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29 pages, 56805 KiB  
Article
Establishing a Geo-Database for Drinking Water and Its Delivery and Storage Components with an Object-Based Approach
by Yakup Emre Coruhlu and Sait Semih Altas
Water 2024, 16(12), 1753; https://doi.org/10.3390/w16121753 - 20 Jun 2024
Cited by 1 | Viewed by 975
Abstract
Infrastructure facilities that serve the city as a whole and should be considered as a whole should be built in an orderly and planned manner, just as cities are. Infrastructure facilities become obsolete over time. Aging infrastructure facilities may become unserviceable over time. [...] Read more.
Infrastructure facilities that serve the city as a whole and should be considered as a whole should be built in an orderly and planned manner, just as cities are. Infrastructure facilities become obsolete over time. Aging infrastructure facilities may become unserviceable over time. When the need for maintenance and repair arises, it is mandatory to renew or replace infrastructure facilities. In this case, necessary maintenance/repair and renovation works should be completed as soon as possible. These infrastructure facilities may not be transferred to maps in the digital environment and may often be managed with person-oriented information, not institutional. There is a problem for decision makers, namely, that the construction, maintenance, repair and governance of infrastructure facilities cannot be carried out systematically, on time and effectively. The only way to provide such a service is through the combined use of today’s informatics, Geographical Information System (GIS) and Global Navigation Satellite System (GNSS) technologies, unlike the classical methods of the past. The aim of the study is to effectively manage the scarce resource of drinking water and its facilities, which are an important component of infrastructure facilities, with a method that uses current mapping technologies and informatics facilities. Especially after Infrastructure for Spatial Information (INSPIRE) and the transformation of Land Administration Domain Model (LADM) to the International Organization for Standardization (ISO) standard, Turkish National Geographic Information System (TNGIS) studies and many academic studies carried out in Türkiye have been modelled with Unified Modelling Language (UML) diagrams in accordance with LADM. Similarly, within the scope of this study, UML diagrams were prepared, and then a GIS database was established. Thanks to field workers, chiefs, engineers and others working on water pipelines, all necessary data, classic, as-built and digital, were gathered. These were collected in different ways in order to conduct spatial and non-spatial analysis in the study area of Trabzon. The most important result from the study is that the entire drinking water infrastructure of Trabzon has been transferred to the system in a structure that allows spatial queries, ensuring that damage detection on water components, maintenance and repair processes are carried out in the shortest time and at the lowest cost. The investigation and application of a sensor-integrated GIS-aided system, making it possible to control and monitor the use of lost and illegal water to be controlled as well as inform consumers who will be affected by possible maintenance and repair, is recommended. Full article
(This article belongs to the Section Water Resources Management, Policy and Governance)
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<p>Methodology and study plan.</p>
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<p>(<b>a</b>) Adapted from TNGIS package diagram of infrastructure theme and simplified [<a href="#B27-water-16-01753" class="html-bibr">27</a>]. (<b>b</b>) Adapted from water network class diagram and simplified [<a href="#B27-water-16-01753" class="html-bibr">27</a>].</p>
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<p>Logical representation of a drinking water distribution system.</p>
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<p>Example of digital operation plan of the Pelitli neighbourhood water network.</p>
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<p>Vakfıkebir drinking water lines: paper map produced in 2015.</p>
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<p>Visualization of drinking water information system with UML use-case diagram.</p>
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<p>Visualization of drinking water information system with UML activity diagram.</p>
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<p>“TNGIS.AY_WATER_TISCBS” Model Data Sets.</p>
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<p>Visualization of drinking water information system with UML class diagram.</p>
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<p>The study area.</p>
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<p>Digitized drinking water geo-database.</p>
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<p>Failure and infrastructure geographical data.</p>
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<p>Failure street map of the pilot area.</p>
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<p>Failure density map of the pilot region.</p>
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<p>Map of structures associated with damaged lines.</p>
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<p>An example map showing the debt situation of consumers.</p>
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<p>An example map showing the water consumption of buildings and the year of construction of the lines.</p>
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<p>Water components, membership and consumption. (<b>a</b>) Water components. (<b>b</b>) Membership and consumption.</p>
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33 pages, 6831 KiB  
Article
Dynamic Land-Use Patterns and the Associated Impacts on Ecosystem Services Value in Putian City, China
by Qingxia Peng, Dongqing Wu, Wenxiong Lin, Shuisheng Fan and Kai Su
Appl. Sci. 2024, 14(11), 4554; https://doi.org/10.3390/app14114554 - 25 May 2024
Viewed by 1001
Abstract
Human actions have led to consistent and profound alterations in land use, which in turn have had a notable effect on the services provided by ecosystems. In this research, the Google Earth Engine (GEE) was initially employed to perform a supervised classification of [...] Read more.
Human actions have led to consistent and profound alterations in land use, which in turn have had a notable effect on the services provided by ecosystems. In this research, the Google Earth Engine (GEE) was initially employed to perform a supervised classification of Landsat satellite images from 2000 to 2020, which allowed us to obtain land-use data for Putian City, China. Next, the geo-informatic Tupu model and the revised valuation model were used to explore the spatial attributes and ecological effects of land-use changes (LUCs). Subsequently, EEH (eco-economic harmony), ESTD (ecosystem services tradeoffs and synergies degree index), and ESDA (exploratory spatial data analysis) methods were employed to further analyze the coordination level, trade-offs, synergies, and spatial patterns of ecological-economic system development. The findings revealed that: (1) The land-use composition in Putian City was predominantly cultivated land and forest land, with other types of land intermixed. Concurrently, there was an ongoing trend of expansion in urban areas. (2) ESV in Putian City exhibited an upward trend, increasing from 15.4 billion CNY to 23.1 billion CNY from 2000 to 2020. (3) ESV exhibited an imbalance in spatial distribution, with high-high agglomeration areas concentrated in the central part of Putian City and the coastal region of Hanjiang District, while low-low agglomeration areas were prevalent in Xianyou County in the southwest, Xiuyu District along the coast, and Licheng District in the urban center. (4) Synergistic relationships among ESs predominated, though the trade-off relationship showed a tendency to expand. (5) The ecological environment and economic progress in Putian City collectively faced a region of potential risk. The findings of this study are intended to serve as a guide for improving the distribution of land resources and for developing strategies that ensure the sustainable development of the region’s socio-economic framework. Full article
(This article belongs to the Special Issue Ecosystems and Landscape Ecology)
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<p>Location of the study area. Sources: Drawings from this study.</p>
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<p>Land-use structure in Putian City during 2000–2020. Sources: Drawings from this study.</p>
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<p>Tupu of LUCs in Putian City from 2000 to 2020. Sources: Drawings from this study.</p>
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<p>Land-use rising Tupu in Putian City from 2000 to 2020. Sources: Drawings from this study.</p>
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<p>Land-use falling Tupu in Putian City from 2000 to 2020. Sources: Drawings from this study.</p>
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<p>Structure comparison of ESV in Putian City from 2000 to 2020. Note: Abbreviations are the same as those given in <a href="#applsci-14-04554-t001" class="html-table">Table 1</a>. Sources: Drawings from this study.</p>
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<p>Ecosystem services value of districts or counties in Putian from 2000 to 2020. Sources: Drawings from this study.</p>
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<p>Spatial differentiation of ESV in Putian from 2000 to 2020. Sources: Drawings from this study.</p>
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<p>LISA aggregation of ESV intensity in Putian City at the grid scale from 2000 to 2020. Sources: Drawings from this study.</p>
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<p>ESTD in Putian City from 2000 to 2020. Note: Abbreviations are the same as those given in <a href="#applsci-14-04554-t001" class="html-table">Table 1</a>. Sources: Drawings from this study.</p>
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<p>SCES in Putian from 2000 to 2020. Note: Abbreviations are the same as those given in <a href="#applsci-14-04554-t001" class="html-table">Table 1</a>. Sources: Drawings from this study.</p>
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18 pages, 6352 KiB  
Article
Super-Resolution Rural Road Extraction from Sentinel-2 Imagery Using a Spatial Relationship-Informed Network
by Yuanxin Jia, Xining Zhang, Ru Xiang and Yong Ge
Remote Sens. 2023, 15(17), 4193; https://doi.org/10.3390/rs15174193 - 25 Aug 2023
Cited by 4 | Viewed by 1785
Abstract
With the development of agricultural and rural modernization, the informatization of rural roads has been an inevitable requirement for promoting rural revitalization. To date, however, the vast majority of road extraction methods mainly focus on urban areas and rely on very high-resolution satellite [...] Read more.
With the development of agricultural and rural modernization, the informatization of rural roads has been an inevitable requirement for promoting rural revitalization. To date, however, the vast majority of road extraction methods mainly focus on urban areas and rely on very high-resolution satellite or aerial images, whose costs are not yet affordable for large-scale rural areas. Therefore, a deep learning (DL)-based super-resolution mapping (SRM) method has been considered to relieve this dilemma by using freely available Sentinel-2 imagery. However, few DL-based SRM methods are suitable due to these methods only relying on the spectral features derived from remote sensing images, which is insufficient for the complex rural road extraction task. To solve this problem, this paper proposes a spatial relationship-informed super-resolution mapping network (SRSNet) for extracting roads in rural areas which aims to generate 2.5 m fine-scale rural road maps from 10 m Sentinel-2 images. Based on the common sense that rural roads often lead to rural settlements, the method adopts a feature enhancement module to enhance the capture of road features by incorporating the relative position relation between roads and rural settlements into the model. Experimental results show that the SRSNet can effectively extract road information, with significantly better results for elongated rural roads. The intersection over union (IoU) of the mapping results is 68.9%, which is 4.7% higher than that of the method without fusing settlement features. The extracted roads show more details in the areas with strong spatial relationships between the settlements and roads. Full article
(This article belongs to the Special Issue Convolutional Neural Network Applications in Remote Sensing II)
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<p>The proposed SRSNet’s architecture. ① is BaseNet; ② is POINet; ③ is the feature enhancement module; and ④ is the up-sampling classification module. In BaseNet, blocks and layers of the same color in the model mean that they are at the same level. SA denotes the spatial attention mechanism. The input LR (low-resolution) remote sensing image <math display="inline"><semantics> <mi>Y</mi> </semantics></math> and the settlement data <math display="inline"><semantics> <mi>P</mi> </semantics></math> have dimensions of <math display="inline"><semantics> <mrow> <mi>W</mi> <mo>×</mo> <mi>H</mi> <mo>×</mo> <mi>C</mi> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <mi>W</mi> <mo>×</mo> <mi>H</mi> <mo>×</mo> <mn>1</mn> </mrow> </semantics></math>, respectively, where <math display="inline"><semantics> <mi>C</mi> </semantics></math> is the number of bands. The size of the output HR (high-resolution) road map <math display="inline"><semantics> <mi>X</mi> </semantics></math> is <math display="inline"><semantics> <mrow> <mo stretchy="false">(</mo> <mi>W</mi> <mo>×</mo> <mi>S</mi> <mo stretchy="false">)</mo> <mo>×</mo> <mo stretchy="false">(</mo> <mi>H</mi> <mo>×</mo> <mi>S</mi> <mo stretchy="false">)</mo> </mrow> </semantics></math>, where <span class="html-italic">S</span> is the scale factor. <span class="html-italic">f</span><sub>max</sub>(·) is the function used to obtain the final classification for each subpixel by selecting the maximum membership probability.</p>
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<p>Structure of the feature enhancement module.</p>
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<p>Flowchart of the methodology.</p>
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<p>Sentinel-2 image map of Chongyang County.</p>
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<p>Distribution of POI-based settlement data and label data patches. (<b>a</b>) The distribution of POI-based settlement data. (<b>b</b>) The distribution of label data patches.</p>
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<p>Illustration of the two comparison methods.</p>
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<p>Visual comparison of the mapping results of different SRM methods. (<b>a</b>) The Sentinel-2 remote sensing image using RGB bands. (<b>b</b>–<b>f</b>) Mapping results of road extraction using SRMCNN-ESPCN, SRMCNN, CASNet, SCNet, and SRSNet, respectively. (<b>g</b>) The reference road map.</p>
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<p>Comparison of the mapping results of three methods for road extraction. (<b>a</b>) The Sentinel-2 remote sensing image using RGB bands. (<b>b</b>–<b>d</b>) Mapping results of road extraction using SRM<sub>CNN</sub>, SRM<sub>CNN_op</sub>, and SRSNet, respectively. (<b>e</b>) The reference road map.</p>
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<p>Comparison of the road mapping results in the vicinity of the settlement area. (<b>a</b>) The Sentinel-2 remote sensing image using RGB bands, where the yellow square area in the remote sensing image indicates the settlements. (<b>b</b>–<b>d</b>) Mapping results of road extraction using SRM<sub>CNN</sub>, SRM<sub>CNN_op</sub>, and SRSNet, respectively, where the green dashed box in (<b>a</b>), (<b>b</b>) and (<b>c</b>) is the area near the settlements. (<b>e</b>) The reference road map.</p>
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<p>Visual comparison of the road mapping results using different SRM methods. (<b>a</b>) The Sentinel-2 remote sensing image using RGB bands. (<b>b</b>,<b>c</b>) Mapping result of the road extracted by SRSNet whose sampling method are nearest and bilinear respectively. (<b>d</b>) Mapping result of the road extracted by SRSNet. (<b>e</b>) The reference road map.</p>
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<p>Grad-CAM visualization of the feature maps of the different layers of the three methods. (<b>a</b>) The original Sentinel-2 image overlay with settlements. (<b>b</b>) The road mapping of the reference. (<b>c</b>) The feature map of the layer extracted by BaseNet. (<b>d</b>) The feature map of the layer after fusing features from settlements, which is the feature map of SRMCNN before up-sampling. (<b>e</b>) The feature map of the last convolutional layer. (<b>f</b>) The weighted superimposition of the feature map of the last convolutional layer on the original image.</p>
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13 pages, 5352 KiB  
Article
Research on Detection and Recognition Technology of a Visible and Infrared Dim and Small Target Based on Deep Learning
by Yuxing Dong, Yan Li and Zhen Li
Electronics 2023, 12(7), 1732; https://doi.org/10.3390/electronics12071732 - 5 Apr 2023
Cited by 1 | Viewed by 1738
Abstract
With the increasing trend towards informatization and intelligence in modern warfare, high-intensity and continuous reconnaissance activities are becoming increasingly common in battlefield environments via airborne, vehicle, UAV, satellite and other platforms. Visible and infrared images are preferred due to their high resolution, strong [...] Read more.
With the increasing trend towards informatization and intelligence in modern warfare, high-intensity and continuous reconnaissance activities are becoming increasingly common in battlefield environments via airborne, vehicle, UAV, satellite and other platforms. Visible and infrared images are preferred due to their high resolution, strong contrast, rich texture details and color features, and strong information expression ability. However, the quality of imaging is easily affected by environmental factors, making it crucial to quickly and accurately filter useful information from massive image data. To this end, super-resolution image preprocessing can improve the detection performance of UAV, and reduce false detection and missed detection of targets. Additionally, super-resolution reconstruction results in high-quality images that can be used to expand UAV datasets and enhance the UAV characteristics, thereby enabling the enhancement of small targets. In response to the challenge of “low-slow small” UAV targets at long distances, we propose a multi-scale fusion super-resolution reconstruction (MFSRCNN) algorithm based on the fast super-resolution reconstruction (FSRCNN) algorithm and multi-scale fusion. Our experiments confirm the feasibility of the algorithm in reconstructing detailed information of the UAV target. On average, the MFSRCNN reconstruction time is 0.028 s, with the average confidence before and after reconstruction being 80.73% and 86.59%, respectively, resulting in an average increase of 6.72%. Full article
(This article belongs to the Section Artificial Intelligence)
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<p>MLIDS integrated defense system.</p>
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<p>UAVX anti-UAV system.</p>
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<p>Network structure diagram of the MFSRCNN algorithm.</p>
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<p>Deconvolution and feature extraction structure diagram.</p>
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<p>Partial convolution kernel output in subnetwork 1.</p>
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<p>Structure diagram of nonlinear transformation.</p>
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<p>Schematic diagram of multi-scale fusion.</p>
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<p>Structure diagram of multi-scale fusion.</p>
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<p>Image reconstruction structure diagram.</p>
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<p>Feature map of feature fusion result.</p>
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<p>Feature extraction result feature map.</p>
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<p>Loss change curve during training.</p>
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<p>Comparison of super-resolution reconstruction results with and without pre-training. (<b>a</b>) Results without pretraining and (<b>b</b>) results with pretraining.</p>
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<p>MFSRCNN performance and parameters compared to other advanced lightweight networks.</p>
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3524 KiB  
Proceeding Paper
Sentinel-1 Polarization Comparison for Flood Segmentation Using Deep Learning
by Mohammadali Abbasi, Reza Shah-Hosseini and Mohammad Aghdami-Nia
Proceedings 2023, 87(1), 14; https://doi.org/10.3390/IECG2022-14069 - 22 Feb 2023
Cited by 3 | Viewed by 1604
Abstract
Flood is one of the most damaging natural hazards, and timely detection of it is very important to save human lives and assess the level of damage. The occurrence of floods in cloudy weather conditions makes the use of radar-based sensors for real-time [...] Read more.
Flood is one of the most damaging natural hazards, and timely detection of it is very important to save human lives and assess the level of damage. The occurrence of floods in cloudy weather conditions makes the use of radar-based sensors for real-time flood mapping inevitable. In the present study, the ETCI 2021 flood event detection competition dataset, organized by the NASA Advanced Concepts and Implementation Team in collaboration with the IEEE GRSS Geoscience Informatics Technical Committee, has been used. Moreover, we have utilized the U-Net and X-Net architecture as a segmentation model to map flooded regions. This study aimed to identify the optimum polarization of the Sentinel-1 satellite for flood detection. By examining and comparing the obtained results, it was observed that the VV polarization offered better results in both models. Furthermore, U-Net had a better performance than X-Net in both polarizations. Full article
(This article belongs to the Proceedings of The 4th International Electronic Conference on Geosciences)
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<p>Red dots indicate the locations in ETCI 2021 flood detection dataset.</p>
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<p>Pre-processing steps.</p>
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<p>U-Net model architecture.</p>
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<p>X-Net model architecture.</p>
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<p>Visual outputs of U-Net model. (<bold>a</bold>) VH image; (<bold>b</bold>) VV image; (<bold>c</bold>) ground truth; (<bold>d</bold>) VH prediction; (<bold>e</bold>) VV prediction.</p>
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<p>Visual outputs of X-Net model. (<bold>a</bold>) VH image; (<bold>b</bold>) VV image; (<bold>c</bold>) ground truth; (<bold>d</bold>) VH prediction; (<bold>e</bold>) VV prediction.</p>
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25 pages, 5978 KiB  
Article
Tailoring Vibrational Signature and Functionality of 2D-Ordered Linear-Chain Carbon-Based Nanocarriers for Predictive Performance Enhancement of High-End Energetic Materials
by Alexander Lukin and Oğuz Gülseren
Nanomaterials 2022, 12(7), 1041; https://doi.org/10.3390/nano12071041 - 22 Mar 2022
Cited by 2 | Viewed by 2705
Abstract
A recently proposed, game-changing transformative energetics concept based on predictive synthesis and preprocessing at the nanoscale is considered as a pathway towards the development of the next generation of high-end nanoenergetic materials for future multimode solid propulsion systems and deep-space-capable small satellites. As [...] Read more.
A recently proposed, game-changing transformative energetics concept based on predictive synthesis and preprocessing at the nanoscale is considered as a pathway towards the development of the next generation of high-end nanoenergetic materials for future multimode solid propulsion systems and deep-space-capable small satellites. As a new door for the further performance enhancement of transformative energetic materials, we propose the predictive ion-assisted pulse-plasma-driven assembling of the various carbon-based allotropes, used as catalytic nanoadditives, by the 2D-ordered linear-chained carbon-based multicavity nanomatrices serving as functionalizing nanocarriers of multiple heteroatom clusters. The vacant functional nanocavities of the nanomatrices available for heteroatom doping, including various catalytic nanoagents, promote heat transfer enhancement within the reaction zones. We propose the innovative concept of fine-tuning the vibrational signatures, functionalities and nanoarchitectures of the mentioned nanocarriers by using the surface acoustic waves-assisted micro/nanomanipulation by the pulse-plasma growth zone combined with the data-driven carbon nanomaterials genome approach, which is a deep materials informatics-based toolkit belonging to the fourth scientific paradigm. For the predictive manipulation by the micro- and mesoscale, and the spatial distribution of the induction and energy release domains in the reaction zones, we propose the activation of the functionalizing nanocarriers, assembled by the heteroatom clusters, through the earlier proposed plasma-acoustic coupling-based technique, as well as by the Teslaphoresis force field, thus inducing the directed self-assembly of the mentioned nanocarbon-based additives and nanocarriers. Full article
(This article belongs to the Special Issue Energetic Nanomaterials)
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Graphical abstract
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<p>The electronic configuration of a fragment of a linear-chain carbon molecule.</p>
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<p>Spatial structure of the 2D-ordered linear-chain carbon-based nanomatrix fragment, containing the nanocavity, available for heteroatom doping.</p>
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<p>Schematic representation of the vacant nanocavity of the 2D-ordered linear-chain carbon-based nanomatrix available for heteroatom doping.</p>
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<p>Schematic representation of the multiple heteroatom-doped functionalizing nanocarrier, based on the 2D-ordered linear-chain carbon-based multicavity nanomatrix, containing the vacant functional nanocavities.</p>
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<p>Schematic representation of the pulse-plasma deposition reactor for growing the 2D-ordered linear-chain carbon nanomatrix: 1—vacuum chamber; 2—substrate; 3—pulse-plasma carbon generator (graphite cylindrical main discharge cathode); 4—the ion source for ionic stimulation; 5—target assembly with removable target material; 6—vacuum sensor.</p>
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<p>Schematic representation of the pulse-plasma generator installed in the reactor of the experimental set-up (<a href="#nanomaterials-12-01041-f005" class="html-fig">Figure 5</a>): 1—a cylindrical main discharge cathode (evaporated material, the high purity graphite) containing cylindrical rods manufactured from various materials and used for heteroatom doping; 2—the main discharge anode; 3—a solenoid final focusing system with plasma neutralization; 4—second auxiliary discharge anode; 5—ignition cathode; 6—ignition anode; 7—dielectric insulator; 8—substrate holder.</p>
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<p>Example of design of a cylindrical main discharge cathode (evaporated material, the high purity graphite), containing cylindrical rods manufactured from various materials, used for heteroatom doping, for instance, silver, tungsten, gold, etc. This is item 1 in <a href="#nanomaterials-12-01041-f006" class="html-fig">Figure 6</a>.</p>
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<p>Schematic representation of using inverse piezoelectric effect during the nanomatrix ion-stimulated pulse-plasma deposition and schematic illustration of SAW streaming.</p>
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<p>Schematic representation of using the direct and inverse piezoelectric effect at the nanomatrix ion-stimulated pulse-plasma deposition.</p>
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<p>An example of the binding energy ratio for carbyne (sp) and graphene-like (sp2) hybridized bonds, obtained using X-ray photoelectron spectroscopy (XPS).</p>
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<p>Schematic representation of the lateral and longitudinal oscillations of the sp-hybridized carbon chains.</p>
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<p>Machine learning-based fine-tuning of the functionalizing nanocarriers: a scheme of tracking and tailoring the key descriptors and linkages for incorporating into the data-driven carbon nanomaterials genome approach.</p>
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<p>Schematic representation of the acoustic hologram transformation into the electromagnetic hologram through the 2D-ordered linear-chain carbon-based functionalizing nanocarrier, assembled by the piezoelectric nanomaterial clusters.</p>
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<p>Modification of the technological chain of the transformative energetic materials’ multistage synthesis.</p>
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28 pages, 14811 KiB  
Article
Accuracy of Sentinel-1 PSI and SBAS InSAR Displacement Velocities against GNSS and Geodetic Leveling Monitoring Data
by Francesca Cigna, Rubén Esquivel Ramírez and Deodato Tapete
Remote Sens. 2021, 13(23), 4800; https://doi.org/10.3390/rs13234800 - 26 Nov 2021
Cited by 53 | Viewed by 8523
Abstract
Correct use of multi-temporal Interferometric Synthetic Aperture Radar (InSAR) datasets to complement geodetic surveying for geo-hazard applications requires rigorous assessment of their precision and accuracy. Published inter-comparisons are mostly limited to ground displacement estimates obtained from different algorithms belonging to the same family [...] Read more.
Correct use of multi-temporal Interferometric Synthetic Aperture Radar (InSAR) datasets to complement geodetic surveying for geo-hazard applications requires rigorous assessment of their precision and accuracy. Published inter-comparisons are mostly limited to ground displacement estimates obtained from different algorithms belonging to the same family of InSAR approaches, either Persistent Scatterer Interferometry (PSI) or Small BAseline Subset (SBAS); and accuracy assessments are mainly focused on vertical displacements or based on few Global Navigation Satellite System (GNSS) or geodetic leveling points. To fill this demonstration gap, two years of Sentinel-1 SAR ascending and descending mode data are processed with both PSI and SBAS consolidated algorithms to extract vertical and horizontal displacement velocity datasets, whose accuracy is then assessed against a wealth of contextual geodetic data. These include permanent GNSS records, static GNSS benchmark repositioning, and geodetic leveling monitoring data that the National Institute of Statistics, Geography, and Informatics (INEGI) of Mexico collected in 2014−2016 in the Aguascalientes Valley, where structurally-controlled land subsidence exhibits fast vertical rates (up to −150 mm/year) and a non-negligible east-west component (up to ±30 mm/year). Despite the temporal constraint of the data selected, the PSI-SBAS inter-comparison reveals standard deviation of 6 mm/year and 4 mm/year for the vertical and east-west rate differences, respectively, thus reassuring about the similarity between the two types of InSAR outputs. Accuracy assessment shows that the standard deviations in vertical velocity differences are 9−10 mm/year against GNSS benchmarks, and 8 mm/year against leveling data. Relative errors are below 20% for any locations subsiding faster than −15 mm/year. Differences in east-west velocity estimates against GNSS are on average −0.1 mm/year for PSI and +0.2 mm/year for SBAS, with standard deviations of 8 mm/year. When discrepancies are found between InSAR and geodetic data, these mostly occur at benchmarks located in proximity to the main normal faults, thus falling within the same SBAS ground pixel or closer to the same PSI target, regardless of whether they are in the footwall or hanging wall of the fault. Establishing new benchmarks at higher distances from the fault traces or exploiting higher resolution SAR scenes and/or InSAR datasets may improve the detection of the benchmarks and thus consolidate the statistics of the InSAR accuracy assessments. Full article
(This article belongs to the Section Remote Sensing Image Processing)
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<p>Location of geodetic stations in Aguascalientes state (<b>a</b>) and in Aguascalientes city in detail (<b>b</b>). The study area is near the geographic centre of Mexico, 340 km north-west from Mexico City. Red lines in the maps are the trace of faults detected up to 2015 [<a href="#B32-remotesensing-13-04800" class="html-bibr">32</a>], and green lines are the footprints of subswaths 1 and 2 of the Sentinel-1 IW beam mode images acquired along ascending and descending orbits.</p>
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<p>Orientation of the satellite Line-Of-Sight (LOS) in (<b>a</b>) the horizontal plane and (<b>b</b>) 3D, and (<b>c</b>) projection of the velocity vector <math display="inline"><semantics> <mover accent="true"> <mi>V</mi> <mo>→</mo> </mover> </semantics></math> along the LOS. The sketches refer to a descending orbit and the right-looking acquisition geometry. LOS orientation is according to the established assumption of negative displacement values indicating movements away from the sensor. Directional cosines refer to a unit vector <math display="inline"><semantics> <mover accent="true"> <mi>u</mi> <mo>→</mo> </mover> </semantics></math> (with length = 1). Notation: <span class="html-italic">α,</span> heading angle; <span class="html-italic">θ</span>, incidence angle.</p>
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<p>(<b>a</b>) INEG permanent station monument; (<b>b</b>) typical benchmark for GNSS and leveling network stations, and (<b>c</b>) monitoring benchmark surveying using geodetic GNSS receivers.</p>
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<p>Equipment used by INEGI to perform the geodetic leveling surveys: (<b>a</b>) Leica DNA03 automatic digital level, (<b>b</b>) level rod with invar bar-code, and (<b>c</b>) benchmark leveling.</p>
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<p>SBAS results: displacement velocity in 2014−2016 along the (<b>a</b>) vertical <span class="html-italic">V<sub>U</sub></span> and (<b>b</b>) east-west <span class="html-italic">V<sub>E</sub></span> directions.</p>
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<p>PSI results: displacement velocity in 2014−2016 along the (<b>a</b>) vertical <span class="html-italic">V<sub>U</sub></span> and (<b>b</b>) east-west <span class="html-italic">V<sub>E</sub></span> directions. <span class="html-italic">V<sub>E</sub></span> larger than 0.03 m/year are dispersed outside the subsidence area.</p>
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<p>Height velocities (<span class="html-italic">V<sub>U</sub></span>) from geodetic data: (<b>a</b>) at the GNSS benchmarks and permanent stations and (<b>b</b>) at the leveling benchmarks; both plotted over PSI-derived vertical velocities.</p>
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<p>Horizontal velocities from GNSS data at the benchmarks and permanent stations: (<b>a</b>) horizontal velocity vector [<span class="html-italic">V<sub>E</sub> V<sub>N</sub></span>] plotted over PSI-derived vertical velocities and (<b>b</b>) only east-west velocities (<span class="html-italic">V<sub>E</sub></span>) plotted over PSI-derived east-west velocities.</p>
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<p>Differences between SBAS and PSI velocities. (<b>a</b>) PSI-SBAS differences in up (<span class="html-italic">Δ</span><span class="html-italic">V<sub>U</sub></span>) direction and (<b>b</b>) SBAS-PSI differences in east-west (<span class="html-italic">Δ</span><span class="html-italic">V<sub>E</sub></span>) direction.</p>
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<p>Comparison of the displacement velocity along the (<b>a</b>) vertical <span class="html-italic">V<sub>U</sub></span> and (<b>b</b>) east-west <span class="html-italic">V<sub>E</sub></span> direction as estimated from the SBAS and PSI InSAR analyses at the 2 permanent GNSS stations and 62 GNSS benchmarks, and distribution of their observed differences: (<b>c</b>) <span class="html-italic">ΔV<sub>U</sub></span> and (<b>d</b>) <span class="html-italic">ΔV<sub>E</sub></span>, respectively. The latter are also inter-compared in (<b>e</b>).</p>
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<p>Comparison of the displacement velocity along the (<b>a</b>) vertical <span class="html-italic">V<sub>U</sub></span> and (<b>b</b>) east-west <span class="html-italic">V<sub>E</sub></span> direction as estimated from the SBAS and PSI InSAR analyses for the whole investigated area (i.e., 128,772 samples for <span class="html-italic">V<sub>U</sub></span>, and 75,546 for <span class="html-italic">V<sub>E</sub></span>), and distribution of their observed differences: (<b>c</b>) <span class="html-italic">ΔV<sub>U</sub></span> and (<b>d</b>) <span class="html-italic">ΔV<sub>E</sub></span>, respectively. The latter are also inter-compared in (<b>e</b>) for the 75,546 samples for which both <span class="html-italic">V<sub>U</sub></span> and <span class="html-italic">V<sub>E</sub></span> are available. The colors in (<b>a</b>), (<b>b</b>), and (<b>e</b>) indicate the scatter density, on a relative scale from 0 (minimum) to 1 (maximum); the scatterplots were created using <span class="html-italic">scatplot.m</span>.</p>
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<p>Displacement velocity along the vertical <span class="html-italic">V<sub>U</sub></span> direction estimated at 10 benchmarks that were surveyed using both GNSS and geodetic leveling: (<b>a</b>) location map onto PSI-derived <span class="html-italic">V<sub>U</sub></span> and (<b>b</b>) comparison plot. The benchmarks are sorted in (<b>b</b>) according to their <span class="html-italic">V<sub>U</sub></span> estimated via leveling.</p>
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<p>Comparison of the displacement velocity along the (<b>a</b>) vertical <span class="html-italic">V<sub>U</sub></span> and (<b>b</b>) east-west <span class="html-italic">V<sub>E</sub></span> direction as estimated from the PSI InSAR analyses and recorded at the permanent GNSS stations and GNSS benchmarks. The observed differences <span class="html-italic">ΔV<sub>U</sub></span> and <span class="html-italic">ΔV<sub>E</sub></span> were further investigated through (<b>c</b>) inter-comparison, (<b>d</b>,<b>g</b>) analysis of the respective histograms, and (<b>e</b>,<b>f</b>,<b>h</b>,<b>i</b>) their distribution in relation to GNSS records.</p>
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<p>Comparison of the displacement velocity along the (<b>a</b>) vertical <span class="html-italic">V<sub>U</sub></span> and (<b>b</b>) east-west <span class="html-italic">V<sub>E</sub></span> direction as estimated from the SBAS InSAR analyses and recorded at the permanent GNSS stations and GNSS benchmarks. The observed differences <span class="html-italic">ΔV<sub>U</sub></span> and <span class="html-italic">ΔV<sub>E</sub></span> are further investigated through (<b>c</b>) inter-comparison, (<b>d</b>,<b>g</b>) analysis of the respective histograms, and (<b>e</b>,<b>f</b>,<b>h</b>,<b>i</b>) their distribution in relation to GNSS records.</p>
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<p>Estimated magnitude of the contribution to the observed velocity differences (<b>a</b>) <span class="html-italic">ΔV<sub>U</sub></span> and (<b>b</b>) <span class="html-italic">ΔV<sub>E</sub></span> that is made by the <span class="html-italic">V<sub>N</sub></span> = 0 assumption.</p>
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<p>Comparison of the displacement velocity along the vertical <span class="html-italic">V<sub>U</sub></span> direction as recorded at the geodetic leveling benchmarks and estimated from the InSAR analysis with the (<b>a</b>–<b>c</b>) PSI and (<b>d</b>–<b>f</b>) SBAS methods: (<b>a</b>,<b>d</b>) velocity scatterplots, (<b>b</b>,<b>e</b>) distribution of the observed differences <span class="html-italic">ΔV<sub>U</sub></span>, and (<b>c</b>,<b>f</b>) their correlation with the vertical velocity at the leveling benchmarks.</p>
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<p>Location of pairs of monitoring benchmarks F23A−F23B and FG26−FG26A with respect to the Oriente fault trace and grid coverages of SBAS (~90 m blue squares) and PSI up velocities (1 arcsecond pixels, i.e., ~30 m).</p>
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20 pages, 5862 KiB  
Article
Evaluating the Spatio-Temporal Distribution of Irrigation Water Components for Water Resources Management Using Geo-Informatics Approach
by Muhammad Mohsin Waqas, Muhammad Waseem, Sikandar Ali, Megersa Kebede Leta, Adnan Noor Shah, Usman Khalid Awan, Syed Hamid Hussain Shah, Tao Yang and Sami Ullah
Sustainability 2021, 13(15), 8607; https://doi.org/10.3390/su13158607 - 2 Aug 2021
Cited by 4 | Viewed by 2575
Abstract
Spatio-temporal distribution of irrigation water components was evaluated at the canal command area in Indus Basin Irrigation System (IBIS) by using a remote sensing-based geo-informatics approach. Satellite-derived MODIS product-based Surface Energy Balance Algorithm for Land (SEBAL) was used for the estimation of the [...] Read more.
Spatio-temporal distribution of irrigation water components was evaluated at the canal command area in Indus Basin Irrigation System (IBIS) by using a remote sensing-based geo-informatics approach. Satellite-derived MODIS product-based Surface Energy Balance Algorithm for Land (SEBAL) was used for the estimation of the actual evapotranspiration (ETa). The ground data-based advection aridity method (AA) was used to calibrate and validate the model. Statistical analysis of the SEBAL based ETa and AA shows the mean values of 87.1 mm and 47.9 mm during Kharif season (May–November) and 100 mm and 77 mm during the Rabi Season (December–April). Mean NSEs of 0.72 and 0.85 and RMSEs 34.9 and 5.76 during the Kharif and the Rabi seasons were observed for ETa and AA, respectively. Rainfall data were calibrated with the point observatory data of the metrological stations. The average annual ETa was found 899 mm for defined four cropping years (2011–2012 to 2014–2015) with the minimum average value of 63.3 mm in January and the maximum average value of 110.6 mm in August. Average of the sum of net canal water use (NCWU) and rainfall during the study period of four years was 548 mm (36% of ETa). Seasonal analysis revealed 39% and 61% of groundwater extraction proportion during Rabi and Kharif seasons, dependent upon the occurrence of rainfall and crop phenology. Overall, the results provide insight into the interrelationships between key water resources management components and the variation of these through time, offering information to improve the strategic planning and management of available water resources in this region. Full article
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<p>Lower Chenab canal command area.</p>
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<p>The methodological framework for the quantification of groundwater irrigation.</p>
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<p>Gross canal water distribution at the CCAs of the LCC system.</p>
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<p>Comparison of satellite-based ETa and ETa by the AA method based calibration (2011–2012 to 2012–2013) and validation (2013–2014 to 2014–2015) of SEBAL.</p>
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<p>Four years average SEBAL estimated ETa of the Rabi season.</p>
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<p>Four years average SEBAL estimated ETa of the Kharif season.</p>
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<p>Actual evapotranspiration at different CCAs of LCC.</p>
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<p>Four years average Rabi season satellite derived rainfall.</p>
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<p>Four years average Kharif season satellite derived rainfall.</p>
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<p>Effective annual rainfall at CCAs (2011–2012 to 2014–2015).</p>
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<p>Four years average Rabi season groundwater irrigation in the LCC.</p>
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<p>Four years average Kharif season groundwater irrigation in the LCC.</p>
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<p>Gross groundwater irrigation at different CCAs of the LCC system.</p>
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20 pages, 3855 KiB  
Review
State of the Art of Monitoring Technologies and Data Processing for Precision Viticulture
by Marco Ammoniaci, Simon-Paolo Kartsiotis, Rita Perria and Paolo Storchi
Agriculture 2021, 11(3), 201; https://doi.org/10.3390/agriculture11030201 - 28 Feb 2021
Cited by 46 | Viewed by 7876
Abstract
Precision viticulture (PV) aims to optimize vineyard management, reducing the use of resources, the environmental impact and maximizing the yield and quality of the production. New technologies as UAVs, satellites, proximal sensors and variable rate machines (VRT) are being developed and used more [...] Read more.
Precision viticulture (PV) aims to optimize vineyard management, reducing the use of resources, the environmental impact and maximizing the yield and quality of the production. New technologies as UAVs, satellites, proximal sensors and variable rate machines (VRT) are being developed and used more and more frequently in recent years thanks also to informatics systems able to read, analyze and process a huge number of data in order to give the winegrowers a decision support system (DSS) for making better decisions at the right place and time. This review presents a brief state of the art of precision viticulture technologies, focusing on monitoring tools, i.e., remote/proximal sensing, variable rate machines, robotics, DSS and the wireless sensor network. Full article
(This article belongs to the Special Issue Precision Viticulture and Enology: Technologies and Applications)
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<p>Precision agriculture (PA) general workflow [<a href="#B2-agriculture-11-00201" class="html-bibr">2</a>].</p>
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<p>Precision agriculture technologies overview (adapted from [<a href="#B11-agriculture-11-00201" class="html-bibr">11</a>], with permission from <span class="html-italic">Sustainability</span>, 2017).</p>
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<p>Rotary-wings UAV.</p>
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<p>Proximal multispectral sensor (OptRx ACS-430, Ag Leader Technology, Ames, IA, USA) for NDVI mapping of vineyard canopy (reproduced from [<a href="#B57-agriculture-11-00201" class="html-bibr">57</a>], with permission from <span class="html-italic">SOIL</span>, 2015).</p>
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<p>VitiCanopy app (Bruno Tisseyre, <a href="http://www.agrotic.org" target="_blank">www.agrotic.org</a>).</p>
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<p>Mobile sensor platform Veris 3150 for ECa mapping (reproduced from [<a href="#B57-agriculture-11-00201" class="html-bibr">57</a>], with permission from <span class="html-italic">SOIL</span>, 2015).</p>
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<p>(<b>a</b>) Mobile soil resistance meters (reproduced from [<a href="#B63-agriculture-11-00201" class="html-bibr">63</a>], with permission from <span class="html-italic">Georgofili</span>, 2017); (<b>b</b>) Electrical Resistivity map 0–50 cm (SO.IN.G. strutture &amp; ambiente S.r.l., Cesa, Arezzo, Italy, 2019).</p>
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<p>Grape quality sensors (reproduced from [<a href="#B9-agriculture-11-00201" class="html-bibr">9</a>], with permission from <span class="html-italic">International Journal of Wine Research</span>, 2015: (<b>a</b>) Multiplex (Force-A, Orsay, France); (<b>b</b>) Spectron (Pellenc SA, Pertuis, France).</p>
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<p>VRT machines: (<b>a</b>) VRT sprayer [<a href="#B67-agriculture-11-00201" class="html-bibr">67</a>] (reproduced from [<a href="#B67-agriculture-11-00201" class="html-bibr">67</a>] with permission from <span class="html-italic">Ist Int. Workshop Vineyard Mech. Grape Wine Qual. Piacenza Acta Hortic</span>, 2013; (<b>b</b>) VRT fertilizer (reproduced from [<a href="#B69-agriculture-11-00201" class="html-bibr">69</a>] with permission from <span class="html-italic">Universitat Politecnica de Valencia</span>, 2015).</p>
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<p>Agbots: (<b>a</b>) Vinbot robot platform (reproduced from [<a href="#B73-agriculture-11-00201" class="html-bibr">73</a>] with permission from <span class="html-italic">Jones, G.; Doran, N., Eds.</span>, 2016); (<b>b</b>) GRAPE (GroundRobot for vineyArd Monitoring and ProtEction) (reproduced from [<a href="#B74-agriculture-11-00201" class="html-bibr">74</a>] with permission from <span class="html-italic">Springer</span>, 2017).</p>
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<p>Weather stations to monitor the vineyard meteorological data (reproduced from [<a href="#B79-agriculture-11-00201" class="html-bibr">79</a>] with permission from <span class="html-italic">Sensors</span>, 2020).</p>
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4 pages, 197 KiB  
Editorial
Geo-Informatics in Resource Management
by Francisco Javier Mesas-Carrascosa
ISPRS Int. J. Geo-Inf. 2020, 9(11), 628; https://doi.org/10.3390/ijgi9110628 - 26 Oct 2020
Viewed by 2455
Abstract
Natural resource management requires reliable and timely information available at local, regional, national, and global scales. Geo-informatics, by remote sensing, global navigation satellite systems, geographical information systems, and related technologies, provides information for natural resource management, environmental protection, and support related to sustainable [...] Read more.
Natural resource management requires reliable and timely information available at local, regional, national, and global scales. Geo-informatics, by remote sensing, global navigation satellite systems, geographical information systems, and related technologies, provides information for natural resource management, environmental protection, and support related to sustainable development. Geo-informatics has proven to be a powerful technology for studying and monitoring natural resources as well as in generating predictive models, making it an important decision-making tool. The manuscripts included in this Special Issue focus on disciplines that advance the field of resource management in geomatics. The manuscripts showcased here provide different examples of challenges in resource management. Full article
(This article belongs to the Special Issue Geo-Informatics in Resource Management)
17 pages, 3399 KiB  
Article
Spatio-Temporal Variations of CO2 Emission from Energy Consumption in the Yangtze River Delta Region of China and Its Relationship with Nighttime Land Surface Temperature
by Juchao Zhao, Shaohua Zhang, Kun Yang, Yanhui Zhu and Yuling Ma
Sustainability 2020, 12(20), 8388; https://doi.org/10.3390/su12208388 - 12 Oct 2020
Cited by 13 | Viewed by 2815
Abstract
The rapid development of industrialization and urbanization has resulted in a large amount of carbon dioxide (CO2) emissions, which are closely related to the long-term stability of urban surface temperature and the sustainable development of cities in the future. However, there [...] Read more.
The rapid development of industrialization and urbanization has resulted in a large amount of carbon dioxide (CO2) emissions, which are closely related to the long-term stability of urban surface temperature and the sustainable development of cities in the future. However, there is still a lack of research on the temporal and spatial changes of CO2 emissions in long-term series and their relationship with land surface temperature. In this study, Defense Meteorological Satellite Program’s Operational Linescan System (DMSP/OLS) data, Suomi National Polar-orbiting Partnership (NPP) Visible Infrared Imaging Radiometer Suite (VIIRS) composite data, energy consumption statistics data and nighttime land surface temperature are selected to realize the spatial informatization of long-term series CO2 emissions in the Yangtze River Delta region, which reveals the spatial and temporal dynamic characteristics of CO2 emissions, spatial autocorrelation distribution patterns and their impacts on nighttime land surface temperature. According to the results, CO2 emissions in the Yangtze River Delta region show an obvious upward trend from 2000 to 2017, with an average annual growth rate of 6.26%, but the growth rate is gradually slowing down. In terms of spatial distribution, the CO2 emissions in that region have significant regional differences. Shanghai, Suzhou and their neighboring cities are the main distribution areas with high CO2 emissions and obvious patch distribution patterns. From the perspective of spatial trend, the areas whose CO2 emissions are of significant growth, relatively significant growth and extremely significant growth account for 8.78%, 4.84% and 0.58%, respectively, with a spatial pattern of increase in the east and no big change in the west. From the perspective of spatial autocorrelation, the global spatial autocorrelation index of CO2 emissions in the Yangtze River Delta region in the past 18 years has been greater than 0.66 (p < 0.01), which displays significant positive spatial autocorrelation characteristics, and the spatial agglomeration degree of CO2 emissions continues to increase from 2000 to 2010. From 2000 to 2017, the nighttime land surface temperature in that region showed a warming trend, and the areas where CO2 emissions are positively correlated with nighttime land surface temperature account for 88.98%. The increased CO2 emissions lead to, to a large extent, the rise of nighttime land surface temperature. The research results have important theoretical and practical significance for the Yangtze River Delta region to formulate a regional emission reduction strategy. Full article
(This article belongs to the Special Issue Sustainable Cities: Challenges and Potential Solutions)
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<p>The location of research area.</p>
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<p>Total digital number (TDN) values in the Yangtze River Delta region from 2000 to 2017.</p>
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<p>Scatter diagram between CO<sub>2</sub> emissions calculated from statistical data and CO<sub>2</sub> emissions simulated from nighttime light data.</p>
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<p>Temporal variation of CO<sub>2</sub> emissions and global Moran’s I during 2000–2017.</p>
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<p>Spatial distribution of CO<sub>2</sub> emissions during 2000–2017.</p>
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<p>Local spatial autocorrelation analysis map of CO<sub>2</sub> emissions from 2000 to 2017.</p>
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<p>Spatial trend characteristics of CO<sub>2</sub> emissions during 2000–2017.</p>
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<p>Temporal variation of nighttime surface temperature during 2000–2017.</p>
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<p>Spatial distribution pattern of CO<sub>2</sub> emissions (<b>a</b>) and nighttime land surface temperature (<b>b</b>) in the Yangtze River Delta from 2000 to 2017.</p>
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<p>Correlation coefficient (<b>a</b>) and significance level (<b>b</b>) of CO<sub>2</sub> emissions and nighttime land surface temperature from 2000 to 2017. Note: ESPC: extremely significant positive correlation; VSPC: very significant positive correlation; RSPC: relatively significant positive correlation; WSPC: weak significant positive correlation; WSNC: weak significant negative correlation; RSNC: relatively significant negative correlation; VSNC: very significant negative correlation; ESNC: extremely significant negative correlation.</p>
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34 pages, 3883 KiB  
Review
A Review of Advanced Technologies and Development for Hyperspectral-Based Plant Disease Detection in the Past Three Decades
by Ning Zhang, Guijun Yang, Yuchun Pan, Xiaodong Yang, Liping Chen and Chunjiang Zhao
Remote Sens. 2020, 12(19), 3188; https://doi.org/10.3390/rs12193188 - 29 Sep 2020
Cited by 145 | Viewed by 16387
Abstract
The detection, quantification, diagnosis, and identification of plant diseases is particularly crucial for precision agriculture. Recently, traditional visual assessment technology has not been able to meet the needs of precision agricultural informatization development, and hyperspectral technology, as a typical type of non-invasive technology, [...] Read more.
The detection, quantification, diagnosis, and identification of plant diseases is particularly crucial for precision agriculture. Recently, traditional visual assessment technology has not been able to meet the needs of precision agricultural informatization development, and hyperspectral technology, as a typical type of non-invasive technology, has received increasing attention. On the basis of simply describing the types of pathogens and host–pathogen interaction processes, this review expounds the great advantages of hyperspectral technologies in plant disease detection. Then, in the process of describing the hyperspectral disease analysis steps, the articles, algorithms, and methods from disease detection to qualitative and quantitative evaluation are mainly summarizing. Additionally, according to the discussion of the current major problems in plant disease detection with hyperspectral technologies, we propose that different pathogens’ identification, biotic and abiotic stresses discrimination, plant disease early warning, and satellite-based hyperspectral technology are the primary challenges and pave the way for a targeted response. Full article
(This article belongs to the Special Issue Remote Sensing and Decision Support for Precision Orchard Production)
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<p>Number of published articles by year on plant disease with hyperspectral data (Data source from Web of Science).</p>
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<p>Plant disease classification by causal agent. Examples and symptoms are listed in each category. Some of these photos were obtained from <a href="https://www.baidu.com" target="_blank">https://www.baidu.com</a>, and some were taken during our own experiments.</p>
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<p>Three fairly distinct stages of plant disease infection, taking wheat <span class="html-italic">Fusarium</span> head blight (FHB) as an example, from inoculation to outbreak.</p>
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<p>Effect of the yellow rust development on the spectral reflectance of winter wheat as days post inoculation (dpi) increase. Gray areas in the reflectance images (lower) indicate significantly different spectral ranges between the inoculated (dotted black line) and non-inoculated (solid black line) leaves.</p>
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<p>Commonly used platforms and scales in plant disease research by hyperspectral techniques. Wheat FHB is cited as the example. (<b>A</b>–<b>C</b>) are the examples of indoor measurement platform at different scales. They are scanning electron microscope, stereo microscope platform, and a typical indoor measurement platform, (<b>D</b>) is a field vehicle platform of hyperspectral imaging, (<b>E</b>) is a unmanned aerial vehicle platform, (<b>F</b>) is a photo of satellite platform; (<b>a</b>–<b>g</b>) are FHB-infected winter wheat hyperspectral images at different scales. They indicated the disease mycelium, infected spikelets, ears, plants, canopy, plots and region hyperspectral images, respectively.</p>
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<p>Basic workflow in hyperspectral imaging-based plant disease classification. PCA: principal component analysis; LESC: local embedding based on spatial coherence algorithm; DWT: discrete wavelet transform; KNN: K-nearest neighbor; SVM: support vector machine; NN: neural networks.</p>
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<p>Two basic workflows of disease severity quantification. a and b indicate that after optimal waveband and feature selection, there are two methods of constructing the final SDIs, one based on feature combination and the other involving model fitting by statistical analysis methods. SVIs: spectral vegetation indices; SDIs: special disease indices; PLSR: partial least squares regression; QDA: quadratic discriminant analysis; FLDA: fisher’s linear discrimination analysis.</p>
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17 pages, 3807 KiB  
Article
Retrieval and Validation of XCO2 from TanSat Target Mode Observations in Beijing
by Zhengyi Bao, Xingying Zhang, Tianxiang Yue, Lili Zhang, Zong Wang, Yimeng Jiao, Wenguang Bai and Xiaoyang Meng
Remote Sens. 2020, 12(18), 3063; https://doi.org/10.3390/rs12183063 - 18 Sep 2020
Cited by 10 | Viewed by 3227
Abstract
Satellite observation is one of the main methods used to monitor the global distribution and variation of atmospheric carbon dioxide (CO2). Several CO2 monitoring satellites have been successfully launched, including Japan’s Greenhouse Gases Observing SATellite (GOSAT), the USA’s Orbiting Carbon [...] Read more.
Satellite observation is one of the main methods used to monitor the global distribution and variation of atmospheric carbon dioxide (CO2). Several CO2 monitoring satellites have been successfully launched, including Japan’s Greenhouse Gases Observing SATellite (GOSAT), the USA’s Orbiting Carbon Observatory-2 (OCO-2), and China’s Carbon Dioxide Observation Satellite Mission (TanSat). Satellite observation targeting the ground-based Fourier transform spectrometer (FTS) station is the most effective technique for validating satellite CO2 measurement precision. In this study, the coincident observations from TanSat and ground-based FTS were performed numerous times in Beijing under a clear sky. The column-averaged dry-air mole fraction of carbon dioxide (XCO2) obtained from TanSat was retrieved by the Department for Eco-Environmental Informatics (DEEI) of China’s State Key Laboratory of Resources and Environmental Information System based on a full physical model. The comparison and validation of the TanSat target mode observations revealed that the average of the XCO2 bias between TanSat retrievals and ground-based FTS measurements was 2.62 ppm, with a standard deviation (SD) of the mean difference of 1.41 ppm, which met the accuracy standard of 1% required by the mission tasks. With bias correction, the mean absolute error (MAE) improved to 1.11 ppm and the SD of the mean difference fell to 1.35 ppm. We compared simultaneous observations from GOSAT and OCO-2 Level 2 (L2) bias-corrected products within a ±1° latitude and longitude box centered at the ground-based FTS station in Beijing. The results indicated that measurements from GOSAT and OCO-2 were 1.8 ppm and 1.76 ppm higher than the FTS measurements on 20 June 2018, on which the daily observation bias of the TanSat XOC2 results was 1.87 ppm. These validation efforts have proven that TanSat can measure XCO2 effectively. In addition, the DEEI-retrieved XCO2 results agreed well with measurements from GOSAT, OCO-2, and the Beijing ground-based FTS. Full article
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<p>View angles and spatial distribution of TanSat target mode observations over Beijing in 2018. The <span class="html-italic">x</span>-axis is the observation time and the <span class="html-italic">y</span>-axis is the observation view angle. The left bottom inset in each panel depicts the locations of the Beijing Fourier transform spectrometer (FTS) site and TanSat footprints in degrees latitude and longitude. The red push pin represents the Beijing FTS site location. The colors indicate the measurement time in Coordinated Universal Time (UTC) of each observation.</p>
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<p>Flow chart of the Department for Eco-Environmental Informatics (DEEI) column-averaged dry-air mole fraction of carbon dioxide (XCO<sub>2</sub>) retrieval algorithm.</p>
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<p>XCO<sub>2</sub> standard deviation (SD) statistics for the different footprints of each TanSat target mode measurement. The bars are color-coded to represent the SD values for the individual footprint of each day, and the numbers are the total statistical SD values for each single-day observation.</p>
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<p>XCO<sub>2</sub> spatial distribution of TanSat target mode observations: (<b>a</b>) FTS location in Beijing and the nine footprints of the TanSat measurements; (<b>b</b>–<b>k</b>) XCO<sub>2</sub> spatial distribution retrieved from each target mode observation. The color bar in the upper right corner is the XCO<sub>2</sub> legend; the range from blue to red represents different XCO<sub>2</sub> values from low to high. The red push pin represents the Beijing FTS site.</p>
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<p>Comparison of XCO<sub>2</sub> retrieved from TanSat in target observation mode with the Beijing ground-based FTS measurements. The XCO<sub>2</sub> values of each observation date are represented by different shapes and colors; the error bars show the 1σ precision of the TanSat XCO<sub>2</sub> retrievals and the ground-based FTS measurements. The one-to-one line is solid, and the best fit line is dashed.</p>
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<p>Spatial distribution of matched GOSAT, OCO-2, and TanSat soundings around the Beijing FTS site. Push pin: Beijing FTS site position; triangles: GOSAT soundings; hollow points with crosses: OCO-2 soundings; diamonds: TanSat soundings. The color range from blue to red represents different XCO<sub>2</sub> values from low to high; red rectangle: criterion range of ±1° latitude and longitude and ±2 h measuring time.</p>
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18 pages, 3594 KiB  
Article
Assessing Soil Erosion Hazards Using Land-Use Change and Landslide Frequency Ratio Method: A Case Study of Sabaragamuwa Province, Sri Lanka
by Sumudu Senanayake, Biswajeet Pradhan, Alfredo Huete and Jane Brennan
Remote Sens. 2020, 12(9), 1483; https://doi.org/10.3390/rs12091483 - 7 May 2020
Cited by 59 | Viewed by 6865
Abstract
This study aims to identify the vulnerable landscape areas using landslide frequency ratio and land-use change associated soil erosion hazard by employing geo-informatics techniques and the revised universal soil loss equation (RUSLE) model. Required datasets were collected from multiple sources, such as multi-temporal [...] Read more.
This study aims to identify the vulnerable landscape areas using landslide frequency ratio and land-use change associated soil erosion hazard by employing geo-informatics techniques and the revised universal soil loss equation (RUSLE) model. Required datasets were collected from multiple sources, such as multi-temporal Landsat images, soil data, rainfall data, land-use land-cover (LULC) maps, topographic maps, and details of the past landslide incidents. Landsat satellite images from 2000, 2010, and 2019 were used to assess the land-use change. Geospatial input data on rainfall, soil type, terrain characteristics, and land cover were employed for soil erosion hazard classification and mapping. Landscape vulnerability was examined on the basis of land-use change, erosion hazard class, and landslide frequency ratio. Then the erodible hazard areas were identified and prioritized at the scale of river distribution zones. The image analysis of Sabaragamuwa Province in Sri Lanka from 2000 to 2019 indicates a significant increase in cropping areas (17.96%) and urban areas (3.07%), whereas less dense forest and dense forest coverage are significantly reduced (14.18% and 6.46%, respectively). The average annual soil erosion rate increased from 14.56 to 15.53 t/ha/year from year 2000 to 2019. The highest landslide frequency ratios are found in the less dense forest area and cropping area, and were identified as more prone to future landslides. The river distribution zones Athtanagalu Oya (A-2), Kalani River-south (A-3), and Kalani River- north (A-9), were identified as immediate priority areas for soil conservation. Full article
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Graphical abstract

Graphical abstract
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<p>(<b>a</b>) Location map of Sabaragamuwa Province in Sri Lanka; (<b>b</b>) digital elevation map; (<b>c</b>) slope angle map; (<b>d</b>) river distribution map.</p>
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<p>The overall methodology of the study.</p>
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<p>Land-use land-cover (LULC) maps: (<b>a</b>) 2000; (<b>b</b>) 2010; (<b>c</b>) 2019.</p>
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<p>Factor maps of Sabaragamuwa Province: (<b>a</b>) slope length and steepness (LS)-factor; (<b>b</b>) rainfall erosivity (R)-factor; (<b>c</b>) soil erodibility (K)-factor; (<b>d</b>,<b>e</b>) crop management (C) -factor and conservation practice (P)-factor; (<b>f</b>) soil erosion hazard map.</p>
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<p>Factor maps of Sabaragamuwa Province: (<b>a</b>) slope length and steepness (LS)-factor; (<b>b</b>) rainfall erosivity (R)-factor; (<b>c</b>) soil erodibility (K)-factor; (<b>d</b>,<b>e</b>) crop management (C) -factor and conservation practice (P)-factor; (<b>f</b>) soil erosion hazard map.</p>
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<p>The percentage of land-use change and landslide frequency ratio (LFR) over the river distribution zones (RDZs).</p>
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<p>(<b>a</b>) River distribution zones map; (<b>b</b>) landslide inventory map; (<b>c</b>) soil erosion hazard map with landslide locations.</p>
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<p>(<b>a</b>) Landslide frequency ratio of each RDZ; (<b>b</b>) the area covered by soil erosion hazard classes of each RDZ.</p>
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17 pages, 3106 KiB  
Technical Note
Goes-13 IR Images for Rainfall Forecasting in Hurricane Storms
by Marilu Meza-Ruiz and Alfonso Gutierrez-Lopez
Forecasting 2020, 2(2), 85-101; https://doi.org/10.3390/forecast2020005 - 30 Apr 2020
Cited by 1 | Viewed by 2452
Abstract
Currently, it is possible to access a large amount of satellite weather information from monitoring and forecasting severe storms. However, there are no methods of employing satellite images that can improve real-time early warning systems in different regions of Mexico. The auto-estimator is [...] Read more.
Currently, it is possible to access a large amount of satellite weather information from monitoring and forecasting severe storms. However, there are no methods of employing satellite images that can improve real-time early warning systems in different regions of Mexico. The auto-estimator is the most commonly used technique that was developed for specific locations in the United States of America (32°–49° latitude) for the type of convective storms. However, the estimation of precipitation intensities for meteorological conditions in tropic latitudes, using the auto-estimator technique, needs to be re-adjusted and calibrated. It is necessary to improve this type of technique that allows decision-makers to have hydro-informatic tools capable of improving early warning systems in tropical regions (15°–25° Mexican tropic latitude). The main objective of the work is to estimate rainfall from satellite imagery in the infrared (IR) spectrum from the Geostationary Operational Environmental Satellite (GOES), validating these estimates with a network of surface rain gauges. Using the GOES-13 IR images every 15 min and using the auto-estimator, a downscaling of six hurricanes was performed from which surface precipitation events were measured. The two main difficulties were to match the satellite images taken every 15 min with the surface data measured every 10 min and to develop a program in C+ that would allow the systematic analysis of the images. The results of this work allow us to get a new adjustment of coefficients in a new equation of the auto-estimator, valid for rain produced by hurricanes, something that has not been done until now. Although no universal relationship has been found for hurricane rainfall, it is evident that the original formula of the auto-estimator technique needs to be modified according to geographical latitude. Full article
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<p>Extraction of the brightness temperature value of the pixels, using the Sat-Viewer<sup>®</sup>.</p>
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<p>The relationship (R<sup>2</sup> = 0.55) between rainfall, the intensity from MGS Cancun 21 August 2007, and temperature of cloud top from the satellite image on the same date of Hurricane Dean.</p>
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<p>The relationship (R<sup>2</sup> = 0.67) between rainfall intensity from MGS Alvarado on 9 August 2012 and the temperature of cloud tops from the satellite image on the same date of Hurricane Ernesto.</p>
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<p>The relationship (R<sup>2</sup> = 0.57) between rainfall intensity from MGS Cabo San Lucas on 15 September 2014 and the temperature of cloud tops from the satellite image at the same date of Hurricane Odile.</p>
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<p>Validation of the methodology using data from Hurricane Odile, 14 (23:50) to 15 (02:10) September 2014 at MGS Cabo San Lucas, BCS. (R<sup>2</sup> = 0.9387).</p>
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<p>Validation of the methodology using data from Hurricane Patricia, 23 (22:00) to 24 (06:30) October 2015, in the MGS Atoyac, Guerrero. (R<sup>2</sup> = 0.9605).</p>
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<p>Spatial distribution of alfa parameter of Equation (3).</p>
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<p>Spatial distribution of beta parameter of Equation (3).</p>
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<p>Temporarily disaggregated series of the RR–MGS Huichapan (red line) and RR–satellite image (blue line) during the Hurricane Manuel (16 Sep 2013), Step (i).</p>
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<p>Temporarily disaggregated series of the RR–MGS Huichapan (red line) and RR–satellite image (blue line) during the Hurricane Manuel (16 Sep 2013), Step (ii).</p>
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<p>Temporarily disaggregated series of the RR–MGS Huichapan (red line) and RR–satellite image (blue line) during the Hurricane Manuel (16 Sep 2013), final step.</p>
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