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19 pages, 6805 KiB  
Article
Multispectral Assessment of Net Radiations Using Comprehensive Multi-Satellite Data
by Muhammad Jawad Arshad, Sikandar Ali, Shahbaz Nasir Khan, Arfan Arshad, Jinping Liu, Faisal Mumtaz, Muhammad Mohsin Waqas, Barjeece Bashir and Rao Husnain Arshad
Water 2024, 16(23), 3378; https://doi.org/10.3390/w16233378 (registering DOI) - 24 Nov 2024
Abstract
Precise estimation of net radiation (Rn) is fundamental to understanding surface energy balance and is critical for accurately determining crop water requirements, especially using remote sensing and geospatial techniques. The core objective of this study is to evaluate multi-satellite-based net radiations on major [...] Read more.
Precise estimation of net radiation (Rn) is fundamental to understanding surface energy balance and is critical for accurately determining crop water requirements, especially using remote sensing and geospatial techniques. The core objective of this study is to evaluate multi-satellite-based net radiations on major cropped areas of the Punjab and Sindh provinces of Pakistan. In this study, overlapping scenes from the Moderate Resolution Imaging Spectroradiometer (MODIS), Landsat 8, and Sentinel 2 were used from 2016 to 2020 along with three temperature products MOD11A1, Landsat 8 (brightness temperature), and ERA5. The multi-satellite-based net radiation estimations on overlapping days were compared with the Global Land Data Assimilation System (GLDAS) dataset. The models based on Landsat 8 and Sentinel 2 data exhibited good performance, with a Nash–Sutcliffe Efficiency (NSE) of 68.9%, a mean error (ME) of 13.918 W/m2, and a bias of 50.669 W/m2. The results indicated that Landsat 8 and Sentinel 2 data produced reliable estimations of net radiation, while MODIS data tended to overestimate due to its higher spatial resolution and broader coverage area. Landsat 8-based estimations are good compared to others, as it has good correlation coefficient and lower RMSE values. The study concludes that Landsat 8 provides the most reliable estimates of net radiation for determining crop water requirements, outperforming other datasets in accuracy. The findings underscore the importance of using high-resolution multi-satellite data for precise agricultural water management, recommending its use in future studies and water resource planning in Pakistan. Full article
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<p>Topographic map of the Punjab and Sindh. The Punjab includes 5 rivers and the Sindh includes 1 major river. The blue line shows the rivers, which are essential for understanding the surface energy balance dynamics in these regions.</p>
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<p>Schematic diagram of estimation of land surface temperature by using Landsat 8. Starting from data acquisition from the Landsat 8 satellite, the process involves multiple stages including preprocessing, band selection, calculation of NDVI and LSE, and conversions to radiance and brightness temperature. Atmospheric corrections are applied to ensure accuracy, and the final LST is calculated using established formulas.</p>
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<p>Flow chart for estimation of net radiation by using Landsat 8, MODIS, and Sentinel 2 with different temperature products of ERA5, MODIS, and Landsat 8.</p>
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<p>Comparison of net radiation (W/m<sup>2</sup>) estimated from different satellites and temperature products with GLDAS; (<b>a</b>) Landsat 8 ERA5, (<b>b</b>) Landsat 8 Landsat 8, (<b>c</b>) Landsat 8 MODIS (MOD11A1), (<b>d</b>) MODIS ERA5, (<b>e</b>) MODIS Landsat 8, (<b>f</b>) MODIS MODIS (MOD11A1), (<b>g</b>) Sentinel 2 ERA5, (<b>h</b>) Sentinel 2 Landsat 8, (<b>i</b>) Sentinel 2 MODIS (MOD11A1).</p>
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<p>(<b>a</b>–<b>c</b>). Time series graph of net radiation estimated by using (<b>a</b>) ERA5, (<b>b</b>) Landsat 8, and (<b>c</b>) MOD11A1.</p>
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<p>(<b>a</b>–<b>c</b>). Statistical performance of net radiation models: (<b>a</b>) Landsat 8 vs. MODIS, (<b>b</b>) Sentinel 2 vs. Landsat 8, (<b>c</b>) Sentinel 2 vs. MODIS.</p>
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19 pages, 15297 KiB  
Article
Forecasting Urban Land Use Dynamics Through Patch-Generating Land Use Simulation and Markov Chain Integration: A Multi-Scenario Predictive Framework
by Ahmed Marey, Liangzhu (Leon) Wang, Sherif Goubran, Abhishek Gaur, Henry Lu, Sylvie Leroyer and Stephane Belair
Sustainability 2024, 16(23), 10255; https://doi.org/10.3390/su162310255 (registering DOI) - 23 Nov 2024
Viewed by 236
Abstract
Rapid urbanization and changing land use dynamics require robust tools for projecting and analyzing future land use scenarios to support sustainable urban development. This study introduces an integrated modeling framework that combines the Patch-generating Land Use Simulation (PLUS) model with Markov Chain (MC) [...] Read more.
Rapid urbanization and changing land use dynamics require robust tools for projecting and analyzing future land use scenarios to support sustainable urban development. This study introduces an integrated modeling framework that combines the Patch-generating Land Use Simulation (PLUS) model with Markov Chain (MC) analysis to simulate land use and land cover (LULC) changes for Montreal Island, Canada. This framework leverages historical data, scenario-based adjustments, and spatial drivers, providing urban planners and policymakers with a tool to evaluate the potential impacts of land use policies. Three scenarios—sustainable, industrial, and baseline—are developed to illustrate distinct pathways for Montreal’s urban development, each reflecting different policy priorities and economic emphases. The integrated MC-PLUS model achieved a high accuracy level, with an overall accuracy of 0.970 and a Kappa coefficient of 0.963 when validated against actual land use data from 2020. The findings indicate that sustainable policies foster more contiguous green spaces, enhancing ecological connectivity, while industrial-focused policies promote the clustering of commercial and industrial zones, often at the expense of green spaces. This study underscores the model’s potential as a valuable decision-support tool in urban planning, allowing for the scenario-driven exploration of LULC dynamics with high spatial precision. Future applications and enhancements could expand its relevance across diverse urban contexts globally. Full article
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<p>Markov Chain and PLUS model framework.</p>
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<p>Land use status for (<b>a</b>) 2012 and (<b>b</b>) 2020.</p>
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<p>(<b>a</b>) Simulated land use status in 2020; (<b>b</b>) current land use status in 2020; (<b>c</b>) the spatial difference between them (colored by the simulated land use type) and; (<b>d</b>) the binary spatial difference between them.</p>
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<p>The influence of driving factors’ proximity to each land use type on land use and land cover (LULC) change.</p>
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<p>Average distance to transportation points for new developments.</p>
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<p>Predicted land use in 2028 compared to observed land use in 2020 under different scenarios.</p>
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<p>Predicted land use in 2028 compared to observed land use in 2020 under different scenarios.</p>
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<p>Average patch size for different land use types under different development scenarios.</p>
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<p>Alternative land use plans.</p>
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<p>Predicted land use in 2028 under different urban plans.</p>
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<p>Land use composition through different buffer distances under each scenario.</p>
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27 pages, 8809 KiB  
Article
Trend Analysis of High-Resolution Soil Moisture Data Based on GAN in the Three-River-Source Region During the 21st Century
by Zhuoqun Li, Siqiong Luo, Xiaoqing Tan and Jingyuan Wang
Remote Sens. 2024, 16(23), 4367; https://doi.org/10.3390/rs16234367 - 22 Nov 2024
Viewed by 246
Abstract
Soil moisture (SM) is a crucial factor in land-atmosphere interactions and climate systems, affecting surface energy, water budgets, and weather extremes. In the Three-River-Source Region (TRSR) of China, rapid climate change necessitates precise SM monitoring. This study employs a novel UNet-Gan model to [...] Read more.
Soil moisture (SM) is a crucial factor in land-atmosphere interactions and climate systems, affecting surface energy, water budgets, and weather extremes. In the Three-River-Source Region (TRSR) of China, rapid climate change necessitates precise SM monitoring. This study employs a novel UNet-Gan model to integrate and downscale SM data from 17 CMIP6 models, producing a high-resolution (0.1°) dataset called CMIP6UNet-Gan. This dataset includes SM data for five depth layers (0–10 cm, 10–30 cm, 30–50 cm, 50–80 cm, 80–110 cm), four Shared Socioeconomic Pathways (SSP1-2.6, SSP2-4.5, SSP3-7.0, SSP5-8.5). The UNet-Gan model demonstrates strong performance in data fusion and downscaling, especially in shallow soil layers. Analysis of the CMIP6UNet-Gan dataset reveals an overall increasing trend in SM across all layers, with higher rates under more intense emission scenarios. Spatially, moisture increases vary, with significant trends in the western Yangtze and northeastern Yellow River regions. Deeper soils show a slower response to climate change, and seasonal variations indicate that moisture increases are most pronounced in spring and winter, followed by autumn, with the least increase observed in summer. Future projections suggest higher moisture increase rates in the early and late 21st century compared to the mid-century. By the end of this century (2071–2100), compared to the Historical period (1995–2014), the increase in SM across the five depth layers ranges from: 5.5% to 11.5%, 4.6% to 9.2%, 4.3% to 7.5%, 4.5% to 7.5%, and 3.3% to 6.5%, respectively. Full article
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<p><b>Above</b> is the location of the study area in China, <b>below</b> is the elevation of the study area and the location of the in-site.</p>
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<p>Training details of the UNet-GAN network.</p>
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<p>The model structure of U-Net (with three output channels for the pretraining phase and five output channels for the fine-tuning phase).</p>
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<p>The model structure of the discriminator. The number following <span class="html-italic">k</span> indicates the convolution kernel size, the number following <span class="html-italic">n</span> indicates the number of output channels, and the number following <span class="html-italic">s</span> indicates the stride.</p>
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<p>Box plots of evaluation metrics for SM from different layers of ERA5-Land and AMSMQTP compared to in situ observations (for MAE, RMSE, and MAPE, smaller values are better, and for R, larger values are better).</p>
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<p>Scatter plot of predicted values versus true values on the test set for five-fold cross-validation (The red dotted line represents a 45-degree diagonal, and the color intensity indicates the density of the points).</p>
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<p>A comparison of the data predicted by the UNet-Gan model for the first layer in the test set with the data from 17 CMIP6 models and their Ensemble, against the AMSMQTP data. The diagram includes three metrics: RMSE, standard deviation, and correlation coefficient.</p>
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<p>Spatial distribution of the annual mean SM trends for Layer 1 under four emission scenarios, with dotted areas indicating regions significant at the 95% confidence level.</p>
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<p>Spatial distribution of annual average SM trend changes in Layer 1 under four emission scenarios for different seasons, with highlighted areas indicating significance at the 95% confidence level (DJF represents winter, MAM represents spring, JJA represents summer, and SON represents autumn).</p>
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<p>Time series of annual average SM for Layer 1 under different historical and future emission scenarios. The legend provides the rate of change, with units in m<sup>3</sup>/m<sup>3</sup> per year, and asterisks indicate significance at the 95% confidence level.</p>
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<p>Time series of annual average SM for Layer 1 under historical and future emission scenarios in different seasons, with the legend showing the rate of change in units of m<sup>3</sup>/m<sup>3</sup> per year. Asterisks indicate significance at the 95% confidence level (DJF represents winter, MAM represents spring, JJA represents summer, and SON represents autumn).</p>
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<p>Time series of annual average SM for Layer 1 under historical and future emission scenarios in different seasons, with the legend showing the rate of change in units of m<sup>3</sup>/m<sup>3</sup> per year. Asterisks indicate significance at the 95% confidence level (DJF represents winter, MAM represents spring, JJA represents summer, and SON represents autumn).</p>
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<p>Same as <a href="#remotesensing-16-04367-f011" class="html-fig">Figure 11</a>, but for JJA and SON.</p>
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<p>Same as <a href="#remotesensing-16-04367-f011" class="html-fig">Figure 11</a>, but for JJA and SON.</p>
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<p>The mean SM of the five layers in TRSR over different periods, with the Historical period covering 1995–2014, and the four emission scenarios covering 2021–2040, 2041–2070, and 2071–2100, respectively. MAM, JJA, SON, and DJF represent mean SM values for spring, summer, autumn, and winter, respectively, while Y represents the mean annual SM.</p>
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<p>The spatial distribution of the percentage increase in Layer 1 SM under four emission scenarios for the end of the 21st century (2071–2100) compared to the beginning of the century (1995–2014).</p>
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<p>The rate of change in SM for the five layers in TRSR over different periods, with the Historical period covering 1995–2014, and the four emission scenarios covering 2021–2040, 2041–2070, and 2071–2100, respectively. Rates that did not pass the 95% significance test are not shown in the figure. MAM, JJA, SON, and DJF represent the rate of SM change for spring, summer, autumn, and winter, respectively, while Y represents the annual rate of SM change, with units in m<sup>3</sup>/m<sup>3</sup> per year.</p>
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25 pages, 7079 KiB  
Article
Research Progress on Land Use and Analysis of Green Transformation in China Since the New Century
by Wei He, Jianzhou Gong and Xiaobin Zeng
Agronomy 2024, 14(12), 2774; https://doi.org/10.3390/agronomy14122774 - 22 Nov 2024
Viewed by 242
Abstract
The optimization of land use structure is a key measure to promote the allocation of land resources, ensure sustainable land development, and address the human-land conflict. Since the 21st century, land use in China has exhibited spatiotemporal dynamic development characteristics in response to [...] Read more.
The optimization of land use structure is a key measure to promote the allocation of land resources, ensure sustainable land development, and address the human-land conflict. Since the 21st century, land use in China has exhibited spatiotemporal dynamic development characteristics in response to socio-economic growth and changes in regional geographical conditions. The academic community, both domestically and internationally, has enriched and refined the research system on China’s land use, driven by the need to optimize its land use structure. This study systematically reviews relevant land use research literature from 2000 to 2024, utilizing bibliometric analysis and visual mapping to conduct phased evaluations and an overall review. The existing LUCC research framework in China is extensive, with a strong focus on land use issues in the context of rapid development. Building on this review and incorporating practical needs, theoretical innovation, interdisciplinary integration, and expansion across multiple fields, we aim to propose a framework for future land resource research. This framework includes: (i) Establishing a Multi-functional Land Use System: This approach promotes the coordinated development of ecological and social benefits of land use. (ii) Enhancing Effective Assessment and Management of Ecological Risks: Such efforts contribute to optimizing spatial planning and ensuring land security. (iii) Addressing Low Land Use Efficiency: Focusing on this issue will enable more precise management aligned with regional characteristics. (iv) Exploring the Application of Multi-disciplinary and Cross-field Technologies in Land Use Efficiency Assessment: This integration will advance spatial planning research. (v) Expanding Research on Multi-functional Land Use and Multi-element Integration: This direction fosters coordination across various planning frameworks, promoting synergies in land use research. Full article
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<p>The 2024 Global EJAtlas (data sourced from <a href="https://ejatlas.org/" target="_blank">https://ejatlas.org/</a>, accessed on 19 November 2024).</p>
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<p>Statistical Chart of Global Environmental Conflict Causes.</p>
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<p>Landsat/Land Cover Change Maps of China for 2000, 2010, and 2020. The map overlays were created using the standard map provided by the China Standard Map Service System (Map Review Approval Number: GS (2020)3184), ensuring no modifications to the base map.</p>
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<p>Division of Arable Land in China’s Nine Major Regions (Billion Mu).</p>
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<p>Comparison of the Number of Land Use Research Publications in China and Internationally. (Note: Pink: domestic land use studies; Green: international land use studies).</p>
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<p>(<b>a</b>) Network Analysis of Land Use/Cover Research in China (2000–2007) and (<b>b</b>) Network Analysis of International Land Use/Cover Research (2000–2007).</p>
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<p>(<b>a</b>) Network Analysis of Land Use/Cover Research in China (2008–2017) and (<b>b</b>) Network Analysis of International Land Use/Cover Research (2008–2017).</p>
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<p>(<b>a</b>) Network Analysis of Land Use/Cover Research in China (2017–2024) and (<b>b</b>) Network Analysis of International Land Use/Cover Research (2017–2024).</p>
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<p>(<b>a</b>) Co-occurrence Analysis of Land Use/Cover Research in China (2000–2024) and (<b>b</b>) Co-occurrence Analysis of International Land Use/Cover Research (2000–2024).</p>
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<p>Heatmap Analysis of Land Use/Cover Research.</p>
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<p>Directions for Future Land Use Research in China and Their Interrelationships.</p>
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<p>Research Framework for Land Use Attributes and Multifunctionality.</p>
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<p>Five Components of the Future Land Use Research Framework.</p>
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20 pages, 1954 KiB  
Article
The Timing of Phosphorus Availability to Corn: What Growth Stages Are Most Critical for Maximizing Yield?
by Kwame Ampong, Chad J. Penn and James J. Camberato
Agronomy 2024, 14(11), 2731; https://doi.org/10.3390/agronomy14112731 - 19 Nov 2024
Viewed by 620
Abstract
Phosphorus (P) is critical for maximizing agricultural production and represents an appreciable input cost. Geologic sources of P that are most easily mined are a finite resource, while P transported from agricultural land to surface waters contributes to water quality degradation. Improved knowledge [...] Read more.
Phosphorus (P) is critical for maximizing agricultural production and represents an appreciable input cost. Geologic sources of P that are most easily mined are a finite resource, while P transported from agricultural land to surface waters contributes to water quality degradation. Improved knowledge of P timing needs by corn (maize) can help inform management decisions that increase P use efficiency, which is beneficial to productivity, economics, and environmental quality. The objective of this study was to evaluate P application timing on the growth and yield components of corn. Corn was grown in a sand-culture hydroponics system that eliminated confounding plant–soil interactions and allowed for precise control of nutrient availability and timing. All nutrients were applied via drip irrigation and were therefore 100% bioavailable. Eight P timing treatments were tested using “low” (L) and “sufficient” (S) P concentrations. In each of the three growth phases, solution P application levels were changed or maintained, resulting in eight possible combinations, LLL, LLS, LSL, LSS, SLL, SSL, SLS, and SSS, where the first, second, and third letters indicate P solution application levels from planting to V6, V6 to R1, and R1 to R6, respectively. All other nutrients were applied at sufficient levels. Sacrificial samples were harvested at V6, R1, and R6 and evaluated for various yield parameters. Plants that received sufficient P between V6 and R1 produced a significantly higher grain yield than plants that received low P between V6 and R1 regardless of the level of P supply before V6 or after R1. The grain yield of plants that received sufficient P only between V6 and R1 did not differ significantly from plants that received only sufficient P (SSS), due to (1) a greater ear P concentration at R1; (2) an efficient remobilization of assimilates from the stem and leaf to grains between R1 and R6 (source–sink relationship); (3) a higher kernel/grain weight; and (4) less investment into root biomass. Full article
(This article belongs to the Special Issue Safe and Efficient Utilization of Water and Fertilizer in Crops)
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<p>Dry weight at the V6 growth stage for corn plant parts in low (L) and sufficient (S) phosphorus (P) treatments applied from emergence to V6: stem dry weight (<b>a</b>); leaf dry weight (<b>b</b>); root dry weight (<b>c</b>); and root/shoot ratio (<b>d</b>). Boxes indicate the interquartile spread (1st and 3rd quartiles), while the horizontal line in the boxplot indicates median values of each P treatment. The lower and upper vertical lines of the box plot indicate the 1st and 3rd quartile, respectively. The rhombus in the boxplots indicates the mean value of four replicates. The same letter on boxplots indicates no significant difference between treatments as assessed by Tukey’s Honest Significant Difference (<span class="html-italic">p</span> ≤ 0.05).</p>
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<p>Dry weight for corn plant parts at R1 grown with low (L) and sufficient (S) solution phosphorus (P) levels: stem dry weight (<b>a</b>); leaf below ear (LBE) dry weight (<b>b</b>); leaf above ear (LAE) dry weight (<b>c</b>); ear dry weight (<b>d</b>); root dry weight (<b>e</b>); and root/shoot ratio (<b>f</b>). Treatments are indicated by letters “L” and “S”, where the first letter indicates the solution P level applied from planting to V6 and the second letter indicates from V6 to R1. Boxes indicate the interquartile spread (1st and 3rd quartiles), while the horizontal line in the boxplot indicates median values of each P treatment. The lower and upper vertical lines of the box plot indicate the 1st and 3rd quartile, respectively. The rhombus in the boxplots indicates the mean value of four replicates. The same letter on boxplots indicates no significant difference between treatments as assessed by Tukey’s Honest Significant Difference (<span class="html-italic">p</span> ≤ 0.05).</p>
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<p>Total dry weight for corn plants at R1 grown with low (L) and sufficient (S) solution phosphorus (P) levels. Treatments are indicated by letters “L” and “S”, where the first letter indicates the solution P level applied from planting to V6 and the second letter indicates from V6 to R1. Boxes indicate the interquartile spread (1st and 3rd quartiles), while the horizontal line in the boxplot indicates median values of each P treatment. The lower and upper vertical lines of the box plot indicate the 1st and 3rd quartile, respectively. The rhombus in the boxplots indicates the mean value of four replicates. The same letter on boxplots indicates no significant difference between treatments as assessed by Tukey’s Honest Significant Difference (<span class="html-italic">p</span> ≤ 0.05).</p>
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<p>Total dry weight for corn plant grown with low (L) and sufficient (S) solution phosphorus (P) levels at R6. Treatments are indicated by letters “L” and “S”, where the first letter indicates the solution P level applied from planting to V6, the second letter indicates from V6 to R1, and the third letter indicates from R1 to R6. Boxes indicate the interquartile spread (1st and 3rd quantiles), while the horizontal line in the boxplot indicates median values of each P treatment. The lower and upper vertical lines of the box plot indicate the 1st and 3rd quartile, respectively. The rhombus in the boxplots indicates the mean value of four replicates. The same letter on boxplots indicates no significant difference between treatments as assessed by Tukey’s Honest Significant Difference (<span class="html-italic">p</span> ≤ 0.05).</p>
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<p>Dry weight for corn plant parts at R6 grown with low (L) and sufficient (S) solution phosphorus (P) levels: stem dry weight (<b>a</b>); leaf below ear (LBE) dry weight (<b>b</b>); leaf above ear (LAE) dry weight (<b>c</b>); cobb, husk, and immature ear (CHI) dry weight (<b>d</b>); root dry weight (<b>e</b>); and root/shoot ratio (<b>f</b>). Treatments are indicated by letters “L” and “S”, where the first letter indicates the solution P level applied from planting to V6, the second letter indicates from V6 to R1, and the third letter indicates from R1 to R6. Boxes indicate the interquartile spread (1st and 3rd quartiles), while the horizontal line in the boxplot indicates median values of each P treatment. The lower and upper vertical lines of the box plot indicate the 1st and 3rd quartile, respectively. The rhombus in the boxplots indicates the mean value of four replicates. The same letter on boxplots indicates no significant difference between treatments as assessed by Tukey’s Honest Significant Difference (<span class="html-italic">p</span> ≤ 0.05).</p>
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<p>Grain yield at 15.5% moisture for corn plants at R6 grown with low (L) and sufficient (S) solution phosphorus (P) levels. Treatments are indicated by letters “L” and “S”, where the first letter indicates the solution P level applied from planting to V6, the second letter indicates from V6 to R1, and the third letter indicates from R1 to R6. Boxes indicate the interquartile spread (1st and 3rd quartiles), while the horizontal line in the boxplot indicates median values of each P treatment. The lower and upper vertical lines of the box plot indicate the 1st and 3rd quartile, respectively. The rhombus in the boxplots indicates the mean value of four replicates. The same letter on boxplots indicates no significant difference between treatments as assessed by Tukey’s Honest Significant Difference (<span class="html-italic">p</span> ≤ 0.05).</p>
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<p>Corn plant growth parameters at R1 grown with low (L) and sufficient (S) solution phosphorus (P) levels varying by growth stage: stem diameter (<b>a</b>); height (<b>b</b>); number of leaves (<b>c</b>); total leaf area (<b>d</b>). Treatments are indicated by letters “L” and “S”, where the first letter indicates the solution P level applied from planting to V6 and the second letter indicates from V6 to R1. Boxes indicate the interquartile spread (1st and 3rd quantiles), while the horizontal line in the boxplot indicates median values of each P treatment. The lower and upper vertical lines of the box plot indicate the 1st and 3rd quartile, respectively. The rhombus in the boxplots indicates the mean value of four replicates. The same letter on boxplots indicates no significant difference between treatments as assessed by Tukey’s Honest Significant Difference (<span class="html-italic">p</span> ≤ 0.05).</p>
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<p>Yield components at R6 for corn plant grown with low (L) and sufficient (S) solution phosphorus (P) levels: grain number (<b>a</b>); kernel row number (<b>b</b>); and 100-grain weight (<b>c</b>). Treatments are indicated by letters “L” and “S”, where the first letter indicates the solution P level applied from planting to V6, the second letter indicates from V6 to R1, and the third letter indicates from R1 to R6. Boxes indicate the interquartile spread (1st and 3rd quartiles), while the horizontal line in the boxplot indicates median values of each P treatment. The lower and upper vertical lines of the box plot indicate the 1st and 3rd quartile, respectively. The rhombus in the boxplots indicates the mean value of four replicates. The same letter on boxplots indicates no significant difference between treatments as assessed by Tukey’s Honest Significant Difference (<span class="html-italic">p</span> ≤ 0.05).</p>
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<p>Grain yield at R6 shown as a function of R1 ear P concentration (<b>a</b>), ear dry weight (<b>b</b>), and total dry weight (<b>c</b>). Values for LL, LS, SL, and SS at R1 were plotted against R6 LLL and LLS, LSL and LSS, SLS and SLL, and SSL and SSS, respectively. The data points at R1 for ear P concentration, ear dry weight, and total dry weight are averages of four replications, and grain yields at R6 are averages of six replications.</p>
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28 pages, 35225 KiB  
Article
Edge Computing-Driven Real-Time Drone Detection Using YOLOv9 and NVIDIA Jetson Nano
by Raj Hakani and Abhishek Rawat
Drones 2024, 8(11), 680; https://doi.org/10.3390/drones8110680 - 19 Nov 2024
Viewed by 617
Abstract
Drones, with their ability to vertically take off and land with their stable hovering performance, are becoming favorable in both civilian and military domains. However, this introduces risks of its misuse, which may include security threats to airports, institutes of national importance, VIP [...] Read more.
Drones, with their ability to vertically take off and land with their stable hovering performance, are becoming favorable in both civilian and military domains. However, this introduces risks of its misuse, which may include security threats to airports, institutes of national importance, VIP security, drug trafficking, privacy breaches, etc. To address these issues, automated drone detection systems are essential for preventing unauthorized drone activities. Real-time detection requires high-performance devices such as GPUs. For our experiments, we utilized the NVIDIA Jetson Nano to support YOLOv9-based drone detection. The performance evaluation of YOLOv9 to detect drones is based on metrics like mean average precision (mAP), frames per second (FPS), precision, recall, and F1-score. Experimental data revealed significant improvements over previous models, with a mAP of 95.7%, a precision of 0.946, a recall of 0.864, and an F1-score of 0.903, marking a 4.6% enhancement over YOLOv8. This paper utilizes YOLOv9, optimized with pre-trained weights and transfer learning, achieving significant accuracy in real-time drone detection. Integrated with the NVIDIA Jetson Nano, the system effectively identifies drones at altitudes ranging from 15 feet to 110 feet while adapting to various environmental conditions. The model’s precision and adaptability make it particularly suitable for deployment in security-sensitive areas, where quick and accurate detection is crucial. This research establishes a solid foundation for future counter-drone applications and shows great promise for enhancing situational awareness in critical, high-risk environments. Full article
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<p>Drone utilization: a spectrum of beneficial and malicious purposes.</p>
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<p>Spectrum of drone threat scenarios.</p>
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<p>Basic framework of a two-stage detector.</p>
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<p>Basic framework of a one-stage detector.</p>
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<p>Timeline of YOLO model advancements.</p>
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<p>State-of-the-art YOLOv9 architecture.</p>
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<p>The proposed drone detection diagram using YOLOv9.</p>
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<p>Overview of transfer learning approaches.</p>
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<p>(<b>a</b>) Edge device-centric architecture for real-time drone detection. (<b>b</b>) Experimental setup for real-time drone detection.</p>
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<p>(<b>a</b>) Edge device-centric architecture for real-time drone detection. (<b>b</b>) Experimental setup for real-time drone detection.</p>
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<p>Overall conducted experiment flowchart.</p>
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<p>Confusion matrix in the proposed method.</p>
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<p>Training and validation evolution over the 100 epoch.</p>
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<p>YOLOv9 modal accuracy over the 100 epoch.</p>
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<p>Distribution of the real bounding box: (<b>a</b>) center point distribution and (<b>b</b>) length and width distribution.</p>
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<p>All the metrics of training the YOLOv9 model.</p>
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<p>Real-time drone detection with YOLOv9 at an altitude of 15 feet.</p>
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<p>Detection of drones in real time with YOLOv9 from an altitude of 50 feet.</p>
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<p>Real-time detection of drones using YOLOv9 at an altitude of 110 feet.</p>
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<p>Drone detection in nighttime and at an altitude of 110 feet.</p>
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<p>Detection of drones in dark environments with artificial lighting.</p>
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<p>Detection of drones in high-altitude scenarios with poor visibility.</p>
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<p>Drone detection in low-visibility cloudy environments.</p>
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<p>Drone detection in multiple-object scenes with complex and dynamic backgrounds.</p>
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<p>Real-time drone detection in complex backgrounds.</p>
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<p>Concurrent detection of two drones with YOLOv9.</p>
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<p>Advanced multiple drone detection with YOLOv9.</p>
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12 pages, 7627 KiB  
Article
Evaluating the Usefulness of a PNT Solution Using DGNSS-SBAS for Canoe Slalom: Simulated and Real-World Analysis
by Paul William Macdermid, Mathew E. Irwin and Darryl Cochrane
Appl. Sci. 2024, 14(22), 10614; https://doi.org/10.3390/app142210614 - 18 Nov 2024
Viewed by 315
Abstract
This study investigated the accuracy and precision of a commercially available PNT solution that uses DGNSS-SBAS technology. Time and position data were sampled at a frequency of 20Hz during both a short and long trajectory of a simulated controlled dry-land slalom, as well [...] Read more.
This study investigated the accuracy and precision of a commercially available PNT solution that uses DGNSS-SBAS technology. Time and position data were sampled at a frequency of 20Hz during both a short and long trajectory of a simulated controlled dry-land slalom, as well as during a real-world on-water slalom exercise. The primary objective was to assess the positional accuracy, availability, integrity, and service continuity of the PNT solution while evaluating its ability to differentiate between trajectories. Additionally, the simulated results were compared with an on-water real-world slalom test to validate the findings. The results of the controlled dry-land slalom test indicate that the PNT solution provided accurate measurements with an overall mean ± SD Hrms of 0.20 ± 0.02 m. The integrity measures, HDOD and PDOP, were found to be ideal to excellent, with values of 0.68 ± 0.03 and 1.36 ± 0.07, respectively. The PNT solution utilised an average of 20 ± 1 satellites from the constellation, resulting in an accuracy of <1.5% when measuring the known trajectory of 50 simulated slalom runs. The data from the real-world on-water slalom test supported these findings, providing similar or improved results. Based on these findings, a PNT solution using DGNSS-SBAS can be considered an effective means of tracking athlete trajectory in the sport of canoe slalom. Future research should be conducted to quantify its efficacy more precisely. Full article
(This article belongs to the Special Issue Human Performance in Sports and Training)
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<p>(<b>A</b>) Dry-land simulated slalom course with marked trajectories (obtained from the Arrow 100 and proceed with ArcGIS Pro) for one trial, labelled as short (−) more direct, and long (−) less direct, for validation purposes, and (<b>B</b>) real-world on-water flatwater slalom course used.</p>
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<p>(<b>A</b>) Dry-land simulated slalom course with marked trajectories (obtained from the Arrow 100 and proceed with ArcGIS Pro), and (<b>B</b>) the 25 runs completed and overlayed on the control trajectories. Colour coding is used to signify trajectory speed, where red is the fastest speed and green the slowest.</p>
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<p>Frequency distribution for (<b>A</b>) number of satellites used by device, (<b>B</b>) he horizontal root mean square (m), (<b>C</b>) the horizontal dilution of precision (HDOP), and (<b>D</b>) the 3D position dilution of precision, for every data point over the short (∎) more direct and long (∎) less direct trajectories for the dry-land slalom simulation.</p>
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<p>Dry-land slalom simulation test showing (<b>A</b>) the mean ± SD for the short (SC) more direct and long (LC) less direct trajectories, measured with the PNT solution, and (<b>B</b>) the percentage differences of the short and long trajectories as measured by the PNT solution compared to the known measured trajectory.</p>
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<p>Frequency distribution for (<b>A</b>) number of satellites used by device, (<b>B</b>) the Hrms (m), (<b>C</b>) the horizontal dilution of precision (HDOP), and (<b>D</b>) the 3D position dilution of precision (PDOP), for every data point for the on-water slalom simulation.</p>
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<p>Dependent variable comparisons between test mean data for each trial for (<b>A</b>) number of satellites used by device, (<b>B</b>) the Hrms (m), (<b>C</b>) the horizontal dilution of precision (HDOP), and (<b>D</b>) the 3D position dilution of precision (PDOP).</p>
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22 pages, 42906 KiB  
Article
Monitoring the Subsidence in Wan’an Town of Deyang Based on PS-InSAR Technology (Sichuan, China)
by Hongyi Guo, Antonio Miguel Martínez-Graña and José Angel González-Delgado
Sustainability 2024, 16(22), 10010; https://doi.org/10.3390/su162210010 - 16 Nov 2024
Viewed by 626
Abstract
In recent years, land subsidence has become a crucial factor affecting urban safety and sustainable development, especially in Wan’an Town. To accurately monitor and analyze the land subsidence in Wan’an Town, this study uses the PS-InSAR technique combined with an improved DEM for [...] Read more.
In recent years, land subsidence has become a crucial factor affecting urban safety and sustainable development, especially in Wan’an Town. To accurately monitor and analyze the land subsidence in Wan’an Town, this study uses the PS-InSAR technique combined with an improved DEM for detailed research on land subsidence in Wan’an Town. PS-InSAR, or Permanent Scatterer Interferometric SAR, is suitable for high-precision monitoring of surface deformation. The natural neighbor interpolation method optimizes DEM data, improving its spatial resolution and accuracy. In this study, multiple periods of SAR imagery data of Wan’an Town were collected and preprocessed through radiometric calibration, phase unwrapping, and other steps. Using the PS-InSAR technique, the phase information of permanent scatterers (PS points) on the surface was extracted to establish a deformation model and preliminarily analyze the land subsidence in Wan’an Town. Concurrently, the DEM data were optimized using the natural neighbor interpolation method to enhance its accuracy. Finally, the optimized DEM data were combined with the surface deformation information extracted through the PS-InSAR technique for a detailed analysis of the land subsidence in Wan’an Town. The research results indicate that the DEM data optimized by the natural neighbor interpolation method have higher accuracy and spatial resolution, providing a more accurate reflection of the topographical features of Wan’an Town. The research found that the optimized DEM provided a more accurate reflection of Wan’an Town’s topographical features. By combining PS-InSAR data, subsidence information from 2016 to 2024 was calculated. The study area showed varying degrees of subsidence, with rates ranging from 6 mm/year to 10 mm/year. Four characteristic deformation areas were analyzed for causes and influencing factors. The findings contribute to understanding urban land subsidence, guiding urban planning, and providing data support for geological disaster warning and prevention. Full article
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<p>Digital elevation model of the study area.</p>
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<p>Topography of the study area and radar image coverage area.</p>
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<p>Geology map of the study area.</p>
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<p>Elevation contrast chart.</p>
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<p>Workflow of PS processing.</p>
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<p>Spatial and temporal baseline distribution map.</p>
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<p>Differential interferogram.</p>
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<p>Spatial distribution of the average subsidence rate in the study area from 2016 to 2024.</p>
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<p>Settlement comparison diagram.</p>
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<p>Total subsidence in the study area from 2016 to 2024.</p>
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<p>Natural neighbor interpolation.</p>
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<p>Time-series deformation map of the study area from 2016 to 2024.</p>
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<p>GPS survey map. (<b>A</b>) Field survey map of target A, (<b>B</b>) field survey map of target B, (<b>C</b>) field survey map of target C, (<b>D</b>) field survey map of target D.</p>
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<p>(<b>A</b>) Deformation analysis of Deformation Target Area A. (<b>B</b>) Deformation analysis of Deformation Target Area B. (<b>C</b>) Deformation analysis of Deformation Target Area C. (<b>D</b>) Deformation analysis of Deformation Target Area D.</p>
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<p>(<b>A</b>) Deformation analysis of Deformation Target Area A. (<b>B</b>) Deformation analysis of Deformation Target Area B. (<b>C</b>) Deformation analysis of Deformation Target Area C. (<b>D</b>) Deformation analysis of Deformation Target Area D.</p>
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14 pages, 3246 KiB  
Article
Analysis of Mineral Composition and Isotope Ratio as Part of Chemical Profiles of Apples for Their Authentication
by Boris Krška, Martin Mészáros, Tomáš Bílek, Aleš Vávra, Jan Náměstek and Jiří Sedlák
Agronomy 2024, 14(11), 2703; https://doi.org/10.3390/agronomy14112703 - 16 Nov 2024
Viewed by 286
Abstract
One of the consequences of the globalisation of food markets is the effort enabling the control of food security and its origin. This might be traced by using different chemical composition analyses. However, for Central Europe, there is a lack of knowledge about [...] Read more.
One of the consequences of the globalisation of food markets is the effort enabling the control of food security and its origin. This might be traced by using different chemical composition analyses. However, for Central Europe, there is a lack of knowledge about the original reference values as well as their heterogeneity among the lands and countries. This study focused on characterizing the mineral profiles of apple tree fruits and comparing these profiles among different districts in Central Europe. The fruits of the apple cultivars ‘Gala’ and ‘Golden Delicious’ originated in the Czech Republic and Poland. The mineral and isotopic content of the apple fruit flesh was analysed using ICP-MS. The data were processed using the ANOVA test and compositely analysed using the PCA and LDA models. The results show relatively high variation in element distribution, particularly 87Sr/86Sr, Mn, Zn, Cu, Ca, P, and B, ranging between 20.6 and67.9% for both cultivars on average. However, their high variability within particular districts complicates the resolution of the LDA model. The reasons are linked to the geomorphological and pedological heterogeneity of the analysed districts as well as the particular sensitivity of the set of chosen primers to agronomic practices and tree performance. For this region, only partial separation among districts could be obtained by P, Ca, and Cu content, as well as the isotopic ratio of 10B/11B. However, the resolution of the geographical discrimination needs to be improved by an enhanced set of primers, the use of more precise analytical techniques for the Sr isotopic ratio, or by multiple chemical analyses. Furthermore, the heterogeneity of the analysed districts could be tackled by more detailed analyses at the level of micro-regions. Full article
(This article belongs to the Section Horticultural and Floricultural Crops)
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<p>Contribution of analysed mineral elements and isotope ratios (<b>A</b>–<b>C</b>), and the PCA of the mineral content in apple cultivar ‘Gala’ with different geographical origins (<b>D</b>–<b>F</b>) according to the sampled districts of the Czech Republic and Poland. Hereby, the full model is represented by (<b>A</b>,<b>D</b>), the reduced model by (<b>B</b>,<b>E</b>), and the isotopic ration model by (<b>C</b>,<b>F</b>).</p>
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<p>Eigenvalue of the components of PCA data analysis shown in <a href="#agronomy-14-02703-f001" class="html-fig">Figure 1</a> and the correlation coefficients of the relationships among the particular elements and isotope ratios in the first five PCA components for (<b>A</b>) the full model and (<b>B</b>) the reduced model.</p>
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<p>Contribution of analysed mineral elements and isotope ratios (<b>A</b>–<b>C</b>), and the PCA of the mineral content in apple cultivar ‘Golden Delicious’ with different geographical origins (<b>D</b>–<b>F</b>) according to the sampled districts of the Czech Republic and Poland. Hereby, the full model is represented by (<b>A</b>,<b>D</b>), the reduced model by (<b>B</b>,<b>E</b>), and the isotopic ration model by (<b>C</b>,<b>F</b>).</p>
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<p>Eigenvalues of the components of PCA data analysis shown in <a href="#agronomy-14-02703-f003" class="html-fig">Figure 3</a>, and the correlation coefficients of the relationships among the particular elements and isotope ratios in the first five PCA components for (<b>A</b>) the full model and (<b>B</b>) the reduced model.</p>
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17 pages, 12206 KiB  
Article
Smart Monitoring Method for Land-Based Sources of Marine Outfalls Based on an Improved YOLOv8 Model
by Shicheng Zhao, Haolan Zhou and Haiyan Yang
Water 2024, 16(22), 3285; https://doi.org/10.3390/w16223285 - 15 Nov 2024
Viewed by 399
Abstract
Land-based sources of marine outfalls are a major source of marine pollution. The monitoring of land-based sources of marine outfalls is an important means for marine environmental protection and governance. Traditional on-site manual monitoring methods are inefficient, expensive, and constrained by geographic conditions. [...] Read more.
Land-based sources of marine outfalls are a major source of marine pollution. The monitoring of land-based sources of marine outfalls is an important means for marine environmental protection and governance. Traditional on-site manual monitoring methods are inefficient, expensive, and constrained by geographic conditions. Satellite remote sensing spectral analysis methods can only identify pollutant plumes and are affected by discharge timing and cloud/fog interference. Therefore, we propose a smart monitoring method for land-based sources of marine outfalls based on an improved YOLOv8 model, using unmanned aerial vehicles (UAVs). This method can accurately identify and classify marine outfalls, offering high practical application value. Inspired by the sparse sampling method in compressed sensing, we incorporated a multi-scale dilated attention mechanism into the model and integrated dynamic snake convolutions into the C2f module. This approach enhanced the model’s detection capability for occluded and complex-feature targets while constraining the increase in computational load. Additionally, we proposed a new loss calculation method by combining Inner-IoU (Intersection over Union) and MPDIoU (IoU with Minimum Points Distance), which further improved the model’s regression speed and its ability to predict multi-scale targets. The final experimental results show that the improved model achieved an mAP50 (mean Average Precision at 50) of 87.0%, representing a 3.4% increase from the original model, effectively enabling the smart monitoring of land-based marine discharge outlets. Full article
(This article belongs to the Section Oceans and Coastal Zones)
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<p>Zhanjiang city outlets point map. (<b>a</b>) “gully”, (<b>b</b>) “weir”, (<b>c</b>) “pipe”, (<b>d</b>) “culvert”, (<b>e</b>) “gully”, (<b>f</b>) “weir”, (<b>g</b>) “pipe”, (<b>h</b>) “culvert”.</p>
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<p>YOLOv8 model structure.</p>
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<p>MSDA mechanism structure. The red points represent the key positions of the convolutional kernel, the yellow area shows the dilation of the kernel at <math display="inline"><semantics> <mrow> <mi mathvariant="normal">r</mi> <mo>=</mo> <mn>1</mn> </mrow> </semantics></math>, the blue area shows the dilation at <math display="inline"><semantics> <mrow> <mi mathvariant="normal">r</mi> <mo>=</mo> <mn>2</mn> </mrow> </semantics></math>, and the green area shows the dilation at <math display="inline"><semantics> <mrow> <mi mathvariant="normal">r</mi> <mo>=</mo> <mn>3</mn> </mrow> </semantics></math>.</p>
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<p>C2f module structure.</p>
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<p>DSConv selectable receptive fields. The blue line represents the continuous shift of the convolutional kernel in the horizontal direction, while the red line represents the continuous shift of the convolutional kernel in the vertical direction.</p>
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<p>Inner-MPDIoU diagram.</p>
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<p>(<b>a</b>) Anchor box category number statistics, (<b>b</b>) Anchor box position statistics. The color of Anchor box in (<b>b</b>) belongs to the same category as that in (<b>a</b>).</p>
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<p>(<b>a</b>) Normalized confusion matrices for YOLOv8 model, (<b>b</b>) normalized confusion matrices for YOLOv8+MSDA model.</p>
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<p>(<b>a</b>) YOLOv8 model’s predicted results, (<b>b</b>) our model’s predicted results.</p>
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<p>(<b>a</b>) P–R curve of the improved model, (<b>b</b>) P–R curve of the improved model after transfer learning.</p>
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<p>Model training process.</p>
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26 pages, 11851 KiB  
Article
Development and Evaluation of Machine Learning Models for Air-to-Land Temperature Conversion Using the Newly Established Kunlun Mountain Gradient Observation System
by Yongkang Li, Qing He, Yongqiang Liu, Amina Maituerdi, Yang Yan and Jiao Tan
Land 2024, 13(11), 1903; https://doi.org/10.3390/land13111903 - 13 Nov 2024
Viewed by 386
Abstract
Mountainous land types are characterized by a scarcity of observational data, particularly in remote areas such as the Kunlun Mountains, where conventional Automatic Weather Stations (AWSs) typically do not record land surface temperature (LST) data. This study aims to develop and evaluate models [...] Read more.
Mountainous land types are characterized by a scarcity of observational data, particularly in remote areas such as the Kunlun Mountains, where conventional Automatic Weather Stations (AWSs) typically do not record land surface temperature (LST) data. This study aims to develop and evaluate models for converting air temperature (TA) to LST using newly established meteorological station data from the Kunlun Mountain Gradient Observation System, thereby providing time-continuous LST data for AWSs. We constructed a conceptual model to explore the relationship between 1.5 m TA and LST and instantiated it using three machine learning algorithms: Support Vector Machine (SVR), Convolutional Neural Network (CNN), and CatBoost. The results demonstrated that the CatBoost algorithm outperformed the others under complex terrain and climatic conditions, achieving a coefficient of determination (R2) of 0.997 and the lowest root mean square error (RMSE) of 0.627 °C, indicating superior robustness and accuracy. Consequently, CatBoost was selected as the optimal model. Additionally, this study analyzed the spatiotemporal distribution characteristics of cloud cover in the Kunlun Mountain region using the MOD11A1 product and assessed the uncertainties introduced by the 8-day average compositing method of the MOD11A2 product. The results revealed significant discrepancies between the monthly average LST derived from polar-orbiting satellites and the hourly composite monthly LST measured on-site or under ideal cloud-free conditions. These differences were particularly pronounced in high-altitude regions (4000 m and above), with the greatest differences occurring in winter, reaching up to 10.2 °C. These findings emphasize the importance of hourly LST calculations based on AWSs for accurately assessing the spatiotemporal characteristics of LST in the Kunlun Mountains, thus providing more precise spatiotemporal support for remote sensing applications in high-altitude regions. Full article
(This article belongs to the Section Land Innovations – Data and Machine Learning)
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<p>Overview of study area.</p>
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<p>Flowchart of data processing steps. Note: The red text section represents the Derivative Data constructed based on the conceptual model proposed in this article.</p>
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<p>Comparison of 10-fold cross-validation of three machine learning algorithms for whether <span class="html-italic">at_diff_up</span> participates or not. (<b>a</b>) is a box plot of RMSE against the Pearson correlation coefficient, (<b>b</b>) is the box plot of significance test probability p against the Pearson correlation coefficient. Note: The feature variable denoted by <b><span class="html-italic">at_diff_up</span></b> represents the difference between the current hourly 1.5 m atmospheric temperature and the corresponding value from the preceding hour.</p>
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<p>Importance box graph of Catboost, the corresponding optimal parameters based on the grid search, and the model validation accuracy metric. Note: ** represents significance through a <span class="html-italic">p</span> &lt; 0.01 correlation test.</p>
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<p>Comparison of Supersite-based measured LST with Catboost-simulated LST across the Kunlun Mountain Vertical Gradient. Note: The elevations of Yeyike, Kalasai, Akesusai, Khunjerab, and Wolonggang are 2275 m, 3013 m, 3934.7 m, 4700 m, and 5896 m, respectively.</p>
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<p>Comparison of Supersite-based measured LST with Catboost-simulated LST across the Kunlun Mountain Vertical Gradient. Note: The elevations of Yeyike, Kalasai, Akesusai, Khunjerab, and Wolonggang are 2275 m, 3013 m, 3934.7 m, 4700 m, and 5896 m, respectively.</p>
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<p>Comparison of Supersite-based measured LST with Catboost-simulated LST across the Kunlun Mountain Vertical Gradient. Note: The elevations of Yeyike, Kalasai, Akesusai, Khunjerab, and Wolonggang are 2275 m, 3013 m, 3934.7 m, 4700 m, and 5896 m, respectively.</p>
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<p>Accuracy evaluation of the CatBoost model across different seasons at five supersites. Panels (<b>a</b>,<b>b</b>) represent the coefficient of determination and the root mean square error of the CatBoost model, respectively.</p>
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<p>Cross-validated Taylor diagrams of Suomi NPP’s VIIRS LST versus Catboost-simulated LST for spring, summer, autumn, winter, daytime, nighttime, and yearly comparisons.</p>
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<p>Cross-validated Taylor diagrams of Terra and Aqua MODIS LST versus Catboost-simulated LST for spring, summer, autumn, winter, daytime, nighttime, and yearly comparisons.</p>
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<p>Spatial distribution of MOD11A1 data availability under cloud influence from 2000 to 2023. Note: (<b>a</b>–<b>g</b>) represent the spatial distribution of data availability for spring, summer, autumn, winter, daytime, nighttime, and the entire year, respectively. (<b>h</b>) represents the spatial distribution of elevation.</p>
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<p>Spatial distribution of MOD11A1 data availability under cloud influence from 2000 to 2023. Note: (<b>a</b>–<b>g</b>) represent the spatial distribution of data availability for spring, summer, autumn, winter, daytime, nighttime, and the entire year, respectively. (<b>h</b>) represents the spatial distribution of elevation.</p>
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<p>Time series comparison of four datasets—8-Day Composite MOD11A2 LST, Site LST in Terra Scan Time, Site LST No Clouds, and Site LST 24h—based on observations from Kunlun Mountain Gradient Stations. Note: (<b>a</b>) Yeyike station represents the 2000 m gradient, (<b>b</b>) Kalasai represents the 3000 m gradient, (<b>c</b>) Akesuaai represents the 4000 m gradient, (<b>d</b>) Khunjurab represents the 5000 m gradient, and (<b>e</b>) Wolonggang represents the 6000 m gradient.</p>
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<p>Time series comparison of four datasets—8-Day Composite MOD11A2 LST, Site LST in Terra Scan Time, Site LST No Clouds, and Site LST 24h—based on observations from Kunlun Mountain Gradient Stations. Note: (<b>a</b>) Yeyike station represents the 2000 m gradient, (<b>b</b>) Kalasai represents the 3000 m gradient, (<b>c</b>) Akesuaai represents the 4000 m gradient, (<b>d</b>) Khunjurab represents the 5000 m gradient, and (<b>e</b>) Wolonggang represents the 6000 m gradient.</p>
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<p>Comparative analysis of time series data from four distinct datasets—derived from monthly composite MOD11A2 LST and site-specific LST measurements at the Kunlun Mountain Gradient LST Observatory. The datasets include MOD11A2 LST, Site LST in Terra Scan Time, Site LST No Clouds, and Site LST 24h. Note: (<b>a</b>) Yeyike station represents the 2000 m gradient, (<b>b</b>) Kalasai represents the 3000 m gradient, (<b>c</b>) Akesuaai represents the 4000 m gradient, (<b>d</b>) Khunjurab represents the 5000 m gradient, and (<b>e</b>) Wolonggang represents the 6000 m gradient.</p>
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19 pages, 16510 KiB  
Article
Mapping Crop Types for Beekeepers Using Sentinel-2 Satellite Image Time Series: Five Essential Crops in the Pollination Services
by Navid Mahdizadeh Gharakhanlou, Liliana Perez and Nico Coallier
Remote Sens. 2024, 16(22), 4225; https://doi.org/10.3390/rs16224225 - 13 Nov 2024
Viewed by 430
Abstract
Driven by the widespread adoption of deep learning (DL) in crop mapping with satellite image time series (SITS), this study was motivated by the recent success of temporal attention-based approaches in crop mapping. To meet the needs of beekeepers, this study aimed to [...] Read more.
Driven by the widespread adoption of deep learning (DL) in crop mapping with satellite image time series (SITS), this study was motivated by the recent success of temporal attention-based approaches in crop mapping. To meet the needs of beekeepers, this study aimed to develop DL-based classification models for mapping five essential crops in pollination services in Quebec province, Canada, by using Sentinel-2 SITS. Due to the challenging task of crop mapping using SITS, this study employed three DL-based models, namely one-dimensional temporal convolutional neural networks (CNNs) (1DTempCNNs), one-dimensional spectral CNNs (1DSpecCNNs), and long short-term memory (LSTM). Accordingly, this study aimed to capture expert-free temporal and spectral features, specifically targeting temporal features using 1DTempCNN and LSTM models, and spectral features using the 1DSpecCNN model. Our findings indicated that the LSTM model (macro-averaged recall of 0.80, precision of 0.80, F1-score of 0.80, and ROC of 0.89) outperformed both 1DTempCNNs (macro-averaged recall of 0.73, precision of 0.74, F1-score of 0.73, and ROC of 0.85) and 1DSpecCNNs (macro-averaged recall of 0.78, precision of 0.77, F1-score of 0.77, and ROC of 0.88) models, underscoring its effectiveness in capturing temporal features and highlighting its suitability for crop mapping using Sentinel-2 SITS. Furthermore, applying one-dimensional convolution (Conv1D) across the spectral domain demonstrated greater potential in distinguishing land covers and crop types than applying it across the temporal domain. This study contributes to providing insights into the capabilities and limitations of various DL-based classification models for crop mapping using Sentinel-2 SITS. Full article
(This article belongs to the Section AI Remote Sensing)
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<p>The flowchart of the research methodology.</p>
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<p>Geographic location of the study area with a true-color median composite of Sentinel-2 satellite imagery generated for 1–10 April 2021.</p>
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<p>The macro-average of the F1-score for the 100 designed architectures on the validation dataset for (<b>a</b>) 1DTempCNN, (<b>b</b>) 1DSpecCNN, and (<b>c</b>) LSTM models.</p>
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<p>The macro-average of the F1-score for the 100 designed architectures on the validation dataset for (<b>a</b>) 1DTempCNN, (<b>b</b>) 1DSpecCNN, and (<b>c</b>) LSTM models.</p>
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<p>The 1DTempCNN architecture with optimal performance.</p>
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<p>The 1DSpecCNN architecture with optimal performance.</p>
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<p>The LSTM architecture with optimal performance.</p>
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<p>(<b>a</b>) The ground reference map; and (<b>b</b>) the LSTM-provided map of land cover and crop type across the entire study area.</p>
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<p>Confusion matrix of the top-performing DL model (i.e., LSTM) in predicting land cover and crop type on the test dataset.</p>
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24 pages, 4045 KiB  
Article
The Impact of Land-Use Carbon Efficiency on Ecological Resilience—The Moderating Role of Heterogeneous Environmental Regulations
by Wei Zhang, Zetian Wang and Shaohua Wang
Sustainability 2024, 16(22), 9842; https://doi.org/10.3390/su16229842 - 12 Nov 2024
Viewed by 449
Abstract
China attaches great importance to land use and ecological civilization; hence, clarifying the relationship of land use on ecological resilience is crucial for urban development. The aim of this paper is to study the impact of land-use carbon efficiency on ecological resilience and [...] Read more.
China attaches great importance to land use and ecological civilization; hence, clarifying the relationship of land use on ecological resilience is crucial for urban development. The aim of this paper is to study the impact of land-use carbon efficiency on ecological resilience and the moderating role played by different environmental regulatory policies between the two, with the aim of providing a research basis and decision-making reference for the country’s ecological high-quality development by proposing suggestions for different subjects based on the results of this study. Taking 30 provinces and cities in mainland China from 2009 to 2022 as samples, the authors constructed an indicator system to measure their ecological resilience using the entropy method, measured their land-use carbon efficiency using the super SBM, and verified the mechanism of land-use carbon efficiency on ecological resilience by using the bidirectional fixed-effects model. Robustness and endogeneity tests confirmed the validity of the regression results. The following is a summary of this study’s findings: (1) Land-use carbon efficiency can enhance ecological resilience through various mechanisms such as scale promotion, structural upgrading, and technological progress. (2) Regional research shows that different regions have distinct effects of land-use carbon efficiency on ecological resilience. The northeastern region shows a non-significant inhibitory effect, whereas the eastern, middle, and western regions show varying degrees of promotion effects. Land-use carbon efficiency contributes to increased ecological resilience in resource-based and non-resource-based provinces, with resource-based provinces witnessing a greater increase in ecological resilience. The effects of land-use carbon efficiency on different aspects of ecological resilience are diverse, with ecosystem resistance and recovery being empowered. However, the precise mechanism through which ecosystem adaptability influences ecological resilience remains unclear. (3) Moreover, there is variation in the moderating impact of environmental legislation. Command-and-control environmental regulation impedes the positive impact of land-use carbon efficiency, and market-incentive environmental regulation strengthens their relationship, while spontaneous-participation environmental regulation does not significantly enhance their connection. It provides a new theoretical perspective for the study of ecological resilience, deepens the understanding of ecological resilience, and provides theoretical support for enhancing the resilience of ecosystems. Full article
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<p>Mechanisms of land-use carbon efficiency on ecological resilience map.</p>
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<p>Kernel density estimates of ecological resilience development levels in China and four regions.</p>
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21 pages, 29489 KiB  
Article
Early Sweet Potato Plant Detection Method Based on YOLOv8s (ESPPD-YOLO): A Model for Early Sweet Potato Plant Detection in a Complex Field Environment
by Kang Xu, Wenbin Sun, Dongquan Chen, Yiren Qing, Jiejie Xing and Ranbing Yang
Agronomy 2024, 14(11), 2650; https://doi.org/10.3390/agronomy14112650 - 11 Nov 2024
Viewed by 421
Abstract
Traditional methods of pest control for sweet potatoes cause the waste of pesticides and land pollution, but the target detection algorithm based on deep learning can control the precise spraying of pesticides on sweet potato plants and prevent most pesticides from entering the [...] Read more.
Traditional methods of pest control for sweet potatoes cause the waste of pesticides and land pollution, but the target detection algorithm based on deep learning can control the precise spraying of pesticides on sweet potato plants and prevent most pesticides from entering the land. Aiming at the problems of low detection accuracy of sweet potato plants and the complex of target detection models in natural environments, an improved algorithm based on YOLOv8s is proposed, which can accurately identify early sweet potato plants. First, this method uses an efficient network model to enhance the information flow in the channel, obtain more effective global features in the high-level semantic structure, and reduce model parameters and computational complexity. Then, cross-scale feature fusion and the general efficient aggregation architecture are used to further enhance the network feature extraction capability. Finally, the loss function is replaced with InnerFocaler-IoU (IFIoU) to improve the convergence speed and robustness of the model. Experimental results showed that the mAP0.5 and model size of the improved network reached 96.3% and 7.6 MB. Compared with the YOLOv8s baseline network, the number of parameters was reduced by 67.8%, the amount of computation was reduced by 53.1%, and the mAP0.5:0.95 increased by 3.5%. The improved algorithm has higher detection accuracy and a lower parameter and calculation amount. This method realizes the accurate detection of sweet potato plants in the natural environment and provides technical support and guidance for reducing pesticide waste and pesticide pollution. Full article
(This article belongs to the Section Precision and Digital Agriculture)
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<p>Sample images of sweet potato.</p>
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<p>YOLOv8 network structure.</p>
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<p>ESPPD-YOLO structure.</p>
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<p>Efficient model based on coordinate attention (EMCA). (<b>a</b>) Inverted residual mobile block (iRMB). (<b>b</b>) The iRMB based on the coordinate attention mechanism (RMBCA). (<b>c</b>) EMCA structure.</p>
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<p>Coordinate attention mechanism.</p>
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<p>EFFF structure.</p>
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<p>GELAN structure.</p>
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<p>Description of Inner-IoU.</p>
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<p>ESPPD-YOLO model training results.</p>
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<p>The mAP curves for different improvement stages.</p>
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<p>Detection results of different models at horizontal angles. (<b>a</b>) Faster R-CNN. (<b>b</b>) SSD. (<b>c</b>) YOLOv5s. (<b>d</b>) YOLOv7. (<b>e</b>) YOLOv8s. (<b>f</b>) YOLOv9s. (<b>g</b>) YOLOv10s. (<b>h</b>) ESPPD-YOLO. The red rectangle indicates the detection frame, the yellow ellipse indicates missed detection, the black ellipse indicates that one sweet potato plant is identified as two or more, the purple ellipse indicates incomplete detection, and the blue ellipse indicates that two sweet potato plants are identified as one.</p>
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<p>Detection results of different models at horizontal angles. (<b>a</b>) Faster R-CNN. (<b>b</b>) SSD. (<b>c</b>) YOLOv5s. (<b>d</b>) YOLOv7. (<b>e</b>) YOLOv8s. (<b>f</b>) YOLOv9s. (<b>g</b>) YOLOv10s. (<b>h</b>) ESPPD-YOLO. The red rectangle indicates the detection frame, the yellow ellipse indicates missed detection, the black ellipse indicates that one sweet potato plant is identified as two or more, the purple ellipse indicates incomplete detection, and the blue ellipse indicates that two sweet potato plants are identified as one.</p>
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<p>Detection results of different models at tilt angles. (<b>a</b>) Faster R-CNN. (<b>b</b>) SSD. (<b>c</b>) YOLOv5s. (<b>d</b>) YOLOv7. (<b>f</b>) YOLOv9s. (<b>g</b>) YOLOv10s. (<b>h</b>) ESPPD-YOLO. The red rectangle indicates the detection frame, the yellow ellipse indicates missed detection, the black ellipse indicates that one sweet potato plant is identified as two or more, the purple ellipse indicates incomplete detection, and the blue ellipse indicates that two sweet potato plants are identified as one.</p>
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<p>Detection results of different models at tilt angles. (<b>a</b>) Faster R-CNN. (<b>b</b>) SSD. (<b>c</b>) YOLOv5s. (<b>d</b>) YOLOv7. (<b>f</b>) YOLOv9s. (<b>g</b>) YOLOv10s. (<b>h</b>) ESPPD-YOLO. The red rectangle indicates the detection frame, the yellow ellipse indicates missed detection, the black ellipse indicates that one sweet potato plant is identified as two or more, the purple ellipse indicates incomplete detection, and the blue ellipse indicates that two sweet potato plants are identified as one.</p>
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<p>Heat map. (<b>a</b>,<b>c</b>) are heat maps of ESPPD-YOLO. (<b>b</b>,<b>d</b>) are heat maps of YOLOv8s. Hot tones (such as red and yellow) represent high-importance areas, and cold tones (such as blue and green) represent low-importance areas.</p>
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27 pages, 21954 KiB  
Article
Long-Term Ground Deformation Monitoring and Quantitative Interpretation in Shanghai Using Multi-Platform TS-InSAR, PCA, and K-Means Clustering
by Yahui Chong and Qiming Zeng
Remote Sens. 2024, 16(22), 4188; https://doi.org/10.3390/rs16224188 - 10 Nov 2024
Viewed by 631
Abstract
Ground subsidence in urban areas is mainly due to natural or anthropogenic activities, and it seriously threatens the healthy and sustainable development of the city and the security of individuals’ lives and assets. Shanghai is a megacity of China, and it has a [...] Read more.
Ground subsidence in urban areas is mainly due to natural or anthropogenic activities, and it seriously threatens the healthy and sustainable development of the city and the security of individuals’ lives and assets. Shanghai is a megacity of China, and it has a long history of ground subsidence due to the overexploitation of groundwater and urban expansion. Time Series Synthetic Aperture Radar Interferometry (TS-InSAR) is a highly effective and widely used approach for monitoring urban ground deformation. However, it is difficult to obtain long-term (such as over 10 years) deformation results using single-platform SAR satellite in general. To acquire long-term surface deformation monitoring results, it is necessary to integrate data from multi-platform SAR satellites. Furthermore, the deformations are the result of multiple factors that are superimposed, and relevant studies that quantitatively separate the contributions from different driving factors to subsidence are rare. Moreover, the time series cumulative deformation results of massive measurement points also bring difficulties to the deformation interpretation. In this study, we have proposed a long-term surface deformation monitoring and quantitative interpretation method that integrates multi-platform TS-InSAR, PCA, and K-means clustering. SAR images from three SAR datasets, i.e., 19 L-band ALOS-1 PALSAR, 22 C-band ENVISAT ASAR, and 20 C-band Sentinel-1A, were used to retrieve annual deformation rates and time series deformations in Shanghai from 2007 to 2018. The monitoring results indicate that there is serious uneven settlement in Shanghai, with a spatial pattern of stability in the northwest and settlement in the southeast of the study area. Then, we selected Pudong International Airport as the area of interest and quantitatively analyzed the driving factors of land subsidence in this area by using PCA results, combining groundwater exploitation and groundwater level change, precipitation, temperature, and engineering geological and human activities. Finally, the study area was divided into four sub-regions with similar time series deformation patterns using the K-means clustering. This study helps to understand the spatiotemporal evolution of surface deformation and its driving factors in Shanghai, and provides a scientific basis for the formulation and implementation of precise prevention and control strategies for land subsidence disasters, and it can also provide reference for monitoring in other urban areas. Full article
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<p>The geographic location of Shanghai and spatial coverage of SAR datasets.</p>
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<p>SAR image acquisition dates and the spatial baselines of three SAR sensors with respect to the reference image for each sensor. The star represents the reference image of each sensor.</p>
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<p>The data processing flowchart of this study.</p>
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<p>Spatial–temporal baseline configurations of SAR datasets: (<b>a</b>) ALOS-1 PALSAR, (<b>b</b>) ENVISAT ASAR, and (<b>c</b>) Sentinel-1A.</p>
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<p>Annual LOS deformation rates obtained from three SAR datasets: (<b>a</b>) ALOS-1 PALSAR, (<b>b</b>) ENVISAT ASAR, and (<b>c</b>) Sentinel-1A.</p>
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<p>(<b>a</b>) Average vertical deformation rate and (<b>b</b>) time series cumulative surface deformation obtained from ALOS-ENVISAT-S1A fusion results for Shanghai from 2007 to 2018.</p>
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<p>Comparisons of long-term time series cumulative deformation obtained by ALOS-ENVISAT-S1A and self-weight consolidation settlement model: (<b>a</b>) P1, (<b>b</b>) P2, (<b>c</b>) P3, and (<b>d</b>) P4.</p>
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<p>(<b>a</b>) Scatterplot and (<b>b</b>) correlation coefficient graph of TS-InSAR deformation rate and field measurements.</p>
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<p>Landsat TM/ETM optical images of Pudong International Airport for the following years: (<b>a</b>) 2007, (<b>b</b>) 2010, (<b>c</b>) 2015, and (<b>d</b>) 2018.</p>
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<p>Vertical annual deformation rates of Pudong International Airport during (<b>a</b>) 2007–2010 and (<b>b</b>) 2015–2018 (base image is from Google Map).</p>
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<p>PCA result derived from ALOS-ENVISAT: (<b>a</b>) variance explained by the PC 1–4 and (<b>b</b>) eigenvectors obtained from PC 1–4.</p>
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<p>PCA result derived from Sentinel-1A: (<b>a</b>) variance explained by the PC 1–4 and (<b>b</b>) eigenvectors obtained from PC 1–4.</p>
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<p>Correlation map between eigenvectors of PC 1–3 obtained from ALOS-ENVISAT and temperature, groundwater level, precipitation, groundwater extraction volume, and impervious surface area: (<b>a</b>) PC1, (<b>b</b>) PC2, and (<b>c</b>) PC3.</p>
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<p>Correlation map between eigenvectors of PC 1–2 obtained from Sentinel-1A and temperature, groundwater level, precipitation, groundwater extraction volume, and impervious surface area: (<b>a</b>) PC and (<b>b</b>) PC2.</p>
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<p>The deformation rate of Pudong International Airport on the east–west profile line: (<b>a</b>) AB profile and (<b>b</b>) CD profile.</p>
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<p>P1–P7 time series cumulative deformation acquired by ALOS-ENVISAT in the runway and terminal areas.</p>
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<p>Q1–Q7 time series cumulative deformation acquired by Sentinel-1A in the runway and terminal areas.</p>
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<p>K-means clustering results of the long-term time series deformation obtained from ALOS-ENVISAT-S1A: (<b>a</b>) spatial distribution of each cluster, (<b>b</b>) percentage of each cluster, (<b>c</b>) time series of cumulative deformation of the cluster center, and (<b>d</b>) violin map of the annual deformation velocity for each cluster.</p>
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