
Full article ">Figure 7
<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>
Full article ">Figure 8
<p>Distribution of different pixels pairs: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
Full article ">Figure 9
<p>Distribution of different waterlines: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
Full article ">Figure 10
<p>Distribution of different deep water regions: (<b>a</b>) Dongdao Island; (<b>b</b>) Yongxing Island; (<b>c</b>) Yongle Atoll.</p>
Full article ">
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 1191
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
Show Figures

Figure 1

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>
Full article ">Figure 2
<p>The construction of U-Net.</p>
Full article ">Figure 3
<p>The structure of MPG-Net. MS and PGC are the two improved structures proposed in this study.</p>
Full article ">Figure 4
<p>The MS structure. Inception module on the left. Dilated residual module with Dilation rate equal to 5 on the right.</p>
Full article ">Figure 5
<p>The PGC structure. The upper branch is the bottleneck module and GC module, and the lower branch is the PSA module.</p>
Full article ">Figure 6
<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>
Full article ">Figure 7
<p>Results of testing set segmentation of aquaculture ponds on Sentinel-2 dataset with different models.</p>
Full article ">Figure 8
<p>Results of testing set segmentation of aquaculture ponds on Planet dataset with different models.</p>
Full article ">Figure 9
<p>Results of ablation experiments on Sentinel-2 testing set.</p>
Full article ">Figure 10
<p>Results of ablation experiments on the Planet testing set.</p>
Full article ">Figure 11
<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>
Full article ">Figure 12
<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>
Full article ">
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
Cited by 1 | Viewed by 2176
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)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<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>
Full article ">Figure 2
<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>
Full article ">Figure 3
<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>
Full article ">Figure 4
<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>
Full article ">Figure 5
<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>
Full article ">Figure 6
<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>
Full article ">
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 895
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 Special Issue Sensors for Smart Industry and Environment)
Show Figures

Figure 1

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>
Full article ">Figure 1 Cont.
<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>
Full article ">Figure 2
<p>Scheme of the methodology to obtain the maps of burned area and fire severity.</p>
Full article ">Figure 3
<p>Processing of the DEM.</p>
Full article ">Figure 4
<p>Average differences between vegetation indices in pre- and post-fire images.</p>
Full article ">Figure 5
<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>
Full article ">Figure 5 Cont.
<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>
Full article ">Figure 6
<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>
Full article ">Figure 7
<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>
Full article ">Figure 8
<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>
Full article ">Figure 8 Cont.
<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>
Full article ">
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 5 | Viewed by 3838
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
Show Figures

Figure 1

Figure 1
<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>
Full article ">Figure 2
<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>
Full article ">Figure 3
<p>Bottom-up approach to satellite product validation using UAV multispectral imagery.</p>
Full article ">Figure 4
<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>
Full article ">Figure 5
<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>
Full article ">Figure 6
<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>
Full article ">Figure 7
<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>
Full article ">Figure 8
<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>
Full article ">Figure 9
<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>
Full article ">Figure 10
<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>
Full article ">Figure 11
<p>Spatial offsets identified of the Altum relative to the Mjolnir V-1240.</p>
Full article ">Figure 12
<p>Comparing all pixels in the common study area to identify differences between sensors independent of the target composition.</p>
Full article ">Figure 13
<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>
Full article ">Figure 14
<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>
Full article ">Figure 15
<p>Histograms of each index investigated for hummocks and hollows of the four different altitude Altum datasets and the Mjolnir V-1240 dataset.</p>
Full article ">Figure 16
<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>
Full article ">Figure 17
<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>
Full article ">Figure 18
<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>
Full article ">Figure 19
<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>
Full article ">
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 1397
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)
Show Figures

Figure 1

Figure 1
<p>Diagram of magic effects resulting from conversions between the physical and the digital worlds.</p>
Full article ">Figure 2
<p>System module structure.</p>
Full article ">Figure 3
<p>The research process of this study.</p>
Full article ">Figure 4
<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>
Full article ">Figure 5
<p>The architecture of the proposed magic show system “FUI Magic”.</p>
Full article ">Figure 6
<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>
Full article ">Figure 7
<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>
Full article ">
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 3 | Viewed by 1402
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)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Summary of the methodology used in the current work to discriminate pasture degradation with SuperDove satellite constellation data.</p>
Full article ">Figure 2
<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>
Full article ">Figure 3
<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>
Full article ">Figure 4
<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>
Full article ">Figure 5
<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>
Full article ">Figure 6
<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>
Full article ">Figure 7
<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>
Full article ">Figure 8
<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>
Full article ">Figure 9
<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>
Full article ">Figure 10
<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>
Full article ">Figure 11
<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>
Full article ">Figure 12
<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>
Full article ">Figure 13
<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>
Full article ">Figure 14
<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>
Full article ">Figure 15
<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>
Full article ">Figure 16
<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>
Full article ">
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
Cited by 1 | Viewed by 2794
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)
Show Figures

Figure 1

Figure 1
<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>
Full article ">Figure 2
<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>
Full article ">Figure 3
<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>
Full article ">Figure 4
<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>
Full article ">
Back to TopTop