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Remote Sensing in Natural Resource and Water Environment

A special issue of Remote Sensing (ISSN 2072-4292). This special issue belongs to the section "Environmental Remote Sensing".

Deadline for manuscript submissions: closed (20 December 2022) | Viewed by 100582

Special Issue Editors


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Guest Editor
School of Water and Environment, Chang’an University, Xi’an 710054, China
Interests: urban flood; flood management; hydrological modeling; water quality analysis; statistical analysis; sustainable water resource management; ecohydrology
Special Issues, Collections and Topics in MDPI journals

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Guest Editor
School of Land Engineering, Chang’an University, Xi'an 710054, China
Interests: cultivated land protection; cultivated land quality; sustainable cultivated land use
Special Issues, Collections and Topics in MDPI journals
School of Architecture, Chang’an University, Xi'an 710054, China
Interests: urban and rural planning; sustainable urban-rural form and policies; land use and transportation integration; plan evaluation
College of Geomatics, Xi’an University of Science and Technology, Xi’an 710054, China
Interests: spatiotemporal data analysis and modeling; pollutant modeling and mapping; hyperspectral remote sensing
Special Issues, Collections and Topics in MDPI journals

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Guest Editor
School of Engineering, University of California, Merced, CA 92521, USA
Interests: atershed science; landscape ecology; GIS/remote sensing; environmental policy

Special Issue Information

Dear Colleagues,

The pollutants generated by humans are severely threatening the ecosystem and the environment, owing to speedy urbanization and industrialization. Sustainable development has been seriously restricted due to a series of issues such as water pollution, air pollution, heavy metals contamination, greenhouse gas emission, and organic pollution. To address these issues, it is urgent to swiftly monitor the environmental parameters, reasonably evaluate the quality of the environment, and accurately predict the dynamics of environmental elements. Specifically, the water resources are met with unprecedented challenges because of the growing population and the increasing risk of pollution. Hence, water resources management should adjust the traditional ideas and deal with these issues using novel theory and technology for sustainable development. Alternatively, the remote sensing technology supplies a new perspective for hydrological monitoring, water resources ecological protection, and water resources planning and utilization owing to its fast detection capacity, wide spatial coverage, and multiple spectral characteristics. Remote sensing technology can be used to retrieve key ecological indicators such as NDVI, NDWI, and NDBI. Meanwhile, some previous studies took advantage of hyperspectral remote sensing to invert pollutant concentrations in soils, the air, vegetation, and water bodies. Furthermore, pollutants discharge and migration and diffusion direction can be efficiently detected by thermal infrared remote sensing technology. So, it is time to dive deep into the application of remote sensing technology in the fields of the environment. The objective of this Special Issue is to publish novel methods and views of using remote sensing techniques in the field of hydrological and water pollution. This Issue seeks to utilize the relevant methods of hydrological and water resources planning and management, including but not limited to remote sensing inversion simulation, experience method, and sustainable development.

Prof. Dr. Pingping Luo
Dr. Xindong Wei
Dr. Kanhua Yu
Dr. Bin Guo
Prof. Dr. Joshua Viers
Guest Editors

Manuscript Submission Information

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Keywords

  • Hyperspectral remote sensing in the environment
  • Retrieving air pollutant concentrations through remote sensing
  • Machine learning algorithms for modeling based on remote sensing data
  • Ecological indicators mapping by remote sensing
  • Urban stormwater models
  • Hydrologic models
  • Flood disaster
  • Water pollution
  • Wastewater treatment
  • Water resource management
  • Urban–rural management
  • Urban planning

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Related Special Issue

Published Papers (32 papers)

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21 pages, 32440 KiB  
Article
Reference-Based Super-Resolution Method for Remote Sensing Images with Feature Compression Module
by Jiayang Zhang, Wanxu Zhang, Bo Jiang, Xiaodan Tong, Keya Chai, Yanchao Yin, Lin Wang, Junhao Jia and Xiaoxuan Chen
Remote Sens. 2023, 15(4), 1103; https://doi.org/10.3390/rs15041103 - 17 Feb 2023
Cited by 5 | Viewed by 2311
Abstract
High-quality remote sensing images play important roles in the development of ecological indicators’ mapping, urban-rural management, urban planning, and other fields. Compared with natural images, remote sensing images have more abundant land cover along with lower spatial resolutions. Given the embedded longitude and [...] Read more.
High-quality remote sensing images play important roles in the development of ecological indicators’ mapping, urban-rural management, urban planning, and other fields. Compared with natural images, remote sensing images have more abundant land cover along with lower spatial resolutions. Given the embedded longitude and latitude information of remote sensing images, reference (Ref) images with similar scenes could be more accessible. However, existing traditional super-resolution (SR) approaches always depend on increases in network depth to improve performance, which limits the acquisition and application of high-quality remote sensing images. In this paper, we proposed a novel, reference-image-based, super-resolution method with feature compression module (FCSR) for remote sensing images to alleviate the above issue while effectively utilizing high-resolution (HR) information from Ref images. Specifically, we exploited a feature compression branch (FCB) to extract relevant features in feature detail matching with large measurements. This branch employed a feature compression module (FCM) to extract features from low-resolution (LR) and Ref images, which enabled texture transfer from different perspectives. To decrease the impact of environmental factors such as resolution, brightness and ambiguity disparities between the LR and Ref images, we designed a feature extraction encoder (FEE) to ensure accuracy in feature extraction in the feature acquisition branch. The experimental results demonstrate that the proposed FCSR achieves significant performance and visual quality compared to state-of-the-art SR methods. Explicitly, when compared with the best method, the average peak signal-to-noise ratio (PSNR) index on the three test sets is improved by 1.0877%, 0.8161%, 1.0296%, respectively, and the structural similarity (SSIM) index on four test sets is improved by 1.4764%, 1.4467%, 0.0882%, and 1.8371%, respectively. Simultaneously, FCSR obtains satisfactory visual details following qualitative evaluation. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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Graphical abstract

Graphical abstract
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<p>Overall framework of our FCSR method. This consists of three components: content extractor, similar feature acquisition, and texture transfer. Similar feature acquisition provided supplementary information according to the feature premise, and the matching and exchange between the LR and Ref image occurred to ensure texture transfer and reconstruct SR images.</p>
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<p>The architecture of the proposed modules. (<b>a</b>) texture swapping branch; (<b>b</b>) feature compression branch (FCB). The FCB is composed of a feature compression module (FCM) and texture swapping branch. FCM employs SVD to adaptively offer complementary information between the LR and Ref images. The texture swapping branch furnishes multi-level features, which are displayed as Level 1 features, Level 2 features, and Level 3 features.</p>
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<p>The structure of a multi-level self-encoder. FEE is the coding portion of the multi-level self-encoder. When pretrained with remote sensing images, FEE is prone to extracting appropriately similar features from the LR and Ref images.</p>
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<p>Examples of RRSSRD training set. The first and third rows represent HR images while the second and fourth rows represent Ref images. Specifically, HR images in the first row correspond to Ref images in the second row, and HR images in the third row correspond to Ref images in the fourth row.</p>
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<p>Visual comparison of some typical SR methods and our model of ×4 factor on the first test set. The results of comparison methods originate from [<a href="#B30-remotesensing-15-01103" class="html-bibr">30</a>]. We enlarge the image details inside the light red rectangle and show in the red rectangle in the upper right corner.</p>
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<p>Visualization results of average PSNR and SSIM values for diverse SR methods of ×4 factor. (<b>a</b>) PSNR and SSIM on 1st test set; (<b>b</b>) PSNR and SSIM on 2nd test set; (<b>c</b>) PSNR and SSIM on 3rd test set; (<b>d</b>) PSNR and SSIM on 4th test set.</p>
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<p>Visual comparison between SRNTT and SRNTT+FCB of ×4 factor on diverse test sets. We enlarge the image details inside the light red rectangle and show in the red rectangle in the upper right corner.</p>
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<p>Visual comparison between FCGSR and our FCSR method of ×4 factor on various test sets. We enlarge the image details inside the light red rectangle and show in the red rectangle in the upper right corner.</p>
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<p>Visual comparison between FCSR-rec and the proposed method of ×4 factor on diverse test sets. FCSR-rec denotes only using reconstruction loss when training FCSR. We enlarge the image details inside the light red rectangle and show in the red rectangle in the upper right corner.</p>
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22 pages, 14984 KiB  
Article
Ecological Security Patterns at Different Spatial Scales on the Loess Plateau
by Liangguo Lin, Xindong Wei, Pingping Luo, Shaini Wang, Dehao Kong and Jie Yang
Remote Sens. 2023, 15(4), 1011; https://doi.org/10.3390/rs15041011 - 12 Feb 2023
Cited by 33 | Viewed by 2693
Abstract
The study of ecological security patterns (ESPs) is of great significance for improving the value of ecosystem services and promoting both ecological protection and high-quality socio-economic development. As an important part of the “Loss Plateau-Sichuan-Yunnan Ecological Barrier” and “Northern Sand Control Belt” in [...] Read more.
The study of ecological security patterns (ESPs) is of great significance for improving the value of ecosystem services and promoting both ecological protection and high-quality socio-economic development. As an important part of the “Loss Plateau-Sichuan-Yunnan Ecological Barrier” and “Northern Sand Control Belt” in the national security strategic pattern, there is an urgent need to study the ESPs on the Loess Plateau. Based on a remote sensing dataset, this study identified the ESPs at different spatial scales, and analyzed the similarities and differences of ecological sources, corridors, and key strategic points, so as to better inform the development and implantation of macro and micro ecological protection strategies. When taken as a whole unit, we identified 58 ecological sources (areas with higher levels of ecosystem services) on the Loess Plateau (total area of 57,948.48 km2), along with 134 corridors (total length of 14,094.32 km), 1325 pinch points (total area of 315.01 km2), and 2406 barrier points (total area of 382.50 km2). When splits into ecoregions, we identified 108 sources (total area of 67,892.51 km2), 226 corridors (total length of 13,403.49 km), 2801 pinch points (total area of 851.07 km2, and 3657 barrier points (total area of 800.70 km2). Human activities and land use types are the main factors influencing the number and spatial distribution of corridors, ecological pinch points, and barrier points. ESPs constructed at different spatial scales are broadly similar, but significant differences among details were identified. As such, when formulating ecological protection and restoration strategies, the spatial scale should be considered. Moreover, specific programs should be determined based on ESP characteristics to maximize the protection of biodiversity and ecosystem integrity from multiple perspectives and directions. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Geographical location, land cover, and ecoregions of the Loess Plateau. (<b>a</b>) shows the spatial distribution of land cover on the Loess Plateau. (<b>b</b>) shows the spatial location of six ecoregions (including two sub-regions) of the Loess Plateau.</p>
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<p>Framework for identifying key areas of ecological conservation and restoration.</p>
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<p>Spatial distribution pattern of ecosystem services on the Loess Plateau.</p>
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<p>Landscape Pattern Index of the Loess Plateau and all ecoregions.</p>
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<p>Spatial distribution of ecological sources on the Loess Plateau.</p>
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<p>Spatial distribution of ecological sources in each ecoregion.</p>
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<p>Spatial distribution of ecological resistance surface in each ecoregion.</p>
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<p>Spatial distribution of ecological security patterns (ESPs) on the Loess Plateau. (<b>a</b>) shows the whole ESPs of the Loess Plateau, and (<b>b</b>) shows the location diagram of local ESPs of the Loess Plateau.</p>
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<p>Land used areas of pinch points and barrier points in the Loess Plateau.</p>
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<p>Spatial distribution of ecological security patterns (ESPs) in each ecoregion.</p>
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<p>Land use areas of pinch points and barrier points in each ecoregion.</p>
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18 pages, 200819 KiB  
Article
A Numerical Assessment and Prediction for Meeting the Demand for Agricultural Water and Sustainable Development in Irrigation Area
by Qiying Zhang, Hui Qian, Panpan Xu, Rui Liu, Xianmin Ke, Alex Furman and Jiatao Shang
Remote Sens. 2023, 15(3), 571; https://doi.org/10.3390/rs15030571 - 18 Jan 2023
Cited by 2 | Viewed by 1706
Abstract
The demand for agricultural water is a growing problem in irrigated regions across the globe, particularly in arid and semi-arid regions. Changes in the level of groundwater in irrigation districts will affect the flow of surface water connected to the aquifer, which may [...] Read more.
The demand for agricultural water is a growing problem in irrigated regions across the globe, particularly in arid and semi-arid regions. Changes in the level of groundwater in irrigation districts will affect the flow of surface water connected to the aquifer, which may damage the sustainability of water resources and ecosystems. In this study, a two-dimensional unsteady flow model based on MODFLOW was constructed and three scenarios were established to assess the demand for agricultural water in the Jiaokou Irrigation District. The results show that the groundwater in the study area is basically balanced. However, the supply of irrigation water for summer irrigation is insufficient. The results of the model prediction indicate that when groundwater is primarily used for irrigation (scenario 1), the maximum water level decrease is 25 m, which is beyond this limit (15 m). When the ratio of groundwater to surface water is 2:1 for irrigation (scenario 2), the largest decrease in water level is approximately 10 m. Scenario 3 is proposed based on the Hanjiang-to-Weihe River Valley Water Diversion Project to prevent the salinization of soil owing to the rise in water level, and its result shows that the maximum decrease and buried depth are approximately 5 m and above 3 m, respectively, indicating that the scenario is more reasonable and sustainable. These findings provide theoretical guidance to protect water resources and prevent water pollution and should serve as a reference for rationally allocating water resources in other irrigation districts in arid and semi-arid areas. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Study area map showing (<b>a</b>) locations and geomorphology, (<b>b</b>) meteorological elements, including precipitation (P), evaporation (E), and temperature (T), (<b>c</b>) stratigraphic profile, and (<b>d</b>) aquifer thickness.</p>
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<p>Map of the distribution of canal system and drainage ditches in the Jiaokou Irrigation District.</p>
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<p>Maps that show the model parameter partition: (<b>a</b>) hydraulic conductivity; (<b>b</b>) recharge area map. See <a href="#app1-remotesensing-15-00571" class="html-app">Table S2</a> for the specific assignment of recharge.</p>
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<p>(<b>a</b>) Digital elevation model of ground surface in the simulation area; (<b>b</b>) The initial head diagram of the study area; (<b>c</b>) Comparison chart between the model running results and actual measured water level above mean sea level.</p>
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<p>Model simulations—scenarios 1, 2, and 3.</p>
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<p>The relationship between crop water demand and supply.</p>
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<p>Maps that show the (<b>a</b>) decrease in water level and (<b>b</b>) buried depth after 50 years for scenario 1.</p>
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<p>Maps showing the (<b>a</b>) decrease in water level and (<b>b</b>) buried depth after 50 years for scenario 2.</p>
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<p>Maps showing the trend in change in water level of (<b>a</b>) G-5, (<b>b</b>) G-7, and (<b>c</b>) G-9 observation well for scenario 2.</p>
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<p>The decrease in groundwater level after (<b>a</b>) 20 years and (<b>b</b>) 30 years of water level restoration.</p>
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<p>Maps that show the (<b>a</b>) decrease in water level and (<b>b</b>) buried depth after 50 years for scenario 3.</p>
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<p>Maps that show the trend in change in the water level of (<b>a</b>) G-5, (<b>b</b>) G-7, and (<b>c</b>) G-9 observation wells for scenario 3.</p>
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21 pages, 8935 KiB  
Article
Flood Runoff Simulation under Changing Environment, Based on Multiple Satellite Data in the Jinghe River Basin of the Loess Plateau, China
by Jiqiang Lyu, Shanshan Yin, Yutong Sun, Kexin Wang, Pingping Luo and Xiaolan Meng
Remote Sens. 2023, 15(3), 550; https://doi.org/10.3390/rs15030550 - 17 Jan 2023
Cited by 10 | Viewed by 2387
Abstract
Understanding the hydrological surface condition changes, climate change and their combined impacts on flood runoff are critical for comprehending the hydrology under environmental changes and for solving future flood management challenges. This study was designed to examine the relative contributions of the hydrological [...] Read more.
Understanding the hydrological surface condition changes, climate change and their combined impacts on flood runoff are critical for comprehending the hydrology under environmental changes and for solving future flood management challenges. This study was designed to examine the relative contributions of the hydrological surface condition changes and climate change in the flood runoff of a 45,421-km2 watershed in the Loess Plateau region. Statistical analytical methods, including Kendall’s trend test, the Theisen median trend analysis, and cumulative anomaly method, were used to detect trends in the relationship between the climatic variables, the normalized difference vegetation index (NDVI), land use/cover change (LUCC) data, and observed flood runoff. A grid-cell distributed rainfall–runoff model was used to detect the quantitative hydrologic responses to the climatic variability and land-use change. We found that climatic variables were not statistically significantly different (p > 0.05) over the study period. From 1985 to 2013, the cropland area continued to decrease, while the forest land, pastures, and residential areas increased in the Jinghe River Basin. Affected by LUCC and climate change, the peak discharges and flood volumes decreased by 8–22% and 5–67%, respectively. This study can provide a reference for future land-use planning and flood runoff control policy formulation and for revision in the study area. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Geographic location of the JRB and its weather and gauge stations.</p>
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<p>The technological route and research method employed in the current study.</p>
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<p>MCDRM model structure and schematic diagram.</p>
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<p>The diagram of the mechanism of surface–subsurface slope runoff generation.</p>
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<p>The relationship between the water depth and the unit width discharge (<span class="html-italic">q</span>-<span class="html-italic">d</span>) in each grid.</p>
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<p>Trend chart of P<sub>flood season</sub> to the annual precipitation in the JRB, from 1970 to 2015; y<sub>1</sub>: the trend line of the proportion of P<sub>flood season</sub> to the annual precipitation in the natural period 1970–1978; y<sub>2</sub>: the trend line of the proportion of P<sub>flood season</sub> to the annual precipitation in the human activity interference period (I) 1979–1990; y<sub>3</sub>: the trend line of the proportion of P<sub>flood season</sub> to the annual precipitation in the human activity interference period (II) 1991–1998; y<sub>4</sub>: the trend line of the proportion of P<sub>flood season</sub> to the annual precipitation in the human activity interference period (III) 1999–2013.</p>
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<p>Spatial distribution map of the precipitation in flood season; (<b>a</b>) natural period 1970–1978; (<b>b</b>) human activity interference period (I) 1979–1990; (<b>c</b>) human activity interference period (II) 1991–1998; (<b>d</b>) human activity interference period (III) 1999–2013.</p>
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<p>Land use in the human activity interference periods of the study; (<b>a</b>) land use in 1985; (<b>b</b>) land use in 1991; (<b>c</b>) land use in 1999; (<b>d</b>) land use in 2013.</p>
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<p>Change in the proportion of the six land use types, from 1985 to 2013.</p>
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<p>NDVI changes in the JRB, from 1998 to 2018.</p>
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<p>(<b>a</b>) Spatial distribution of the NDVI mean. (<b>b</b>) Annual mean NDVI variation trend.</p>
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<p>Diagram of the typical flooding process simulation in the JRB; (<b>a</b>) Date of event onset is 25/7/1975; (<b>b</b>) Date of event onset is 30/7/1990; (<b>c</b>) Date of event onset is 7/7/1994; (<b>d</b>) Date of event onset is 7/7/1996.</p>
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<p>Simulation diagram of the flooding process in the Basin under the changing environment; (<b>a</b>) Date of event onset is 4/8/1993; (<b>b</b>) Date of event onset is 7/7/1994; (<b>c</b>) Date of event onset is 5/8/1995; (<b>d</b>) Date of event onset is 7/7/1996; (<b>e</b>) Date of event onset is 6/7/1998; (<b>f</b>) Date of event onset is 24/8/2003; (<b>g</b>) Date of event onset is 20/7/2005; (<b>h</b>) Date of event onset is 23/7/2010; (<b>i</b>) Date of event onset is 8/7/2013.</p>
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17 pages, 27331 KiB  
Article
Improved Surface Soil Organic Carbon Mapping of SoilGrids250m Using Sentinel-2 Spectral Images in the Qinghai–Tibetan Plateau
by Jiayi Yang, Junjian Fan, Zefan Lan, Xingmin Mu, Yiping Wu, Zhongbao Xin, Puqiong Miping and Guangju Zhao
Remote Sens. 2023, 15(1), 114; https://doi.org/10.3390/rs15010114 - 25 Dec 2022
Cited by 12 | Viewed by 2944
Abstract
Soil organic carbon (SOC) is a critical indicator for the global carbon cycle and the overall carbon pool balance. Obtaining soil maps of surface SOC is fundamental to evaluating soil quality, regulating climate change, and global carbon cycle modeling. However, efficient approaches for [...] Read more.
Soil organic carbon (SOC) is a critical indicator for the global carbon cycle and the overall carbon pool balance. Obtaining soil maps of surface SOC is fundamental to evaluating soil quality, regulating climate change, and global carbon cycle modeling. However, efficient approaches for obtaining accurate SOC information remain challenging, especially in remote or inaccessible regions of the Qinghai–Tibet Plateau (QTP), which is influenced by complex terrains, climate change, and human activities. This study employed field measurements, SoilGrids250m (SOC_250m, a spatial resolution of 250 m × 250 m), and Sentinel-2 images with different machine learning methods to map SOC content in the QTP. Four machine learning methods including partial least squares regression (PLSR), support vector machines (SVM), random forest (RF), and artificial neural network (ANN) were used to construct spatial prediction models based on 396 field-collected sampling points and various covariates from remote sensing images. Our results revealed that the RF model outperformed the PLSR, SVM, and ANN models, with a higher determination coefficient (R2 of 0.82 is from the training datasets) and the ratio of performance to deviation (RPD = 2.54). The selected covariates according to the variable importance in projection (VIP) were: SOC_250m, B2, B11, Soil-Adjusted Vegetation Index (SAVI), Normalized Difference Vegetation Index (NDVI), B5, and Soil-Adjusted Total Vegetation Index (SATVI). The predicted SOC map showed an overall decrease in SOC content ranging from 69.30 g·kg−1 in the southeast to 1.47 g·kg−1 in the northwest. Our prediction showed spatial heterogeneity of SOC content, indicating that Sentinel-2 images were acceptable for characterizing the variability of SOC. The findings provide a scientific basis for carbon neutrality in the QTP and a reference for the digital mapping of SOC in the alpine region. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Distribution of sampling points in the QTP.</p>
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<p>Methodological flowchart for SOC prediction.</p>
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<p>Predicted and observed SOC for the calibration dataset.</p>
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<p>The variable importance projection values distribution in RF.</p>
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<p>RF accuracy during the variable selection process using the different numerous trees (n<sub>tree</sub>).</p>
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<p>Spatial variability of SOC in the QTP.</p>
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<p>Comparison of SOC mapping results with the existing maps ((<b>a</b>) HWSD, (<b>b</b>) Li’s prediction, (<b>c</b>) Our prediction).</p>
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<p>Comparisons of (<b>a</b>) HWSD, (<b>b</b>) Li’s prediction, (<b>c</b>) Our prediction, and (<b>d</b>) true color image.</p>
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17 pages, 5930 KiB  
Article
Remote Sensing-Supported Flood Forecasting of Urbanized Watersheds—A Case Study in Southern China
by Yu Gu, Yangbo Chen, Huaizhang Sun and Jun Liu
Remote Sens. 2022, 14(23), 6129; https://doi.org/10.3390/rs14236129 - 3 Dec 2022
Cited by 5 | Viewed by 1887
Abstract
Urbanization has significant impacts on watershed hydrology, but previous studies have been confirmatory and not comprehensive; in particular, few studies have addressed the impact of urbanization on flooding in highly urbanized watersheds. In this study, this effect is studied in Chebei Creek, a [...] Read more.
Urbanization has significant impacts on watershed hydrology, but previous studies have been confirmatory and not comprehensive; in particular, few studies have addressed the impact of urbanization on flooding in highly urbanized watersheds. In this study, this effect is studied in Chebei Creek, a highly urbanized watershed in the Pearl River Delta, southern China. Landsat satellite images acquired in 2015 were used to estimate land use and cover changes using the Decision Tree (DT) C4.5 classification algorithm, while the Liuxihe model, a physically based distributed hydrological model (PBDHM), is employed to simulate watershed flooding and hydrological processes. For areas with high degrees of urbanization, the duration of the flood peak is only 1 h, and the flood water level shows steep rises and falls. These characteristics increase the difficulty of flood modeling and forecasting in urbanized areas. At present, hydrological research in urbanized watersheds generally focuses on the quantitative simulation of runoff from urban areas to the watershed, flood flows, peak flood flow, and runoff depth. Few studies have involved real-time flood forecasting in urbanized watersheds. To achieve real-time flood forecasting in urbanized watersheds, PBDHMs and refined underlying surface data based on remote sensing technology are necessary. The Liuxihe model is a PBDHM that can meet the accuracy requirements of inflow flood forecasting for reservoir flood control operations. The accuracies of the two flood forecasting methods used in this study were 83.95% and 97.06%, showing the excellent performance of the Liuxihe model for the real-time flood forecasting of urbanized rivers such as the Chebei Creek watershed. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Framework of the Liuxihe model.</p>
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<p>Location and map of the Chebei Creek watershed.</p>
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<p>DEM of the Chebei Creek watershed produced using a 1:10,000 vector topographic map of Guangzhou City.</p>
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<p>LUC types of the Chebei Creek watershed. (<b>a</b>) 2015 automated LUC; (<b>b</b>) 2015 corrected LUC.</p>
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<p>Soil map of the Chebei Creek watershed: (<b>a</b>) 1987 soil type map from the FAO dataset; (<b>b</b>) updated 1987 soil type map with estimated LUC; (<b>c</b>) 2015 soil type map with estimated LUC.</p>
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<p>Liuxihe model structures in the Chebei Creek watershed. (<b>a</b>) Spatial location of the Chebei Creek sub-watershed; (<b>b</b>) model structure based on the Chebei Creek sub-watershed.</p>
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<p>Results of the parameter optimization of the Liuxihe model with the particle swarm optimization (PSO) algorithm. (<b>a</b>) Change curve of the objective function; (<b>b</b>) parameter evolution process.</p>
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<p>Parameter optimization and simulation processes for representative floods. (<b>a</b>) The parameter optimization flood (No. 2021060211); and the simulation floods: (<b>b</b>) No. 2021053114, (<b>c</b>) No. 2021061308, and (<b>d</b>) No. 2021062203.</p>
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<p>Parameter optimization and simulation processes for representative floods. (<b>a</b>) The parameter optimization flood (No. 2021060211); and the simulation floods: (<b>b</b>) No. 2021053114, (<b>c</b>) No. 2021061308, and (<b>d</b>) No. 2021062203.</p>
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<p>Three rounds of forecasts for the flood 15 June 2022. (<b>a</b>) First-round forecast results; (<b>b</b>) second-round rolling forecast results; and (<b>c</b>) third-round rolling forecast results.</p>
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<p>Three rounds of forecasts for the flood 2 July 2022. (<b>a</b>) First-round forecast results; (<b>b</b>) second-round rolling forecast results; and (<b>c</b>) third-round rolling forecast results.</p>
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17 pages, 4525 KiB  
Article
Reconstruction of Historical Land Use and Urban Flood Simulation in Xi’an, Shannxi, China
by Shuangtao Wang, Pingping Luo, Chengyi Xu, Wei Zhu, Zhe Cao and Steven Ly
Remote Sens. 2022, 14(23), 6067; https://doi.org/10.3390/rs14236067 - 30 Nov 2022
Cited by 30 | Viewed by 2510
Abstract
Reconstruction of historical land uses helps to understand patterns, drivers, and impacts of land-use change, and is essential for finding solutions to land-use sustainability. In order to analyze the relationship between land-use change and urban flooding, this study used the Classification and Regression [...] Read more.
Reconstruction of historical land uses helps to understand patterns, drivers, and impacts of land-use change, and is essential for finding solutions to land-use sustainability. In order to analyze the relationship between land-use change and urban flooding, this study used the Classification and Regression Tree (CART) method to extract modern (2017) land-use data based on remote sensing images. Then, the Paleo-Land-Use Reconstruction (PLUR) program was used to reconstruct the land-use maps of Xi’an during the Ming (1582) and Qing (1766) dynasties by consulting and collecting records of land-use change in historical documents. Finally, the Flo-2D model was used to simulate urban flooding under different land-use scenarios. Over the past 435 years (1582–2017), the urban construction land area showed a trend of increasing, while the unused land area and water bodies were continuously decreasing. The increase in urban green space and buildings was 20.49% and 19.85% respectively, and the unused land area changed from 0.32 km2 to 0. Urban flooding in the modern land-use scenario is the most serious. In addition to the increase in impervious areas, the increase in building density and the decrease in water areas are also important factors that aggravate urban flooding. This study can provide a reference for future land-use planning and urban flooding control policy formulation and revision in the study area. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Location and remote sensing image of the study area.</p>
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<p>Historical Land-Use Reconstruction Process Using the PLUR Program.</p>
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<p>DEM of the study area. (<b>a</b>) Untreated; (<b>b</b>) Ming dynasty; (<b>c</b>) Qing dynasty; (<b>d</b>) Modern.</p>
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<p>The different design hyetographs.</p>
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<p>Land use in the three periods of the study.</p>
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<p>Land use in the three periods of the study.</p>
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<p>Land-use change Statistics.</p>
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<p>Distribution of the maximum inundation depth of the “20160724” rainstorm.</p>
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<p>The total amount of surface water volume under the designed rainstorm in different periods.</p>
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<p>(<b>a</b>) level II and (<b>b</b>) level III inundation area.</p>
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<p>Variation process of the inundation depth of the maximum water accumulation point in (<b>a</b>) 10-year recurrence period; (<b>b</b>) 20-year recurrence period; (<b>c</b>) 50-year recurrence period; (<b>d</b>) 100-year recurrence period.</p>
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16 pages, 3792 KiB  
Article
Research on Sediment Discharge Variations and Driving Factors in the Tarim River Basin
by Zhaoxia Ye, Yaning Chen, Qifei Zhang, Yongchang Liu and Xueqi Zhang
Remote Sens. 2022, 14(22), 5848; https://doi.org/10.3390/rs14225848 - 18 Nov 2022
Cited by 4 | Viewed by 2249
Abstract
Sediment discharge is widely regarded as a critical indicator of soil and water loss. The Mann–Kendall (M-K) test was applied to analyze the trends of temperature, precipitation, annual runoff, annual sediment discharge (ASD), and snow cover area proportion (SCAP). Sensitivity coefficient and contribution [...] Read more.
Sediment discharge is widely regarded as a critical indicator of soil and water loss. The Mann–Kendall (M-K) test was applied to analyze the trends of temperature, precipitation, annual runoff, annual sediment discharge (ASD), and snow cover area proportion (SCAP). Sensitivity coefficient and contribution rate were adopted to assess the sensitivity of ASD to driving factors, and the contribution of driving factors to ASD. The results showed: (1) ASD of the Kaidu River and the Aksu River originating from Tien Shan decreased at rates of 3.8503 × 107 kg per year (p < 0.01) and 47.198 × 107 kg per year, respectively, from 2001 to 2019. The ASD there was also found to be more sensitive to SCAP changes in autumn and winter, respectively. (2) ASD of the Yarkand River and the Yulong Kashgar River originating from the Karakoram Mountains increased at rates of 21.807 × 107 kg per year and 27.774 × 107 kg per year, respectively, during 2001–2019. The ASD there was determined to be more sensitive to annual runoff. (3) In terms of contribution rate, except for the Kaidu River, annual runoff of the other three rivers made the largest contribution. (4) In addition, the proportion of glacial-melt water, slope, glacierization and human activities are also possible factors affecting sediment discharge. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Study area of the Tarim River Basin. Note: The letter R means river.</p>
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<p>Annual sediment discharge and suspended sediment concentration at the main rivers of the TRB.</p>
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<p>Intra-annual variation of sediment discharge at the main rivers of the TRB.</p>
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<p>Average annual and monthly SCAP in the Kaidu River Basin, the Aksu River Basin, the Yarkand River Basin, and the Yulong Kashgar River Basin over the period of 2001–2019. (<b>a</b>) Spatial averaged SCAP in the Tarim River Basin; (<b>b</b>) monthly SCAP in different sub-basins of the Tarim River Basin.</p>
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<p>Variations of maximum, average, and minimum SCAP in the Tarim River Basin during 2001–2019.</p>
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<p>Seasonal variations of SCAP in the Tarim River Basin from 2001 to 2019.</p>
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16 pages, 5201 KiB  
Article
Using a Two-Stage Scheme to Map Toxic Metal Distributions Based on GF-5 Satellite Hyperspectral Images at a Northern Chinese Opencast Coal Mine
by Bin Guo, Xianan Guo, Bo Zhang, Liang Suo, Haorui Bai and Pingping Luo
Remote Sens. 2022, 14(22), 5804; https://doi.org/10.3390/rs14225804 - 17 Nov 2022
Cited by 4 | Viewed by 2169
Abstract
Toxic metals have attracted great concern worldwide due to their toxicity and slow decomposition. Although metal concentrations can be accurately obtained with chemical methods, it is difficult to map metal distributions on a large scale due to their inherently low efficiency and high [...] Read more.
Toxic metals have attracted great concern worldwide due to their toxicity and slow decomposition. Although metal concentrations can be accurately obtained with chemical methods, it is difficult to map metal distributions on a large scale due to their inherently low efficiency and high cost. Moreover, chemical analysis methods easily lead to secondary contamination. To address these issues, 110 topsoil samples were collected using a soil sampler, and positions for each sample were surveyed using a global navigation satellite system (GNSS) receiver from a coal mine in northern China. Then, the metal contents were surveyed in a laboratory via a portable X-ray fluorescence spectroscopy (XRF) device, and GaoFen-5 (GF-5) satellite hyperspectral images were used to retrieve the spectra of the soil samples. Furthermore, a Savitzky–Golay (SG) filter and continuous wavelet transform (CWT) were selected to smooth and enhance the soil reflectance. Competitive adaptive reweighted sampling (CARS) and Boruta algorithms were utilized to identify the feature bands. The optimum two-stage method, consisting of the random forest (RF) and ordinary kriging (OK) methods, was used to infer the metal concentrations. The following outcomes were achieved. Firstly, both zinc (Zn) (68.07 mg/kg) and nickel (Ni) (26.61 mg/kg) surpassed the regional background value (Zn: 48.60 mg/kg, Ni: 19.5 mg/kg). Secondly, the optimum model of RF, combined with the OK (RFOK) method, with a relatively higher coefficient of determination (R2) (R2 = 0.60 for Zn, R2 = 0.30 for Ni), a lower root-mean-square error (RMSE) (RMSE = 12.45 mg/kg for Zn, RMSE = 3.97 mg/kg for Ni), and a lower mean absolute error (MAE) (MAE = 9.47 mg/kg for Zn, MAE = 3.31mg/kg for Ni), outperformed the other four models, including the RF, OK, inverse distance weighted (IDW) method, and the optimum model of RF combined with IDW (RFIDW) method in estimating soil Zn and Ni contents, respectively. Thirdly, the distribution of soil Zn and Ni concentrations obtained from the best-predicted method and the GF-5 satellite hyperspectral images was in line with the actual conditions. This scheme proves that satellite hyperspectral images can be used to directly estimate metal distributions, and the present study provides a scientific base for mapping heavy metal spatial distribution on a relatively large scale. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>The flowchart of this study.</p>
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<p>The map of soil sampling sites; (<b>a</b>,<b>b</b>) show photos of the areas of the sampling field.</p>
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<p>Histograms and box plots of Zn and Ni concentrations (No. of samples = 110). (Note: The red curve is the fitting line; “+” denotes outliers.)</p>
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<p>Original and pretreated soil reflectance curves. (Notes: (<b>a</b>) OR is the original soil reflectance curve; (<b>b</b>) SG denotes the soil reflectance curve smoothed by SG; (<b>c</b>–<b>l</b>) L1–L10 are the reconstructed spectra using CWT at decomposition scales of 1–10).</p>
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<p>The position of feature bands for Zn and Ni based on the CARS algorithm.</p>
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<p>The position of feature bands for Zn and Ni based on the Boruta algorithm.</p>
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<p>Evaluating RF model performance at each decomposition scale of CWT.</p>
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<p>Scatter plots for the optimum inversion models. (Note: (<b>a</b>) and (<b>b</b>) represent Zn and Ni, respectively.)</p>
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<p>Spatial distribution maps of Zn contents in the research area.</p>
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<p>Spatial distribution maps of Ni contents in the study area.</p>
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16 pages, 2184 KiB  
Article
Urban Flood-Related Remote Sensing: Research Trends, Gaps and Opportunities
by Wei Zhu, Zhe Cao, Pingping Luo, Zeming Tang, Yuzhu Zhang, Maochuan Hu and Bin He
Remote Sens. 2022, 14(21), 5505; https://doi.org/10.3390/rs14215505 - 1 Nov 2022
Cited by 20 | Viewed by 4997
Abstract
As a result of urbanization and climate change, urban areas are increasingly vulnerable to flooding, which can have devastating effects on the loss of life and property. Remote sensing technology can provide practical help for urban flood disaster management. This research presents a [...] Read more.
As a result of urbanization and climate change, urban areas are increasingly vulnerable to flooding, which can have devastating effects on the loss of life and property. Remote sensing technology can provide practical help for urban flood disaster management. This research presents a review of urban flood-related remote sensing to identify research trends and gaps, and reveal new research opportunities. Based on the Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA), the systematic literature search resulted in 347 documents classified as geography, disaster management application, and remote sensing data utilization. The main results include 1. most of the studies are located in high-income countries and territories and inland areas; 2. remote sensing for observing the environment was more popular than observing the building; 3. the most often applied disaster management activities were vulnerability assessment and risk modeling (mitigation) and rapid damage assessment (response); 4. DEM is often applied to simulate urban floods as software inputs. We suggest that future research directions include 1. coastal urban study areas in non-high-income countries/territories to help vulnerable populations; 2. understudied disaster management activities, which often need to observe the buildings in more urban areas; 3. data standardization will facilitate integration with international standard methods for assessing urban floods. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>PRISMA flow diagram.</p>
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<p>Number of documents per publication year.</p>
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<p>The number of articles and World Bank economy classification for study area country/territory.</p>
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<p>Number of articles corresponding to observations.</p>
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<p>Remote sensing data type: the number of documents (<b>a</b>) all publication years; (<b>b</b>) each publication year. Remote sensing data analysis method: the number of documents (<b>c</b>) all publication years; (<b>d</b>) each publication year.</p>
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21 pages, 10042 KiB  
Article
Spatially Non-Stationary Relationships between Changing Environment and Water Yield Services in Watersheds of China’s Climate Transition Zones
by Zhe Cao, Wei Zhu, Pingping Luo, Shuangtao Wang, Zeming Tang, Yuzhu Zhang and Bin Guo
Remote Sens. 2022, 14(20), 5078; https://doi.org/10.3390/rs14205078 - 11 Oct 2022
Cited by 21 | Viewed by 2650
Abstract
Identifying the spatial and temporal heterogeneity of water-related ecosystem services and the mechanisms influencing them is essential for optimizing ecosystem governance and maintaining watershed sustainable development. However, the complex and undiscovered interplay between human activities and natural factors underpins the solutions to the [...] Read more.
Identifying the spatial and temporal heterogeneity of water-related ecosystem services and the mechanisms influencing them is essential for optimizing ecosystem governance and maintaining watershed sustainable development. However, the complex and undiscovered interplay between human activities and natural factors underpins the solutions to the water scarcity and flooding challenges faced by climate transition zone basins. This study used a multiple spatial-scale analysis to: (i) quantify the spatial and temporal variations of the water yield ecosystem service (WYs) of the Wei River Basin (WRB) from 2000 to 2020 using the InVEST model and remote sensing data; and (ii) look at how human activities, climate, topography, and vegetation affect the WYs at the climate transition zone sub-catchment scale using the geographical detector model and multi-scale geographically weighted regression (MGWR). The conclusive research reveals that there would be a gradual increase in WYs between the years 2000 and 2020, as well as a distinct and very different spatial aggregation along the climatic divide. The average yearly precipitation was shown to be particularly linked to the water yield of the WRB. The interplay of human, climatic, plant, and terrain variables has a substantially higher influence than most single factors on the geographical differentiation of WYs. Bivariate enhancement and non-linear enhancement are the most common types of factor interactions. This shows that there are significant interactions between natural and human variables. Our study shows that precipitation and temperature are the main factors that cause WYs in the semi-arid zone. In the semi-humid zone, precipitation and vegetation are the key controlling factors that cause WYs. We provide new perspectives for understanding and optimizing ecosystem management by comparing the drivers of WYS in sub-basins with different climatic conditions. Based on the findings, we recommend that particular attention should be paid to ecosystem restoration practices in watersheds in climatic transition zones. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Geographical location of the study area and the sub-basins in the WRB. The whole basin is divided into five sub-basins: 1. The Beiluo River; 2. The Jing River; 3. The upper reach of the Wei River basin; 4. The middle reach of the Wei River basin; and 5. The lower reach of the Wei River basin.</p>
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<p>Annual precipitation, actual evapotranspiration and water yield service in the Wei River basin from 2000–2020.</p>
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<p>Spatial pattern of WYs in Wei River basin from 2000 to 2020.</p>
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<p>Univariate LISA maps of WYs in 2000–2020.</p>
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<p>The synergistic contribution of potential impact factors to water yield services. * represents bivariate enhancement; # represents non-linear enhancement.</p>
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<p>A combined plot of regression coefficients of drivers derived from the MGWR model in 2020. The Centre line is the median; box limits indicate upper and lower quartiles; and the outline displays the distribution of the data. Variables include (<b>a</b>) population density (POP), (<b>b</b>) gross domestic product (GDP), (<b>c</b>) precipitation (PRE), (<b>d</b>) temperature (TEM), (<b>e</b>) aspect (ASPECT), (<b>f</b>) slope (SLOPE), (<b>g</b>) fractional vegetation cover (FVC), (<b>h</b>) net primary productivity (NPP).</p>
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<p>Differences in WYs’ Local R<sup>2</sup> in the WRB. (<b>a</b>) The differences in the Local R<sup>2</sup> in the WRB. (<b>b</b>) The differences in the Local R<sup>2</sup> in the sub-basin.</p>
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<p>Local spatial distribution of regression coefficients of MGWR model.Variables include (<b>a</b>) population density (POP), (<b>b</b>) gross domestic product (GDP), (<b>c</b>) precipitation (PRE), (<b>d</b>) temperature (TEM), (<b>e</b>) aspect (ASPECT), (<b>f</b>) slope (SLOPE), (<b>g</b>) fractional vegetation cover (FVC), (<b>h</b>) net primary productivity (NPP).</p>
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<p>The distribution patterns of primary control variables in disparate positions in WRB. (<b>a</b>) The distribution patterns of the first major control variables; (<b>b</b>) the distribution patterns of the second main control factors.</p>
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20 pages, 6637 KiB  
Article
Retrieval of Chlorophyll-a Concentrations Using Sentinel-2 MSI Imagery in Lake Chagan Based on Assessments with Machine Learning Models
by Xuming Shi, Lingjia Gu, Tao Jiang, Xingming Zheng, Wen Dong and Zui Tao
Remote Sens. 2022, 14(19), 4924; https://doi.org/10.3390/rs14194924 - 1 Oct 2022
Cited by 17 | Viewed by 3865
Abstract
Chlorophyll-a (Chl-a) is an important characterized parameter of lakes. Monitoring it accurately through remote sensing is thus of great significance for early warnings of water eutrophication. Sentinel Multispectral Imager (MSI) images from May to September between 2020 and 2021 were used along with [...] Read more.
Chlorophyll-a (Chl-a) is an important characterized parameter of lakes. Monitoring it accurately through remote sensing is thus of great significance for early warnings of water eutrophication. Sentinel Multispectral Imager (MSI) images from May to September between 2020 and 2021 were used along with in-situ measurements to estimate Chl-a in Lake Chagan, which is located in Jilin Province, Northeast China. In this study, the extreme gradient boosting (XGBoost) and Random Forest (RF) models, which had similar performances, were generated by six single bands and six band combinations. The RF model was then selected based on the assessments (R2 = 0.79, RMSE = 2.51 μg L−1, MAPE = 9.86%), since its learning of the input features in the model conformed to the bio-optical properties of Case 2 waters. The study considered Chl-a concentrations in Lake Chagan as a seasonal pattern according to the K-Nearest-Neighbors (KNN) classification. The RF model also showed relatively stable performance for three seasons (spring, summer and autumn) and it was applied to map Chl-a in the whole lake. The research presents a more reliable machine learning (ML) model with higher precision than previous empirical models, as shown by the effects of the input features linked with the biological mechanisms of Chl-a. Its robustness was revealed by the temporal and spatial distributions of Chl-a concentrations, which were consistent with in-situ measurements in the map. This research was capable of revealing the current ecological situation in Lake Chagan and can serve as a reference in remote sensing of inland lakes. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Study area and field measurements. The left-hand part shows the geographical location and the right-hand part shows the composition of the lake and distribution of sampling points in the field.</p>
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<p>Flowchart of the proposed RF model for estimating Chl-a. The left-hand panel shows the input variables and the right-hand panel shows the evaluation and application processes.</p>
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<p>Performance of the validation results of the XGBoost and RF models for the Chl-a concentrations. (<b>a</b>) XGBoost model; (<b>b</b>) RF model. The straight line is 1:1, the horizontal axis is the measured value and the vertical axis is the retrieved value.</p>
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<p>Figure of the features of density scatter: (<b>a</b>) XGBoost; (<b>b</b>) RF. The features are ranked by importance from top to bottom on the vertical axis. On the horizontal axis, red represents a high correlation, and blue represents a low correlation. This illustrates the relationship between the input features and the output Chl-a values.</p>
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<p>Figure of the features of density scatter: (<b>a</b>) XGBoost; (<b>b</b>) RF. The features are ranked by importance from top to bottom on the vertical axis. On the horizontal axis, red represents a high correlation, and blue represents a low correlation. This illustrates the relationship between the input features and the output Chl-a values.</p>
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<p>Box plot of seasonal classification results of the validation set achieved by KNN.</p>
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<p>The RF model’s performance on validation set in different seasons: (<b>a</b>) spring, (<b>b</b>) summer and (<b>c</b>) autumn.</p>
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<p>Average Chl-a concentrations retrieved by the RF model between 2020 and 2021 for sampling points in the field.</p>
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<p>Spatial distribution of Chl-a concentrations retrieved by the RF model between 2020 and 2021 for the whole lake: (<b>a</b>) 2020 spring; (<b>b</b>) 2021 spring; (<b>c</b>) 2020 summer; (<b>d</b>) 2021 summer; (<b>e</b>) 2020 autumn; (<b>f</b>) 2021 autumn.</p>
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<p>Spatial distribution of Chl-a concentrations retrieved by the RF model between 2020 and 2021 for the whole lake: (<b>a</b>) 2020 spring; (<b>b</b>) 2021 spring; (<b>c</b>) 2020 summer; (<b>d</b>) 2021 summer; (<b>e</b>) 2020 autumn; (<b>f</b>) 2021 autumn.</p>
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<p>Relative feature importance of each input feature: (<b>a</b>) RF; (<b>b</b>) XGBoost model.</p>
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<p>SHAP summary bar plot: (<b>a</b>) RF model; (<b>b</b>) XGBoost model.</p>
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<p>Algorithms’ performances on (<b>a</b>) the training set of the NIRRI algorithm, (<b>b</b>) the validation set of the NIRRI algorithm, (<b>c</b>) the training set of the Enhanced Three algorithm and (<b>d</b>) the validation set of the Enhanced Three algorithm.</p>
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<p>Polygonal trend between the in situ hyperspectral data and the ESA L2A products.</p>
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<p>Time series of (<b>a</b>) averaged Chl-a concentrations retrieved by the RF model and (<b>b</b>) TSS concentrations of the in situ measurement points.</p>
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26 pages, 5628 KiB  
Article
Controls on Alpine Lake Dynamics, Tien Shan, Central Asia
by Qifei Zhang, Yaning Chen, Zhi Li, Gonghuan Fang, Yanyun Xiang and Yupeng Li
Remote Sens. 2022, 14(19), 4698; https://doi.org/10.3390/rs14194698 - 20 Sep 2022
Cited by 5 | Viewed by 2128
Abstract
The number and area of alpine lakes in Tien Shan (TS) are rapidly growing in response to a warming climate and retreating glaciers. This paper presents a comparative analysis of lake classification and changes by dividing alpine lakes (within a 10 km buffer [...] Read more.
The number and area of alpine lakes in Tien Shan (TS) are rapidly growing in response to a warming climate and retreating glaciers. This paper presents a comparative analysis of lake classification and changes by dividing alpine lakes (within a 10 km buffer of the glacier margins) into four types (supraglacial lakes, proglacial lakes, extraglacial lakes and non-glacial lakes), and subsequently determining the driving forces of change across the TS region from 1990 to 2015. The analysis utilized multiple satellite images and climatic data from gridded data sets and meteorological station observations. The results indicate that the total number and area of glacial lakes continuously increased during the study period, whereas non-glacial lakes intermittently expanded. Specifically, the total number and area of all glacial lakes (supraglacial lakes, proglacial lakes and extraglacial lakes) increased by 45.45% and 27.08%, respectively. Non-glacial lakes, in contrast, increased in quantity and area by 23.92% and 19.01%, respectively. Alpine lakes are closer to glaciers at high altitudes; in fact, some (e.g., proglacial lakes) are connected to glacier termini, and these show the highest expansion speed during the study period. The area of proglacial lakes expanded by 60.32%. Extraglacial lakes expanded by 21.06%. Supraglacial lakes, in marked contrast to the other types, decreased in area by 3.74%. Widespread rises in temperature and glacier wastage were the primary cause of the steady expansion of glacial lakes, particularly those linked to small- and medium-sized glaciers distributed in the Eastern TS where glacial lakes have rapidly increased. Both proglacial and extraglacial lakes expanded by 6.47%/a and 2%/a, respectively, from 1990 to 2015. While these proglacial and extraglacial lakes are located in largely glacierized areas, lakes in the Central TS exhibited the slowest expansion, increasing in area by 1.44%/a and 0.74%/a, respectively. Alterations in non-glacial lake areas were driven by changes in precipitation and varied spatially over the region. This study has substantial implications for the state of water resources under the complex regional changes in climate in the TS and can be used to develop useful water-resource management and planning strategies throughout Central Asia. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Map showing the TS study region (<b>a</b>); changes in annual temperature and precipitation (<b>b</b>,<b>c</b>); map of study area showing the spatial distribution of lakes, glaciers, rivers and meteorological stations (<b>d</b>); monthly average temperature (ERA-5) and precipitation (GPCC) (<b>e</b>); hypsometric curve of the TS region and distribution of the area by layer under each 500 m elevation band (<b>f</b>). Note: Jan = January, Mar = March, Jul = July, Sep = September, Nov = November.</p>
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<p>Flow chart showing the process used for alpine lake extraction.</p>
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<p>Diagram showing the classification of alpine lakes across the TS region (<b>a</b>); the available Landsat images used in the TS; (<b>b</b>) alpine lakes within a 10 km buffer zone of a glacier were extracted in the TS; (<b>c</b>) the position of different types of alpine lakes relative to the glaciers; (<b>d</b>–<b>h</b>) examples of supraglacial, proglacial, extraglacial and non-glacial lakes in the TS. Note: the bule framework means the different types of alpine lakes.</p>
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<p>Distribution of the four alpine lake types of different sizes in the TS in 2015.</p>
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<p>Yearly changing rates of the different alpine lake types in terms of number (<b>a</b>) and lake area (<b>b</b>) in the TS from 1990 to 2015.</p>
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<p>Variations in the number and area of the four types of alpine lakes in the TS between 1990 and 2015.</p>
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<p>Changes in glacial lakes in the TS from 1990 to 2015. (<b>a</b>,<b>c</b>,<b>e</b>) Newly formed lakes between 1990–2000, 2000–2010, and 2010–2015; (<b>b</b>,<b>d</b>,<b>f</b>) Extinct (lost) lakes between the periods of 1990–2000, 2000–2010, and 2010–2015.</p>
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<p>Changes in glacier number and area across the Eastern Tien Shan. (<b>a</b>,<b>d</b>) Glacier number; (<b>b</b>,<b>e</b>) glacier area; (<b>c</b>,<b>f</b>) change rates in glacier area for glaciers of different sizes.</p>
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<p>Mean annual and cumulative glacier mass balance for Tuyuksuyskiy glacier and Urumqi glacier No. 1 in the TS from 1980 to 2015. (<b>a</b>) Ts. Tuyuksuyskiy glacier; (<b>b</b>) Urumqi glacier No. 1.</p>
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<p>Geographical information in the TS region (<b>a</b>); spatial distribution of glaciers and glacial lakes (<b>b</b>,<b>c</b>); the proportion of glaciers and glacial lakes (<b>d</b>,<b>e</b>); spatial variations in annual TWS (<b>f</b>); variations in monthly TWS (<b>g</b>); variations in annual TWS (<b>h</b>).</p>
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<p>Variations in annual temperature and precipitation in the TS from 1990 to 2015. (<b>a</b>) Variations in temperature from the meteorological stations; (<b>b</b>) variations in temperature from the ERA5 data; (<b>c</b>) variations in precipitation from the meteorological stations; (<b>d</b>) variations in precipitation from the GPCC data.</p>
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21 pages, 9375 KiB  
Article
Assessment of Satellite-Based Precipitation Products for Estimating and Mapping Rainfall Erosivity in a Subtropical Basin, China
by Xianghu Li, Xuchun Ye and Chengyu Xu
Remote Sens. 2022, 14(17), 4292; https://doi.org/10.3390/rs14174292 - 31 Aug 2022
Cited by 3 | Viewed by 1862
Abstract
Rainfall erosivity is an important indicator for quantitatively representing the erosive power of rainfall. This study expanded three satellite-based precipitation products (SPPs) for estimating and mapping rainfall erosivity in a subtropical basin in China and evaluated their performance at different rainfall erosivity intensities, [...] Read more.
Rainfall erosivity is an important indicator for quantitatively representing the erosive power of rainfall. This study expanded three satellite-based precipitation products (SPPs) for estimating and mapping rainfall erosivity in a subtropical basin in China and evaluated their performance at different rainfall erosivity intensities, seasons, and spaces. The results showed that the rainfall erosivity data from GPM-IMERG had the smallest errors compared to the estimates from rain gauge data on monthly and seasonal scales, while data from PERSIANN-CDR and TRMM 3B42 significantly underestimated and slightly overestimated rainfall erosivity, respectively. The three SPPs generally presented different strengths and weaknesses in different seasons. TRMM 3B42 performed best in summer, with small biases, but its performance was less satisfactory in winter. The precision of estimates from GPM-IMERG was higher than that from TRMM 3B42; the biases, especially in winter, were significantly reduced. For different intensities, PERSIANN-CDR overestimated light rainfall erosivity but underestimated heavy rainfall erosivity. In terms of space, TRMM 3B42 and GPM-IMERG correctly presented the spatial pattern of rainfall erosivity. However, PERSIANN-CDR tended to be less skillful in describing its spatial maps. Outcomes of the study provide an insight into the suitability of the SPPs for estimating and mapping rainfall erosivity and suggest possible directions for further improving these products. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Location of the Poyang Lake Basin and distribution of the rain gauges.</p>
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<p>Monthly variation of the R, ME, RMSE, and BIAS ((<b>a</b>,<b>c</b>,<b>e</b>,<b>g</b>) for monthly rainfall erosivity; (<b>b</b>,<b>d</b>,<b>f</b>,<b>h</b>) for monthly erosivity density).</p>
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<p>Seasonal variation of R, ME, RMSE, and BIAS ((<b>a</b>,<b>c</b>,<b>e</b>,<b>g</b>) for rainfall erosivity; (<b>b</b>,<b>d</b>,<b>f</b>,<b>h</b>) for erosivity density).</p>
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<p>Distribution of frequencies and corresponding contribution rates of rainfall erosivity in different intensity categories ((<b>a</b>): monthly scale; (<b>b</b>): seasonal scale).</p>
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<p>Distribution of the Mean (<b>a</b>), ME (<b>b</b>), RMSE (<b>c</b>), and BIAS (<b>d</b>) of rainfall erosivity in different intensity categories on the monthly scale.</p>
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<p>Distribution of the Mean (<b>a</b>), ME (<b>b</b>), RMSE (<b>c</b>), and BIAS (<b>d</b>) of rainfall erosivity in different intensity categories on seasonal scale.</p>
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<p>Changes in FBI (<b>a</b>), FAR (<b>b</b>), POD (<b>c</b>), and ETS (<b>d</b>) scores at different thresholds on the monthly scale.</p>
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<p>Changes in FBI (<b>a</b>), FAR (<b>b</b>), POD (<b>c</b>), and ETS (<b>d</b>) scores at different thresholds on the seasonal scale.</p>
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<p>Comparison of the spatial patterns of average annual rainfall erosivity.</p>
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<p>Spatial correlation between estimates from the three SPPs and that from the rain gauge data (<b>left</b> for rainfall erosivity; <b>right</b> for erosivity density).</p>
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<p>Comparison of spatial patterns of average annual erosivity density.</p>
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18 pages, 3279 KiB  
Article
Community Scale Assessment of the Effectiveness of Designed Discharge Routes from Building Roofs for Stormwater Reduction
by Xiaoran Fu, Dong Wang, Qinghua Luan, Jiahong Liu, Zhonggen Wang and Jiayu Tian
Remote Sens. 2022, 14(13), 2970; https://doi.org/10.3390/rs14132970 - 21 Jun 2022
Cited by 6 | Viewed by 1899
Abstract
Urban flooding is increasing due to climate change and the expansion of impervious land surfaces. Green roofs have recently been identified as effective solutions for mitigating urban stormwater. However, discharge routes that involve receiving catchments of stormwater runoff from roofs to mitigate high [...] Read more.
Urban flooding is increasing due to climate change and the expansion of impervious land surfaces. Green roofs have recently been identified as effective solutions for mitigating urban stormwater. However, discharge routes that involve receiving catchments of stormwater runoff from roofs to mitigate high flows have been limited. Thus, a hydrological model was constructed to investigate the effects of changing discharge routes on stormwater flow. Three hypothetical scenarios were assessed using various combinations of discharge routes and roof types. The reduction effects on outflow and overflow were identified and evaluated across six return periods of designed rainstorms in the Tai Hung Tulip House community in Beijing. The results showed that green roofs, together with the discharge routes connecting to pervious catchments, were effective in reducing peak flow (13.9–17.3%), outflow volume (16.3–27.3%), drainage overflow frequency, and flood duration. Although mitigation can be improved by considering discharge routes, it is limited compared to that achieved by the effects of green roofs. However, integrating green roofs and discharge routes can improve community resilience to rainstorms with longer return periods. These results provide useful information for effective design of future stormwater mitigation and management strategies in small-scale urban areas. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Study area position and Tai Hung Tulip House (THTH) community catchment as used in the model. (<b>a</b>) Location of Beijing Economic-Technological Development Area; (<b>b</b>) digital elevation model of THTH community; (<b>c</b>) land use and drainage networks of THTH community.</p>
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<p>Simulated (green lines) and observed (red circles) hydrographs at drainage node J20 for two rainfall events (blue bars) during the monitoring periods: (<b>a</b>) 20 July 2019 rainfall event and (<b>b</b>) 7 September 2016 rainfall event.</p>
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<p>Flow hydrographs at outfalls (O1 and O2) for the various scenarios (S1, S2, S3, and S4) and rainfall events with return periods of: (<b>a</b>,<b>g</b>) 5; (<b>b</b>,<b>h</b>) 10; (<b>c</b>,<b>i</b>) 20; (<b>d</b>,<b>j</b>) 30; (<b>e</b>,<b>k</b>) 50; and (<b>f</b>,<b>l</b>) 100 years.</p>
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<p>Frequency distribution of overflow volume of junction nodes for the various scenarios (S1, S2, S3, and S4) and rainfall events with return period of (<b>a1</b>–<b>a4</b>) 5, (<b>b1</b>–<b>b4</b>) 10, (<b>c1</b>–<b>c4</b>) 20, (<b>d1</b>–<b>d4</b>) 30, (<b>e1</b>–<b>e4</b>) 50, and (<b>f1</b>–<b>f4</b>) 100 years.</p>
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<p>Frequency distribution of overflow cumulative duration of junction nodes for the various scenarios (S1, S2, S3 and S4) and rainfall events with return period of (<b>a1</b>–<b>a4</b>) 5, (<b>b1</b>–<b>b4</b>) 10, (<b>c1</b>–<b>c4</b>) 20, (<b>d1</b>–<b>d4</b>) 30, (<b>e1</b>–<b>e4</b>) 50, and (<b>f1</b>–<b>f4</b>) 100 years.</p>
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<p>Reduction rate of the (<b>a</b>) peak flow at outfalls (O1 and O2), (<b>b</b>) total outfall flow at outfalls (O1 and O2), (<b>c</b>) overflow volume of junction nodes, (<b>d</b>) overflow cumulative duration of junction nodes for the discharge route scenarios (S2, S3, and S4) compared to the current status quo (S1) during rainstorms with 5–100–year return periods.</p>
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16 pages, 4888 KiB  
Article
Ecological Impacts of Land Use Change in the Arid Tarim River Basin of China
by Yifeng Hou, Yaning Chen, Jianli Ding, Zhi Li, Yupeng Li and Fan Sun
Remote Sens. 2022, 14(8), 1894; https://doi.org/10.3390/rs14081894 - 14 Apr 2022
Cited by 36 | Viewed by 4157
Abstract
Land use/cover change has become an indispensable part of global eco-environmental change research. The Tarim River Basin is the largest inland river basin in China. It is also one of the most ecologically fragile areas in the country, with greening and desertification processes [...] Read more.
Land use/cover change has become an indispensable part of global eco-environmental change research. The Tarim River Basin is the largest inland river basin in China. It is also one of the most ecologically fragile areas in the country, with greening and desertification processes coexisting. This paper analyzes the evolution of land-use/cover change in the Tarim River Basin over the past 30 years based on remote sensing data. The research also explores the contribution of conversion between different land types to the ecological environment by selecting methods, such as transfer matrix and ecological contribution rate. Results indicate that grassland and barren land are the main land types in the region, accounting for 72.46% and 18.87% of the basin area, respectively. From 1990 to 2019, cropland area increased from 33,585.89 km2 to 52,436.40 km2, an increase of 56.13%, while barren land areas decreased from 781,380.57 km2 to 760,783.29 km2. Most of the land-use conversion was grassland to other land types and other land types to barren land. Since 1990, the conversion of barren land to grassland and cropland in the basin has led to ecological improvement, whereas the conversion of grassland to cropland has caused deterioration, but with a generally improving trend. It is anticipated that, over the next decade, changes in land types will involve increases in grassland and woodland area, decreases in barren land and cropland, and an overall improvement in the ecological environment in the watershed. Since agriculture and animal husbandry are the main industries in the Tarim River Basin and the land-use structure is dominated by cropland and grassland, several key measures should be implemented. These include improving land use, rationalizing the use of water and soil resources, slowing down the expansion of cropland, and alleviating the contradiction between humans and land, with the ultimate aim of achieving sustainable development of the social economy and ecological environment. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Sketch map of the Tarim River Basin, China. The map is from the Chinese Standard Map (<a href="http://bzdt.ch.mnr.gov.cn/GS" target="_blank">http://bzdt.ch.mnr.gov.cn/GS</a> (accessed on 11 April 2022) (2019)1822).</p>
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<p>Land use simulation process.</p>
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<p>Land uses in the Tarim River Basin from 1990 to 2019: (<b>a</b>) 1990; (<b>b</b>) 2000; (<b>c</b>) 2010; and (<b>d</b>) 2019.</p>
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<p>Land-use type changes in the Tarim River Basin.</p>
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<p>Land-use transfer map of the Tarim River Basin from 1990 to 2019: (<b>a</b>) 1990–2000; (<b>b</b>) 2000–201; (<b>c</b>) 2010–2019; and (<b>d</b>) 1990–2019.</p>
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<p>Changes in ecological environment in the Tarim River Basin from 1990 to 2019: (<b>a</b>) 1990–2000; (<b>b</b>) 2000–2010; (<b>c</b>) 2010–2019; and (<b>d</b>) 1990–2019.</p>
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<p>Ecological contribution of the Tarim River Basin (1990–2019). (<b>A</b>) Contribution rate of land conversion among different land types to ecological environment: (<b>a</b>) 1990–2000; (<b>b</b>) 2000–2010; (<b>c</b>) 2010–2019; and (<b>d</b>) 1990–2019 (1. cropland; 2. grassland; 3. woodland; 4. built-up land; 5. water bodies; and 6. barren land). (<b>B</b>) Eco-environment quality index of the Tarim River Basin (1990–2019).</p>
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<p>Future land changes in the Tarim River Basin: (<b>a</b>) 2019; (<b>b</b>): actual and simulated land-use change results of the CA-Markov Model for 2030; (<b>c</b>) 2019–2030; (<b>d</b>): future land-use type transfer for 1990–2030.</p>
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<p>Future ecological changes in the Tarim River Basin: (<b>a</b>) 2019–2030; (<b>b</b>) 1990–2030; (<b>c</b>,<b>d</b>) future ecological contribution of the Tarim River Basin (1. cropland; 2. grassland; 3. woodland; 4. built-up land; 5. water bodies; and 6. barren land).</p>
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19 pages, 9123 KiB  
Article
Impact of Elevation-Dependent Warming on Runoff Changes in the Headwater Region of Urumqi River Basin
by Zhouyao Zheng, Sheng Hong, Haijun Deng, Zhongqin Li, Shuang Jin, Xingwei Chen, Lu Gao, Ying Chen, Meibing Liu and Pingping Luo
Remote Sens. 2022, 14(8), 1780; https://doi.org/10.3390/rs14081780 - 7 Apr 2022
Cited by 8 | Viewed by 2292
Abstract
Warming in mountainous areas has obvious elevation dependence (warming rate increases with elevation), which deeply impacts runoff change in mountainous areas. This study analysed the influence of elevation-dependent warming on runoff in the headwater region of the Urumqi River Basin (URB) based on [...] Read more.
Warming in mountainous areas has obvious elevation dependence (warming rate increases with elevation), which deeply impacts runoff change in mountainous areas. This study analysed the influence of elevation-dependent warming on runoff in the headwater region of the Urumqi River Basin (URB) based on meteorological data, remote sensing images, and runoff data. Results indicated a significant warming rate in the URB from 1960 to 2019 (0.362 °C/decade; p < 0.01). The temperature increased with an obvious elevation-dependent warming in the URB, especially during winter. Glaciers sharply retreated in the headwater region of the URB under regional warming, and remote-based results showed that glacier areas decreased by 29.45 km2 (−57.81%) from the 1960s to 2017. The response of glacier mass balance and meltwater runoff to temperature change has a lag of 3 years in the headwater region of the URB. The elevation-dependent warming of temperature changes significantly impacted glacial meltwater runoff in the URB (R2 = 0.49). Rising temperatures altered the glacial meltwater runoff, and the maximum annual runoff of the Urumqi Glacier No. 1 meltwater runoff increased 78.6% in 1990–2017 compared to 1960–1990. During the period of 1960–1996, the total glacial meltwater runoff amounted to 26.9 × 108 m3, accounting for 33.4% of the total runoff during this period, whereas the total glacial meltwater runoff accounted for 51.1% of the total runoff in 1996–2006. Therefore, these results provide a useful reference for exploring runoff changes in mountainous watersheds in the context of elevation-dependent warming. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>The Urumqi River Basin. ①, ②, and ③ are the Houxia hydrological station, Daxigou meteorology station, and Glacier No. 1 hydrological station, respectively. Lines A, B, and C show the topography and temperature profiles in Figure 5. The glaciers boundary shape format data are from the second glacier inventory data, and DEM elevation data are from the SRTM (<a href="https://earthexplorer.usgs.gov/" target="_blank">https://earthexplorer.usgs.gov/</a>, accessed on 4 April 2022).</p>
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<p>Scatter plot of the monthly mean temperature of meteorological station observations from the Daxigou station compared to the monthly mean temperature at the corresponding grid point, with the black dashed line indicating that the temperature is equal to 0 °C.</p>
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<p>Average annual temperature in the headwater region of the Urumqi River Basin.</p>
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<p>Elevation change of warming in the headwater region of the URB from 1960 to 2017; (<b>a</b>) annual average, (<b>b</b>) spring, (<b>c</b>) summer, (<b>d</b>) autumn, (<b>e</b>) winter.</p>
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<p>Comparison of topographic profiles and mean annual warming rate profiles: (<b>a1</b>) Line A topographic profile, (<b>a2</b>) Line B topographic profile, (<b>a3</b>) Line C topographic profile, (<b>b1</b>) Line A mean annual warming rate profile, (<b>b2</b>) Line B mean annual warming rate profile, (<b>b3</b>) Line C mean annual warming rate profile.</p>
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<p>Glacier area changes in the URB during different periods. From (<b>a</b>–<b>e</b>) is glacier boundary in 1960s, 1991, 2001, 2011, and 2017, respectively; (<b>f</b>) shows the glacier changes in the URB in different periods. The background images in (<b>b</b>–<b>e</b>) are corresponding Landsat images.</p>
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<p>Glacier changes at different elevation zones in the headwater region of the URB.</p>
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<p>Glacier changes at different elevation zones: (<b>a</b>) area of glacier change at different elevations, (<b>b</b>) rate of glacier change at different elevations, (<b>c</b>) rate of warming at different elevations, and (<b>d</b>) scatter plot of warming rate vs. rate of glacier change at corresponding elevations.</p>
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<p>Changes in mass balance of Urumqi Glacier No. 1.</p>
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<p>Observed runoff from Glacier No. 1 hydrological station at URB; (<b>a</b>) annual runoff, (<b>b</b>) cumulative anomaly of annual runoff, (<b>c</b>) annual runoff probability density from1960 to1989, (<b>d</b>) annual runoff probability density from 1990 to 2017.</p>
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<p>Runoff changes at the Hero Bridge hydrological station of the headwater region of the URB: (<b>a</b>) annual runoff, (<b>b</b>) cumulative anomaly of annual runoff, with the anomaly base period of 1960–1989.</p>
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17 pages, 5963 KiB  
Article
Assessing the Sensitivity of Vegetation Cover to Climate Change in the Yarlung Zangbo River Basin Using Machine Learning Algorithms
by Lizhuang Cui, Bo Pang, Gang Zhao, Chunguang Ban, Meifang Ren, Dingzhi Peng, Depeng Zuo and Zhongfan Zhu
Remote Sens. 2022, 14(7), 1556; https://doi.org/10.3390/rs14071556 - 23 Mar 2022
Cited by 11 | Viewed by 2725
Abstract
Vegetation is a key indicator of the health of most terrestrial ecosystems and different types of vegetation exhibit different sensitivity to climate change. The Yarlung Zangbo River Basin (YZRB) is one of the highest basins in the world and has a wide variety [...] Read more.
Vegetation is a key indicator of the health of most terrestrial ecosystems and different types of vegetation exhibit different sensitivity to climate change. The Yarlung Zangbo River Basin (YZRB) is one of the highest basins in the world and has a wide variety of vegetation types because of its complex topographic and climatic conditions. In this paper, the sensitivity to climate change for different vegetation types, as reflected by the Normalized Difference Vegetation Index (NDVI), was assessed in the YZRB. Three machine learning models, including multiple linear regression, support vector machine, and random forest, were adopted to simulate the response of each vegetation type to climatic variables. We selected random forest, which showed the highest performance in both the calibration and validation periods, to assess the sensitivity of the NDVI to temperature and precipitation changes on an annual and monthly scale using hypothetical climatic scenarios. The results indicated there were positive responses of the NDVI to temperature and precipitation changes, and the NDVI was more sensitive to temperature than to precipitation on an annual scale. The NDVI was predicted to increase by 1.60%–4.68% when the temperature increased by 1.5 °C, while it only changed by 0.06%–0.24% when the precipitation increased by 10% in the YZRB. Monthly, the vegetation was more sensitive to temperature changes in spring and summer. Spatially, the vegetation was more sensitive to temperature increases in the upper and middle reaches, where the existing temperatures were cooler. The time-lag effects of climate were also analyzed in detail. For both temperature and precipitation, Needleleaf Forest and Broadleaf Forest had longer time lags than those of other vegetation types. These findings are useful for understanding the eco-hydrological processes of the Tibetan Plateau. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>The topography, vegetation types, and sub-catchments of the Yarlung Zangbo River Basin (YZRB) ((<b>a</b>) Topography, (<b>b</b>) Vegetation types, (<b>c</b>) Sub-catchments).</p>
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<p>Basin-averaged inter-annual variations in the Normalized Difference Vegetation Index (NDVI) and climatic variables as well as the slope of the NDVI for each vegetation type in the YZRB ((<b>a</b>) Annual total precipitatin, (<b>b</b>) Annual average temperature, (<b>c</b>) NDVI, (<b>d</b>) Slope of NDVI) (NF: Needleleaf Forest, BF: Broadleaf Forest, Sc: Scrub, St: Steppe, M: Meadow, AV: Alpine Vegetation, CV: Cultivated Vegetation).</p>
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<p>Basin-averaged inter-annual variations of climatic variables and the NDVI as well as their slope in the YZRB ((<b>a</b>) Temperature, (<b>b</b>) Precipitation, (<b>c</b>) NDVI, (<b>d</b>) Slope of temperature, (<b>e</b>) Slope of precipitation, (<b>f</b>) Slope of NDVI).</p>
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<p>The observed and predicted NDVI series in the validation period from the random forest for different vegetation types.</p>
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<p>The response to temperature and precipitation for different vegetation types on an annual scale ((<b>a</b>) The response of NDVI to temperature, (<b>b</b>) The response of NDVI to Precipitation).</p>
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<p>The distribution of the response to temperature and precipitation changes on an annual scale in the YZRB ((<b>a</b>) 1.5 °C increase in temperature, (<b>b</b>) 10% increase in precipitation, (<b>c</b>) 10% decrease in precipitation).</p>
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<p>The response to temperature and precipitation for different vegetation types on a monthly scale ((<b>a</b>) 1.5 °C increase in temperature, (<b>b</b>) 10% increase in precipitation, (<b>c</b>) 10% decrease in precipitation).</p>
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<p>The distribution of the responses to a temperature increase (1.5 °C) on a monthly scale in the YZRB ((<b>a</b>) Spring, (<b>b</b>) Summer, (<b>c</b>) Autumn, (<b>d</b>) Winter).</p>
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<p>The correlations between the NDVI and climatic variables at time lags of 0–3 months for different vegetation types ((<b>a</b>) Rank of correlation coefficients, (<b>b</b>) Rank of importance).</p>
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19 pages, 125621 KiB  
Article
TRDet: Two-Stage Rotated Detection of Rural Buildings in Remote Sensing Images
by Baochai Peng, Dong Ren, Cheng Zheng and Anxiang Lu
Remote Sens. 2022, 14(3), 522; https://doi.org/10.3390/rs14030522 - 22 Jan 2022
Cited by 7 | Viewed by 3186
Abstract
Fast and accurate acquisition of the outline of rural buildings on remote sensing images is an efficient method to monitor illegal rural buildings. The traditional object detection method produces useless background information when detecting rural buildings; the semantic segmentation method cannot accurately segment [...] Read more.
Fast and accurate acquisition of the outline of rural buildings on remote sensing images is an efficient method to monitor illegal rural buildings. The traditional object detection method produces useless background information when detecting rural buildings; the semantic segmentation method cannot accurately segment the contours between buildings; the instance segmentation method cannot obtain regular building contours. The rotated object detection methods can effectively solve the problem that the traditional artificial intelligence method cannot accurately extract the outline of buildings. However, the rotated object detection methods are easy to lose location information of small objects in advanced feature maps and are sensitive to noise. To resolve these problems, this paper proposes a two-stage rotated object detection network for rural buildings (TRDet) by using a deep feature fusion network (DFF-Net) and a pixel attention module (PAM). Specifically, TRDet first fuses low-level location and high-level semantic information through the DFF-Net and then reduces the interference of noise information to the network through the PAM. The experimental results show that the mean average precession (mAP), precision, recall rate, and F1 score of the proposed TRDet are 83.57%, 91.11%, 86.5%, and 88.74%, respectively, which outperform the R2CNN model by 15%, 15.54%, 4.01%, and 9.87%. The results demonstrate that the TRDet can achieve better detection in small rural buildings and dense rural buildings. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Objects’ size scatter of the dataset: red triangle represents the pixel size in the most concentrated rural buildings: (<b>a</b>) Training set; (<b>b</b>) Validation set.</p>
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<p>Different rural building targets in the dataset: (<b>a</b>) mountain dense rural buildings; (<b>b</b>) suburb dense rural buildings; (<b>c</b>) sparse rural buildings; (<b>d</b>) small rural buildings; (<b>e</b>) large rural buildings.</p>
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<p>Different rural building targets in the dataset: (<b>a</b>) mountain dense rural buildings; (<b>b</b>) suburb dense rural buildings; (<b>c</b>) sparse rural buildings; (<b>d</b>) small rural buildings; (<b>e</b>) large rural buildings.</p>
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<p>TRDet network architecture: TRDet consists of two phases: feature extraction and rotation branch. In the feature extraction phase, multiple levels’ abundant features are extracted and integrated by DFF-Net and PAM. Then, RPN generates a series of horizontal anchors, the ROI Align to align features, and the GAP to replace the fully connected layer. By Combining the above predictions, R-NMS produces the final detection results.</p>
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<p>Structure of the backbone network.</p>
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<p>DFF-Net: firstly, C<sub>3</sub> is expanded the number of channels in the feature map by DFM, and then the deep feature fusion is carried out with C<sub>4</sub>.</p>
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<p>PAM: the sensitive position score map obtained by F<sub>3</sub> strengthens the building characteristics.</p>
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<p>Calculation of <math display="inline"><semantics> <mrow> <msub> <mi>S</mi> <mrow> <mi>A</mi> <mo>∩</mo> <mi>B</mi> </mrow> </msub> </mrow> </semantics></math>: (<b>a</b>) the intersection area of two rotated boxes A and B; (<b>b</b>) calculation convex hull (P1, ... , Pn); (<b>c</b>) division of the convex hull.</p>
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<p>Different convergence processes of loss value during the training stage.</p>
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<p>Example of TRDet model detection results: (<b>a</b>) image for the rural building in Zigui; (<b>b</b>) image for the rural building in Dianjun.</p>
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<p>Comparison of detection of R2CNN and TRDet: R2CNN ignores many hard samples and identifies incorrect fields as buildings. (<b>a</b>) Are the ground truth bounding boxes of buildings; (<b>b</b>) are the R2CNN detection results; (<b>c</b>) are TRDet detection results.</p>
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<p>Comparison of detection of R3Det, SCRDet, and TRDet: TRDet has better performance in detecting dense buildings. (<b>a</b>) Represents the ground truth; (<b>b</b>) represents the R3Det detection results; (<b>c</b>) denotes SCRDet detection results; (<b>d</b>) denotes TRDet detection results.</p>
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<p>Comparison of detection of R3Det, SCRDet, and TRDet: TRDet has better performance in detecting dense buildings. (<b>a</b>) Represents the ground truth; (<b>b</b>) represents the R3Det detection results; (<b>c</b>) denotes SCRDet detection results; (<b>d</b>) denotes TRDet detection results.</p>
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<p>Comparison of detection of R2CNN, SCRDet, and TRDet: TRDet has better performance in the horizontal detection task. (<b>a</b>) the ground truth; (<b>b</b>) the R2CNN detection results; (<b>c</b>) SCRDet detection results; (<b>d</b>) TRDet detection results.</p>
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<p>Comparison of detection of R2CNN, SCRDet, and TRDet: TRDet has better performance in the horizontal detection task. (<b>a</b>) the ground truth; (<b>b</b>) the R2CNN detection results; (<b>c</b>) SCRDet detection results; (<b>d</b>) TRDet detection results.</p>
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18 pages, 6250 KiB  
Article
Quantifying the Contributions of Climate Change and Human Activities to Water Volume in Lake Qinghai, China
by Guoqing Yang, Miao Zhang, Zhenghui Xie, Jiyuan Li, Mingguo Ma, Peiyu Lai and Junbang Wang
Remote Sens. 2022, 14(1), 99; https://doi.org/10.3390/rs14010099 - 26 Dec 2021
Cited by 14 | Viewed by 4437
Abstract
Lake Qinghai has shrunk and then expanded over the past few decades. Quantifying the contributions of climate change and human activities to lake variation is important for water resource management and adaptation to climate change. In this study, we calculated the water volume [...] Read more.
Lake Qinghai has shrunk and then expanded over the past few decades. Quantifying the contributions of climate change and human activities to lake variation is important for water resource management and adaptation to climate change. In this study, we calculated the water volume change of Lake Qinghai, analyzed the climate and land use changes in Lake Qinghai catchment, and distinguished the contributions of climate change and local human activities to water volume change. The results showed that lake water volume decreased by 9.48 km3 from 1975 to 2004 and increased by 15.18 km3 from 2005 to 2020. The climate in Lake Qinghai catchment is becoming warmer and more pluvial, and the changes in land use have been minimal. Based on the Soil and Water Assessment Tool (SWAT), land use change, climate change and interaction effect of them contributed to 7.46%, 93.13% and −0.59%, respectively, on the variation in surface runoff into the lake. From the perspective of the water balance, we calculated the proportion of each component flowing into and out of the lake and found that the contribution of climate change to lake water volume change was 97.55%, while the local human activities contribution was only 2.45%. Thus, climate change had the dominant impact on water volume change in Lake Qinghai. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Location of the study area in (<b>a</b>) the Lake Qinghai catchment, and the catchment in (<b>b</b>) China and (<b>c</b>) Qinghai Province. The triangles in panel (<b>c</b>) show the location of meteorological stations in or around the catchment and colors indicate elevation.</p>
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<p>(<b>a</b>) Land use in the 2010s and (<b>b</b>) soil types in the study area.</p>
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<p>Relationship between the lake area and the measured lake level, (<b>a</b>) unary linear model and (<b>b</b>) quadratic polynomial model. The abscissa represents the elevation of lake level, and the ordinate represents lake area, shaded area represents the 95% confidence intervals.</p>
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<p>Change in (<b>a</b>) annual mean lake area and (<b>b</b>) annual mean lake water volume. The blue inverted triangles correspond to the lake area for the decreasing period, the red positive triangles represent the increase period, shaded area represents the 95% confidence interval. The blue bars represent lake water volume change from previous year.</p>
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<p>Climate change in Lake Qinghai catchment. (<b>a</b>) Annual precipitation change and (<b>b</b>) annual mean air temperature change. The red dotted line with number indicates the average state before and after the mutation year.</p>
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<p>Observed and simulated monthly surface runoff for the calibration and validation period at Gangcha and Buha hydrologic stations with the performance statistics of R<sup>2</sup>, NSE and PBIAS. Green shaded area represents the prediction uncertainty (95PPU).</p>
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<p>Simulated surface runoff under three different scenarios, (<b>a</b>) actual simulation, (<b>b</b>) land use change simulation and (<b>c</b>) climate change simulation. The green triangles represent the mean values, and the orange horizontal lines represent the medians.</p>
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<p>Contributions of climate change and human activities to the water volume change in Lake Qinghai. Light blue represents the impact of climate change, and pink represents the impact of human activities.</p>
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26 pages, 8403 KiB  
Article
Hybrid Models Incorporating Bivariate Statistics and Machine Learning Methods for Flash Flood Susceptibility Assessment Based on Remote Sensing Datasets
by Jun Liu, Jiyan Wang, Junnan Xiong, Weiming Cheng, Huaizhang Sun, Zhiwei Yong and Nan Wang
Remote Sens. 2021, 13(23), 4945; https://doi.org/10.3390/rs13234945 - 5 Dec 2021
Cited by 31 | Viewed by 3659
Abstract
Flash floods are considered to be one of the most destructive natural hazards, and they are difficult to accurately model and predict. In this study, three hybrid models were proposed, evaluated, and used for flood susceptibility prediction in the Dadu River Basin. These [...] Read more.
Flash floods are considered to be one of the most destructive natural hazards, and they are difficult to accurately model and predict. In this study, three hybrid models were proposed, evaluated, and used for flood susceptibility prediction in the Dadu River Basin. These three hybrid models integrate a bivariate statistical method of the fuzzy membership value (FMV) and three machine learning methods of support vector machine (SVM), classification and regression trees (CART), and convolutional neural network (CNN). Firstly, a geospatial database was prepared comprising nine flood conditioning factors, 485 flood locations, and 485 non-flood locations. Then, the database was used to train and test the three hybrid models. Subsequently, the receiver operating characteristic (ROC) curve, seed cell area index (SCAI), and classification accuracy were used to evaluate the performances of the models. The results reveal the following: (1) The ROC curve highlights the fact that the CNN-FMV hybrid model had the best fitting and prediction performance, and the area under the curve (AUC) values of the success rate and the prediction rate were 0.935 and 0.912, respectively. (2) Based on the results of the three model performance evaluation methods, all three hybrid models had better prediction capabilities than their respective single machine learning models. Compared with their single machine learning models, the AUC values of the SVM-FMV, CART-FMV, and CNN-FMV were 0.032, 0.005, and 0.055 higher; their SCAI values were 0.05, 0.03, and 0.02 lower; and their classification accuracies were 4.48%, 1.38%, and 5.86% higher, respectively. (3) Based on the results of the flood susceptibility indices, between 13.21% and 22.03% of the study area was characterized by high and very high flood susceptibilities. The three hybrid models proposed in this study, especially CNN-FMV, have a high potential for application in flood susceptibility assessment in specific areas in future studies. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>The study area of Dadu river basin: (<b>a</b>) digital elevation model (DEM), and inventory map in Dadu river basin; (<b>b</b>) the location of Dadu river basin in China; and (<b>c</b>) flooded area in the city of Ya’an. Note: panel (<b>c</b>) is cited from <a href="https://www.sohu.com/a/413756156_583574" target="_blank">https://www.sohu.com/a/413756156_583574</a> (accessed on 18 November 2021).</p>
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<p>Flash flood conditioning factors: (<b>a</b>) altitude, (<b>b</b>) slope, (<b>c</b>) slope aspect, (<b>d</b>) topographic wetness index (TWI), (<b>e</b>) maximum three-day precipitation (M3DP), (<b>f</b>) land cover, (<b>g</b>) soil texture, (<b>h</b>) normalized difference vegetation index (NDVI), and (<b>i</b>) distance to the river (DR).</p>
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<p>The processing of the methodology used in this study.</p>
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<p>Information Gain (IG) values of the flash flood conditioning factors: altitude, slope, slope aspect, topographic wetness index (TWI), maximum three-day precipitation (M3DP), land cover, soil texture, normalized difference vegetation index (NDVI), and distance to the river (DR).</p>
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<p>Frequency distribution of the flood pixels and the Fuzzy membership values (FMVs) of the factors (<b>a</b>) altitude, (<b>b</b>) maximum three-day precipitation (M3DP), (<b>c</b>) topographic wetness index (TWI), (<b>d</b>) distance to the river (DR), (<b>e</b>) slope, (<b>f</b>) land cover, (<b>g</b>) soil texture, and (<b>h</b>) slope aspect.</p>
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<p>Spatial distributions and area proportions of the FSI classes: (<b>a</b>) FSI<sub>SVM</sub>, (<b>b</b>) FSI<sub>SVM-FMV</sub>, (<b>c</b>) FSI<sub>CART</sub>, (<b>d</b>) FSI<sub>CART-FMV</sub>, (<b>e</b>) FSI<sub>CNN</sub>, and (<b>f</b>) FSI<sub>CNN-FMV</sub>.</p>
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<p>Optimal tree used for (<b>a</b>) the CART model and (<b>b</b>) the CART-FMV hybrid model.</p>
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<p>Architecture of the 1D-CNN used in this study.</p>
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<p>The ROC curves and AUC values of the six models: (<b>a</b>) Success rate curve. (<b>b</b>) Prediction-rate curve.</p>
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18 pages, 5202 KiB  
Article
Projected Meteorological Drought over Asian Drylands under Different CMIP6 Scenarios
by Hongwei Li, Zhi Li, Yaning Chen, Yongchang Liu, Yanan Hu, Fan Sun and Patient Mindje Kayumba
Remote Sens. 2021, 13(21), 4409; https://doi.org/10.3390/rs13214409 - 2 Nov 2021
Cited by 25 | Viewed by 4735
Abstract
Asia currently has the world’s largest arid and semi-arid zones, so a timely assessment of future droughts in the Asian drylands is prudent, particularly in the context of recent frequent sandstorms. This paper assesses the duration, frequency, and intensity of drought events in [...] Read more.
Asia currently has the world’s largest arid and semi-arid zones, so a timely assessment of future droughts in the Asian drylands is prudent, particularly in the context of recent frequent sandstorms. This paper assesses the duration, frequency, and intensity of drought events in the Asian drylands based on nine climate models of the Coupled Model Intercomparison Project Phase 6 (CMIP6). The results show that a high percentage of land area is experiencing significant drought intensification of 65.1%, 89.9%, and 99.8% under Shared Socioeconomic Pathways (SSP)126, SSP245, and SSP585 scenarios, respectively. Furthermore, the data indicate that future droughts will become less frequent but longer in duration and more intense, with even more severe future droughts predicted for northwest China and western parts of Uzbekistan and Kazakhstan. Drought durations of 10.8 months and 13.4 months are anticipated for the future periods of 2021–2060 and 2061–2100, respectively, compared to the duration of 6.6 months for the historical period (1960–2000). Meanwhile, drought intensity is expected to reach 1.37 and 1.66, respectively, for future events compared to 0.97 for the historical period. However, drought severity under SSP245 will be weaker than that under SSP126 due to the mitigating effect of precipitation. The results of this study can provide a basis for the development of adaptation measures in Asian dryland nations. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Spatial distribution of land cover types in Asian drylands. (Data from European Space Agency).</p>
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<p>Standardized Taylor diagram showing the model simulation capability of simulated values for nine GCMs from 1960–2014 for observational data of temperature, precipitation, and potential evapotranspiration. (The standard deviation in a Standardized Taylor diagram is the ratio of the standard deviation of the model to the standard deviation of the observations).</p>
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<p>Temporal evolution of SPEI on a 12-month scale for the drylands of Asia and three future paths, which are SSP126, SSP245, and SSP585 (Averaged for the whole region). The colored lines represent the SPEI by ensemble means of GCMs in 2015–2100 under SSPs. The shadow represents the range of multiple GCMs. The black dashed line indicates the year 2015, allowing for a better comparison between historical and future periods.</p>
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<p>Spatial distribution of estimated Sen’s slope of monthly SPEI values for (<b>a</b>) the historical period and the three future paths of (<b>b</b>) SSP126, (<b>c</b>) SSP245, and (<b>d</b>) SSP585 in the drylands of Asia. The dot in the figure indicates that the region exceeds the Mann–Kendall significance test (0.05).</p>
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<p>Spatial distribution of Asian dryland RMDD for the 2021–2060 (<b>a</b>,<b>b</b>,<b>c</b>) and 2061–2100 (<b>c</b>,<b>d</b>,<b>f</b>) cycles under SSP126 (<b>a</b>,<b>d</b>), SSP245 (<b>b</b>,<b>e</b>), and SSP585 (<b>c</b>,<b>f</b>) scenarios, relative to the 1961–2000 reference cycle. Changes in drought duration for 2021–2100 as identified by the SPEI drought index. Drought duration changes in Asian drylands for 2021–2060 and 2061–2100 under SSP126, SSP245, and SSP585 scenarios (<b>g</b>). Two regions (<b>i</b>) in northwest China and Mongolia (<b>h</b>) in the five Central Asian countries are delineated. The bar graphs and black vertical lines indicate the mean and range of multiple GCM projections.</p>
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<p>Spatial distribution of Asian dryland RADF for the cycles 2021–2060 (<b>a</b>,<b>b</b>,<b>c</b>) and 2061–2100 (<b>c</b>,<b>d</b>,<b>f</b>) under the SSP126 (<b>a</b>,<b>d</b>), SSP245 (<b>b</b>,<b>e</b>) and SSP585 (<b>c</b>,<b>f</b>) scenarios, relative to the 1961–2000 reference cycle. Changes in drought frequency as identified by the SPEI drought index for 2021–2100. Drought frequency changes (<b>g</b>) in the drylands of Asia for 2021–2060 and 2061–2100 under the SSP126, SSP245, and SSP585 scenarios. Two regions (<b>i</b>) in northwest China and Mongolia and (<b>h</b>) in the five Central Asian countries are delineated. The bar graphs and black vertical lines indicate the mean and range of multiple GCM projections.</p>
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<p>Spatial distribution of Asian dryland (RMDI) for the two cycles of 2021–2060 (<b>a</b>,<b>b</b>,<b>c</b>) and 2061–2100 (<b>c</b>,<b>d</b>,<b>f</b>) under SSP126 (<b>a</b>,<b>d</b>), SSP245 (<b>b</b>,<b>e</b>), and SSP585 (<b>c</b>,<b>f</b>) scenarios, relative to the 1961–2000 reference cycle. Changes in drought intensity as identified by the SPEI drought index for 2021–2100. Drought intensity changes (<b>g</b>) in drylands of Asia for 2021–2060 and 2061–2100 under SSP126, SSP245, and SSP585 scenarios. Two regions (<b>i</b>) in northwest China and Mongolia (<b>h</b>) in the five Central Asian countries are delineated. The bar graphs and black vertical lines indicate the mean and range of multiple GCM projections.</p>
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<p>Temporal evolution of precipitation in the drylands of Asia over the two future paths of SSP126 and SSP245. Colored lines represent the mean precipitation ensemble for GCMs 2021–2100 under SSP. Shading represents the range of multiple GCMs. Colored dashed lines indicate trend lines to better compare trend changes in precipitation.</p>
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19 pages, 15138 KiB  
Article
Risk Assessment of Urban Floods Based on a SWMM-MIKE21-Coupled Model Using GF-2 Data
by Lidong Zhao, Ting Zhang, Jun Fu, Jianzhu Li, Zhengxiong Cao and Ping Feng
Remote Sens. 2021, 13(21), 4381; https://doi.org/10.3390/rs13214381 - 30 Oct 2021
Cited by 19 | Viewed by 3495
Abstract
Global climate change and rapid urbanization have caused increases in urban floods. Urban flood risk assessment is a vital method for preventing and controlling such disasters. This paper takes the central region of Cangzhou city in Hebei Province as an example. Detailed topographical [...] Read more.
Global climate change and rapid urbanization have caused increases in urban floods. Urban flood risk assessment is a vital method for preventing and controlling such disasters. This paper takes the central region of Cangzhou city in Hebei Province as an example. Detailed topographical information, such as the buildings and roads in the study area, was extracted from GF-2 data. By coupling the two models, the SWMM and MIKE21, the spatial distribution of the inundation region, and the water depth in the study area under different return periods, were simulated in detail. The results showed that, for the different return periods, the inundation region was generally consistent. However, there was a large increase in the mean inundation depth within a 10-to-30-year return period, and the increase in the maximum inundation depth and inundation area remained steady. The comprehensive runoff coefficient in all of the scenarios exceeded 0.8, indicating that the drainage system in the study area is insufficient and has a higher flood risk. The flood risk of the study area was evaluated based on the damage curve, which was obtained from field investigations. The results demonstrate that the loss per unit area was less than CNY 250/m2 in each return period in the majority of the damaged areas. Additionally, the total loss was mainly influenced by the damaged area, but, in commercial areas, the total loss was highly sensitive to the inundation depth. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>The locations of the measured sites in the study area.</p>
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<p>(<b>a</b>) The frequency curve of the designed rainfall; (<b>b</b>) typical rainfall process and designed rainfall process under different return periods.</p>
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<p>(<b>a</b>) Buildings extracted from GF-2 data and land-use type in the study area; (<b>b</b>) modified DEM based on buildings.</p>
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<p>Generalization results of the SWMM model and the topological relationship of the pipeline.</p>
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<p>Observed and simulated water depths of the two historical rainfall events: (<b>a</b>) 16 August 2009; (<b>b</b>) 1 August 2012.</p>
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<p>Spatial distribution of the maximum inundation depth under different return periods.</p>
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<p>(<b>a</b>) Boxplots of the maximum inundation depth distribution under different return periods; (<b>b</b>) mean inundation depth and maximum inundation area under different return periods.</p>
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<p>(<b>a</b>) Spatial distribution of the maximum velocity under a 3-year return period; (<b>b</b>) spatial distribution of the inundation depth above 40 cm under a 3-year return period.</p>
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<p>(<b>a</b>) Boxplots of the maximum velocities under different return periods; (<b>b</b>) boxplots of the duration time distribution of the inundation depths above 40 cm under different return periods.</p>
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<p>Spatial distribution of the inundation loss per unit area under different return periods.</p>
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<p>(<b>a</b>) Distribution of the ratios of the damaged areas to the total damaged areas in the groups, and the total inundation loss under different return periods; (<b>b</b>) standardized regression coefficients under different return periods.</p>
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20 pages, 6283 KiB  
Article
Influences of Climate Change and Human Activities on NDVI Changes in China
by Yu Liu, Jiyang Tian, Ronghua Liu and Liuqian Ding
Remote Sens. 2021, 13(21), 4326; https://doi.org/10.3390/rs13214326 - 27 Oct 2021
Cited by 52 | Viewed by 4872
Abstract
The spatiotemporal evolution of vegetation and its influencing factors can be used to explore the relationships among vegetation, climate change, and human activities, which are of great importance for guiding scientific management of regional ecological environments. In recent years, remote sensing technology has [...] Read more.
The spatiotemporal evolution of vegetation and its influencing factors can be used to explore the relationships among vegetation, climate change, and human activities, which are of great importance for guiding scientific management of regional ecological environments. In recent years, remote sensing technology has been widely used in dynamic monitoring of vegetation. In this study, the normalized difference vegetation index (NDVI) and standardized precipitation–evapotranspiration index (SPEI) from 1998 to 2017 were used to study the spatiotemporal variation of NDVI in China. The influences of climate change and human activities on NDVI variation were investigated based on the Mann–Kendall test, correlation analysis, and other methods. The results show that the growth rate of NDVI in China was 0.003 year−1. Regions with improved and degraded vegetation accounted for 71.02% and 22.97% of the national territorial area, respectively. The SPEI decreased in 60.08% of the area and exhibited an insignificant drought trend overall. Human activities affected the vegetation cover in the directions of both destruction and restoration. As the elevation and slope increased, the correlation between NDVI and SPEI gradually increased, whereas the impact of human activities on vegetation decreased. Further studies should focus on vegetation changes in the Continental Basin, Southwest Rivers, and Liaohe River Basin. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Main environmental characteristics of China: (<b>a</b>) Mean annual normalized difference vegetation index (NDVI) in nine river basins from 1998–2017; (<b>b</b>) mean annual standardized precipitation–evapotranspiration index (SPEI) and its grid point position from 1998–2017; (<b>c</b>) elevation; (<b>d</b>) slope; and (<b>e</b>) LUCC.</p>
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<p>Variations in the (<b>a</b>) NDVI and (<b>b</b>) SPEI in China from 1997–2017.</p>
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<p>(<b>a</b>) Spatial distribution of the trend in the NDVI in China during 1998–2017; (<b>b</b>) spatial distribution of significant changes in the NDVI in China from 1998–2017; (<b>c</b>) spatial distribution of the trend in the SPEI in China during 1998–2017; and (<b>d</b>) spatial distribution of significant changes in the SPEI in China from 1998–2017.</p>
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<p>Significance analysis of changes in the (<b>a</b>) NDVI and (<b>b</b>) SPEI in China and its nine river basins from 1998–2017. YARB—Yangtze River Basin, YRB—Yellow River Basin, PRB—Pearl River Basin, SWR—Southwest Rivers, SER—Southeast Rivers, HRB—Haihe River Basin, HURB—Huaihe River Basin, SLRB—Songhua and Liaohe River Basin, CB—Continental Basin.</p>
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<p>(<b>a</b>) Spatial distribution of the correlation between the NDVI and SPEI in China from 1998–2017; and (<b>b</b>) spatial distribution of significant correlations between NDVI and SPEI in China from 1998–2017.</p>
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<p>Effects of LUCC on NDVI: (<b>a</b>) five phases of LUCC change (in 2000, 2005, 2010, 2015, and 2020) and (<b>b</b>) trend of NDVI change corresponding to different LUCC types (in 2000, 2005, 2010, and 2015).</p>
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<p>Correlations between different NDVI levels and SPEI under different vegetation types: (<b>a</b>) cropland; (<b>b</b>) forest; (<b>c</b>) grassland; (<b>d</b>) water; (<b>e</b>) urban land; and (<b>f</b>) unused land.</p>
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<p>(<b>a</b>) Relationship between NDVI and elevation in China (1–31 represent elevation zones of −200–0 m, 0–200 m, 200–400 m, …, 5800–6000 m, respectively; 32 indicates that the elevation is &gt; 6000 m); and (<b>b</b>) relationship between NDVI and slope in China (1–35 represent the slope zones 0°–1°, 1°–2°, 2°–3°, …, 34°–35°, respectively; 36 denotes a slope &gt; 35°).</p>
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<p>Correlation between NDVI and SPEI at different elevations and slopes: (<b>a</b>) elevation (1 indicates that the elevation is &lt;200 m; 2–40 represent the elevation zones of 200–400 m, 400–600 m, 600–800 m, …, 8000–8200 m, respectively; 41 denotes elevation of &gt;8200 m); (<b>b</b>) slope (1–45 represent slope zones of 0°–1°, 1°–2°, 2°–3°, …, 44°–45°, respectively; 46 denotes a slope &gt; 45°).</p>
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<p>Climatic regionalization of China.</p>
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16 pages, 10589 KiB  
Article
Evaluation and Projection of Wind Speed in the Arid Region of Northwest China Based on CMIP6
by Yunxia Long, Changchun Xu, Fang Liu, Yongchang Liu and Gang Yin
Remote Sens. 2021, 13(20), 4076; https://doi.org/10.3390/rs13204076 - 12 Oct 2021
Cited by 13 | Viewed by 2635
Abstract
Near surface wind speed has significant impacts on ecological environment change and climate change. Based on the CN05.1 observation data (a gridded monthly dataset with the resolution of 0.25 latitude by 0.25 longitude over China), this study evaluated the ability of 25 Global [...] Read more.
Near surface wind speed has significant impacts on ecological environment change and climate change. Based on the CN05.1 observation data (a gridded monthly dataset with the resolution of 0.25 latitude by 0.25 longitude over China), this study evaluated the ability of 25 Global Climate Models (GCMs) from Coupled Model Intercomparison Project phase 6 (CMIP6) in simulating the wind speed in the Arid Region of Northwest China (ARNC) during 1971–2014. Then, the temporal and spatial variations in the surface wind speed of ARNC in the 21st century were projected under four Shared Socioeconomic Pathways (SSPs), SSP1-2.6, SSP2-4.5, SSP3-7.0, and SP5-8.5. The results reveal that the preferred-model ensemble (PME) can fairly evaluate the temporal and spatial distribution of surface wind speed with the temporal and spatial correlation coefficients exceeding 0.5 at the significance level of p = 0.05 when compared to the 25 single models and their ensemble mean. After deviation correction, the PME can reproduce the distribution characteristics of high wind speed in the east and low in the west, high in mountainous areas, and low in basins. Unfortunately, no models or model ensemble can accurately reproduce the decreasing magnitude of observed wind speed. In the 21st century, the surface wind speed in the ARNC is projected to increase under SSP1-2.6 scenario but will decrease remarkably under the other three scenarios. Moreover, the higher the emission scenarios, the more significant the surface wind speed decreases. Spatially, the wind speed will increase significantly in the west and southeast of Xinjiang, decrease in the north of Xinjiang and the south of Tarim Basin. What’s more, under the four scenarios, the surface wind speed will decrease in spring, summer and autumn, especially in summer, and increase in winter. The wind speed will decrease significantly in the north of Tianshan Mountains in summer, decrease significantly in the north of Xinjiang and the southern edge of Tarim Basin in spring and autumn, and increase in fluctuation with high values in Tianshan Mountains in winter. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Variations (<b>a</b>) and trends (<b>b</b>) of observed (black solid line) and simulated (color dot line, red and green solid line) surface wind speed in the ARNC from 1971 to 2014.</p>
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<p>Taylor chart of CMIP6 models in simulating wind speed in the ARNC during 1971–2014.</p>
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<p>Comparison between revised/unrevised PME and observation in time and space. (<b>a</b>) annual mean surface wind speed (<b>b</b>) monthly mean surface wind speed (<b>c</b>) observed wind speed (<b>d</b>) simulated wind speed by the unrevised PME (<b>e</b>) simulated wind speed by the revised PME.</p>
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<p>Variations in projected annual wind speed in the ARNC from 1995 to 2100 under different emission scenarios. The black bar chart shows the variation trend of surface wind speed in NF, MF, FF and FP.</p>
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<p>Spatial difference distribution of NF (row 1), MF (row 2), FF (row 3), and FP (row 4) relative to BP (1995–2014) under four emission scenarios.</p>
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<p>Variations in the seasonal wind speed in the ARNC from 1995 to 2100 under four emission scenarios. The black bar chart shows the variation trend of surface wind speed in NF, MF, FF and FP.</p>
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<p>Spatial difference distribution of seasonal mean wind speed relative to BP in NF (row 1), MF (row 2), FF (row 3), and FP (row 4) under four emission scenarios.</p>
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<p>Spatial difference distribution of seasonal mean wind speed relative to BP in NF (row 1), MF (row 2), FF (row 3), and FP (row 4) under four emission scenarios.</p>
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21 pages, 5789 KiB  
Article
Dynamic Assessment of the Impact of Flood Disaster on Economy and Population under Extreme Rainstorm Events
by Xin Su, Weiwei Shao, Jiahong Liu, Yunzhong Jiang and Kaibo Wang
Remote Sens. 2021, 13(19), 3924; https://doi.org/10.3390/rs13193924 - 30 Sep 2021
Cited by 26 | Viewed by 3838
Abstract
In the context of climate change and rapid urbanization, flood disaster loss caused by extreme rainstorm events is becoming more and more serious. An accurate assessment of flood disaster loss has become a key issue. In this study, extreme rainstorm scenarios with 50- [...] Read more.
In the context of climate change and rapid urbanization, flood disaster loss caused by extreme rainstorm events is becoming more and more serious. An accurate assessment of flood disaster loss has become a key issue. In this study, extreme rainstorm scenarios with 50- and 100-year return periods based on the Chicago rain pattern were designed. The dynamic change process of flood disaster loss was obtained by using a 1D–2D coupled model, Hazard Rating (HR) method, machine learning, and ArcPy script. The results show that under extreme rainstorm events, the direct economic loss and affected population account for about 3% of the total GDP and 16% of the total population, respectively, and built-up land is the main disaster area. In addition, the initial time and the peak time of flood disaster loss increases with an increasing flood hazard degree and decreases with the increase in the return period. The total loss increases with the increase in the return period, and the unit loss decreases with the increase in the return period. Compared with a static assessment, a dynamic assessment can better reveal the development law of flood disaster loss, which has great significance for flood risk management and the mitigation of flood disaster loss. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Location of the study area and related display. (<b>a</b>) Location of Guangdong Province; (<b>b</b>) location of the study area and average annual precipitation from 2000 to 2019.</p>
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<p>Relevant data in this study, where (<b>a</b>) is the pipe network, (<b>b</b>) is the land use, (<b>c</b>) is the DEM, (<b>d</b>) is the slope map, with a spatial resolution of 30 m. Pipe1 and Pipe2 in Figure (<b>a</b>) are, respectively, the selected pipes for model verification, while Outlet1 and Outlet2 in Figure (<b>b</b>) are, respectively, the selected river channel outlet for model verification.</p>
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<p>Overall research framework.</p>
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<p>Schematic diagram of water exchange between one-dimensional pipeline and two-dimensional surface. (<b>a</b>) h<sub>2D</sub> &lt; h<sub>1D</sub>; (<b>b</b>) h<sub>1D</sub> &lt; Z<sub>2D</sub> &lt; h<sub>2D</sub>; (<b>c</b>) Z<sub>2D</sub> &lt; h<sub>1D</sub> &lt; h<sub>2D</sub>; (<b>d</b>) Z<sub>2D</sub> = h<sub>1D</sub> = h<sub>2D</sub>.</p>
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<p>Spatial distribution of inundation depth and velocity. (<b>a</b>,<b>c</b>) represent inundation depth and flow velocity for 50-year return period; (<b>b</b>,<b>d</b>) represent inundation depth and flow velocity for 100-year return period.</p>
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<p>The river discharge process of basin outlet under different return periods. (<b>a</b>) 50-year return period; (<b>b</b>) 100-year return period.</p>
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<p>The typical pipe inflow process under different return periods. (<b>a</b>) 50-year return period; (<b>b</b>) 100-year return period.</p>
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<p>The statistical results over time for different return periods. (<b>a</b>) Amount of the total flood volume; (<b>b</b>) inundation area.</p>
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<p>Spatial distribution of flood hazard zonation based on HR values. (<b>a</b>) 50-year return period; (<b>b</b>) 100-year return period.</p>
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<p>Correlation and importance of different categories of POIs kernel densities with GDP and population. (<b>a</b>) Correlation coefficient; (<b>b</b>) importance factor.</p>
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<p>Spatial distribution of GDP and population in 2020 predicted by the random forest regression model. (<b>a</b>) GDP; (<b>b</b>) population.</p>
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<p>Flood loss ratio for different land use types and dynamic changes of direct economic loss under four flood hazard degrees for different return periods. (<b>a</b>) Flood loss rate; (<b>b</b>) direct economic loss.</p>
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<p>Dynamic changes of potential flood-affected population and flood-affected population. (<b>a</b>) potential flood-affected population and (<b>b</b>) flood-affected population.</p>
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16 pages, 2190 KiB  
Article
Cloud Transform Algorithm Based Model for Hydrological Variable Frequency Analysis
by Xia Bai, Juliang Jin, Shaowei Ning, Chengguo Wu, Yuliang Zhou, Libing Zhang and Yi Cui
Remote Sens. 2021, 13(18), 3586; https://doi.org/10.3390/rs13183586 - 9 Sep 2021
Cited by 2 | Viewed by 1651
Abstract
Hydrological variable frequency analysis is a fundamental task for water resource management and water conservancy project design. Given the deficiencies of higher distribution features for the upper tail section of hydrological variable frequency curves and the corresponding safer resulting design of water conservancy [...] Read more.
Hydrological variable frequency analysis is a fundamental task for water resource management and water conservancy project design. Given the deficiencies of higher distribution features for the upper tail section of hydrological variable frequency curves and the corresponding safer resulting design of water conservancy projects utilizing the empirical frequency formula and Pearson type III function-based curve fitting method, the normal cloud transform algorithm-based model for hydrological variable frequency analysis was proposed through estimation of the sample empirical frequency by the normal cloud transform algorithm, and determining the cumulative probability distribution curve by overlapping calculation of multiple conceptual cloud distribution patterns, which is also the primary innovation of the paper. Its application result in northern Anhui province, China indicated that the varying trend of the cumulative probability distribution curve of annual precipitation derived from the proposed approach was basically consistent with the result obtained through the traditional empirical frequency formula. Furthermore, the upper tail section of the annual precipitation frequency curve derived from the cloud transform algorithm varied below the calculation result utilizing the traditional empirical frequency formula, which indicated that the annual precipitation frequency calculation result utilizing the cloud transform algorithm was more optimal compared to the results obtained by the traditional empirical frequency formula. Therefore, the proposed cloud transform algorithm-based model was reliable and effective for hydrological variable frequency analysis, which can be further applied in the related research field of hydrological process analysis. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Distribution of regions and observation sites in northern Anhui province, China.</p>
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<p>Distribution of probability density fitting curve of annual precipitation in north Anhui province, China. (<b>a</b>) Guoyangzha Station; (<b>b</b>) Dangshan Station; (<b>c</b>) Linquan Station; (<b>d</b>) Mohekou Station; and (<b>e</b>) Xifeihezha Station.</p>
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<p>Distribution of probability density fitting curve of annual precipitation in north Anhui province, China. (<b>a</b>) Guoyangzha Station; (<b>b</b>) Dangshan Station; (<b>c</b>) Linquan Station; (<b>d</b>) Mohekou Station; and (<b>e</b>) Xifeihezha Station.</p>
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<p>Frequency distribution fitting curve of annual precipitation in northern Anhui province, China. (<b>a</b>) Guoyangzha Station; (<b>b</b>) Dangshan Station; (<b>c</b>) Linquan Station; (<b>d</b>) Mohekou Station; and (<b>e</b>) Xifeihezha Station.</p>
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28 pages, 10008 KiB  
Article
Spatiotemporal Characteristics of the Water Quality and Its Multiscale Relationship with Land Use in the Yangtze River Basin
by Jian Wu, Sidong Zeng, Linhan Yang, Yuanxin Ren and Jun Xia
Remote Sens. 2021, 13(16), 3309; https://doi.org/10.3390/rs13163309 - 20 Aug 2021
Cited by 31 | Viewed by 3841
Abstract
The spatiotemporal characteristics of river water quality are the key indicators for ecosystem health evaluation in basins. Land use patterns, as one of the main driving forces of water quality change, affect stream water quality differently with the variations in the spatiotemporal scales. [...] Read more.
The spatiotemporal characteristics of river water quality are the key indicators for ecosystem health evaluation in basins. Land use patterns, as one of the main driving forces of water quality change, affect stream water quality differently with the variations in the spatiotemporal scales. Thus, quantitative analysis of the relationship between different land cover types and river water quality contributes to a better understanding of the effects of land cover on water quality, the landscape planning of water quality protection, and integrated water resources management. Based on water quality data of 2006–2018 at 18 typical water quality stations in the Yangtze River basin, this study analyzed the spatial and temporal variation characteristics of water quality by using the single-factor water quality identification index through statistical analysis. Furthermore, the Spearman correlation analysis method was adopted to quantify the spatial-scale and temporal-scale effects of various land uses, including agricultural land (AL), forest land (FL), grassland (GL), water area (WA), and construction land (CL), on the stream water quality of dissolved oxygen (DO), chemical oxygen demand (CODMn), and ammonia (NH3-N). The results showed that (1) in terms of temporal variation, the water quality of the river has improved significantly and the tributaries have improved more than the main rivers; (2) in the spatial variation respect, the water quality pollutants in the tributaries are significantly higher than those in the main stream, and the concentration of pollutants increases with the decrease of the distance from the estuary; and (3) the correlation between DO and land use is low, while that between NH3-N, CODMn, and land use is high. CL and AL have a negative effect on water quality, while FL and GL have a purifying effect on water quality. In particular, AL and CL have a significant positive correlation with pollutants in water. Compared with NH3-N, CODMn has a higher correlation with land use at a larger scale. The results highlight the spatial scale and seasonal dependence of land use on water quality, which can provide a scientific basis for land management and seasonal pollution control. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>The location of water quality stations in the study area.</p>
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<p>Diagram of watershed (<b>a</b>) division and buffer zone (<b>b</b>) division in the Yangtze River basin (<b>c</b>) (taking Longdong Station as an example).</p>
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<p>Box plots of water quality concentration of DO (<b>a</b>) COD<sub>Mn</sub> (<b>b</b>), and NH<sub>3</sub>-N (<b>c</b>) in the wet and dry seasons. The X-axis represents water quality stations, and the positive directions along the X-axis indicate an increase in the distance from the site to the estuary. The left side of the green line is the main stream, and the right side is the tributary.</p>
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<p>The monthly identification index of DO of each monitoring section (white block indicates lack of monitoring data). The first seven sites are the trunk streams.</p>
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<p>The monthly identification index of COD<sub>Mn</sub> of each monitoring section (white block indicates lack of monitoring data). The first seven sites are the trunk streams.</p>
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<p>The monthly identification index of NH<sub>3</sub>-N of each monitoring section (white block indicates lack of monitoring data). The first seven sites are the trunk streams.</p>
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<p>Annual changes in water quality identification indexes of different pollutants. The first seven sites are the trunk streams.</p>
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<p>Changing trend in the identification index of comprehensive water quality. The blue line represents a significance level of 0.05, and the red line represents a significance level of 0.01.</p>
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<p>Land use distribution in 2005 (<b>a</b>), 2010 (<b>b</b>), 2015 (<b>c</b>), and 2018 (<b>d</b>).</p>
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<p>Box plot of 18 sites with different land use ratios in each buffer zone in 2018.</p>
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<p>Correlation index of DO and different land use types in different seasons in S1, S2, S3, and S4. Each row from the top to the bottom represents a type of land use.</p>
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<p>Correlation index of COD<sub>MN</sub> and different land use types in different seasons in S1, S2, and S3. Each row from the top to the bottom represents a type of land use.</p>
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<p>Correlation index of NH<sub>3</sub>-N and different land use types in different seasons in S1, S2, and S3. Each row from the top to the bottom represents a type of land use.</p>
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<p>Scatter plot of DO (<b>a</b>), COD<sub>Mn</sub> (<b>b</b>), NH<sub>3</sub>-N (<b>c</b>) concentration, and Q-value. The red line is a linear fitting line. The dark-red shaded area is the 95% confidence interval, and the light-red shaded area is the 95% prediction interval.</p>
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16 pages, 9021 KiB  
Article
The Water Availability on the Chinese Loess Plateau since the Implementation of the Grain for Green Project as Indicated by the Evaporative Stress Index
by Linjing Qiu, Yuting Chen, Yiping Wu, Qingyue Xue, Zhaoyang Shi, Xiaohui Lei, Weihong Liao, Fubo Zhao and Wenke Wang
Remote Sens. 2021, 13(16), 3302; https://doi.org/10.3390/rs13163302 - 20 Aug 2021
Cited by 10 | Viewed by 2456
Abstract
The vegetation coverage on the Loess Plateau (LP) of China has clearly increased since the implementation of the Grain for Green Project in 1999, but there is a debate about whether the improved greenness was achieved at the expense of the balance between [...] Read more.
The vegetation coverage on the Loess Plateau (LP) of China has clearly increased since the implementation of the Grain for Green Project in 1999, but there is a debate about whether the improved greenness was achieved at the expense of the balance between the supply and demand of water resources. Therefore, developing reliable indicators to evaluate the water availability is a prerequisite for maintaining ecological sustainability and ensuring the persistence of vegetation restoration. This study was designed to evaluate water availability on the LP during 2000–2015, using the evaporative stress index (ESI) derived from a remote sensing dataset. The relative dependences of the ESI on climatic and biological factors (including temperature, precipitation and land cover change) were also analyzed. The results showed that the leaf area index (LAI) in most regions of the LP showed a significant increasing trend (p < 0.05), and larger gradients of increase were mainly detected in the central and eastern parts of the LP. The evapotranspiration also exhibited an increasing trend in the central and eastern parts of the LP, with a gradient greater than 10 mm/year. However, almost the whole LP exhibited a decreased ESI from 2000 to 2015, and the largest decrease occurred on the central and eastern LP, indicating a wetting trend. The soil moisture storage in the 0–289-cm soil profiles showed an increasing trend in the central and eastern LP, and the area with an upward trend enlarged with the soil depth. Further analysis revealed that the decreased ESI on the central and eastern LP mainly depended on the increase in the LAI compared with climatic influences. This work not only demonstrated that the ESI was a useful indicator for understanding the water availability in natural and managed ecosystems under climate change but also indicated that vegetation restoration might have a positive effect on water conservation on the central LP. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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Graphical abstract

Graphical abstract
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<p>The geographical location of the LP and the spatial distribution of land cover types on the LP.</p>
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<p>Spatiotemporal change in the LAI on the LP during 2000–2015: (<b>a</b>) the spatial distribution of the mean annual LAI; (<b>b</b>) the annual average LAI for different land cover types; (<b>c</b>) the spatial features of the annual trend of the LAI at the statistically significant level of 0.05; and (<b>d</b>) the area percentage of different land cover types with a significant increasing trend (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>(<b>a</b>) The spatial distribution of the mean annual ET on the LP during 2000–2015; (<b>b</b>) the spatial features of the annual trend of ET with a statistically significant level of 0.05; (<b>c</b>) the spatial distribution of the partial correlation coefficients between ET and LAI eliminating the influences of precipitation and temperature, with a statistically significant level of 0.05; and (<b>d</b>) the area percentage of the region exhibiting an upward trend of ET and partial correlation coefficients greater than 0.6 between the LAI and ET, with a statistically significant level of 0.05.</p>
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<p>The spatial distribution of the mean annual ESI on the LP during 2000–2015 (<b>a</b>) and its slope trends (<b>b</b>).</p>
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<p>The spatial distributions of the annual mean temperature (<b>a</b>) and precipitation (<b>c</b>), and the slopes of the trends of temperature (<b>b</b>) and precipitation (<b>d</b>).</p>
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<p>(<b>a</b>) The spatial distribution of the partial correlation coefficients between the ESI and LAI, eliminating the influences of precipitation and temperature; (<b>b</b>) the spatial distribution of the partial correlation coefficients between the ESI and precipitation, eliminating the influences of LAI and temperature; (<b>c</b>) the spatial distribution of the partial correlation coefficients between the ESI and temperature, eliminating the influences of LAI and precipitation. The small insets in all plots show the spatial distribution of the partial correlation coefficients, while the large insets show only the partial correlation coefficients with a statistically significant level of 0.05.</p>
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<p>Calculated relative dependence of the ESI on precipitation, temperature and the LAI based on (<b>a</b>) multiple regression analysis and (<b>b</b>) partial correlation analysis.</p>
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<p>Spatiotemporal change in the SPEI and AI on the LP during 2000–2015: (<b>a</b>,<b>c</b>) show the spatial distribution of the annual mean SPEI and AI, respectively; (<b>b</b>,<b>d</b>) show the slope of the trends for the SPEI and AI, respectively.</p>
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<p>Spatiotemporal features of soil moisture on the LP during the period of 2000–2015. The left column shows the spatial pattern of linear trends (mm/year) in the 0–7-cm (<b>a</b>), 7–100-cm (<b>d</b>), 100–289-cm (<b>g</b>) and 0–289-cm (<b>j</b>) soil layers. The middle column shows the annual mean soil moisture for the 0–7-cm (<b>b</b>), 7–100-cm (<b>e</b>), 100–289-cm (<b>h</b>) and 0–289-cm (<b>k</b>) soil layers, and the areas with a significant change (<span class="html-italic">p</span> &lt; 0.05) based on <span class="html-italic">t</span>-test are stippled. The right column shows the area-averaged annual soil moisture and its linear trends (mm/year) in the 0–7-cm (<b>c</b>), 7–100-cm (<b>f</b>), 100–289-cm (<b>i</b>) and 0–289-cm (<b>l</b>) soil layers.</p>
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<p>Overview of the methods used in this study.</p>
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Jump to: Research

14 pages, 2528 KiB  
Technical Note
Attributing Evapotranspiration Changes with an Extended Budyko Framework Considering Glacier Changes in a Cryospheric-Dominated Watershed
by Yaping Chang, Yongjian Ding, Qiudong Zhao and Shiqiang Zhang
Remote Sens. 2023, 15(3), 558; https://doi.org/10.3390/rs15030558 - 17 Jan 2023
Cited by 2 | Viewed by 1784
Abstract
The retreat of glaciers has altered hydrological processes in cryospheric regions and affects water resources at the basin scale. It is necessary to elucidate the contributions of environmental changes to evapotranspiration (ET) variation in cryospheric-dominated regions. Considering the upper reach of the Shule [...] Read more.
The retreat of glaciers has altered hydrological processes in cryospheric regions and affects water resources at the basin scale. It is necessary to elucidate the contributions of environmental changes to evapotranspiration (ET) variation in cryospheric-dominated regions. Considering the upper reach of the Shule River Basin as a typical cryospheric-dominated watershed, an extended Budyko framework addressing glacier change was constructed and applied to investigate the sensitivity and contribution of changes in environmental variables to ET variation. The annual ET showed a significant upward trend of 1.158 mm yr−1 during 1982–2015 in the study area. ET was found to be the most sensitive to precipitation (P), followed by the controlling parameter (w), which reflects the integrated effects of landscape alterations, potential evapotranspiration (ET0), and glacier change (∆W). The increase in P was the dominant factor influencing the increase in ET, with a contribution of 112.64%, while the decrease in w largely offset its effect. The contributions of P and ET0 to ET change decreased, whereas that of w increased when considering glaciers using the extended Budyko framework. The change in glaciers played a clear role in ET change and hydrological processes, which cannot be ignored in cryospheric watersheds. These findings are helpful for better understanding changes in water resources in cryospheric regions. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Map of the upper reach of the Shule River Basin (URSRB).</p>
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<p>Temporal variations in annual (<b>a</b>) ET, (<b>b</b>) P, (<b>c</b>) ET<sub>0</sub>, and (<b>d</b>) ∆W during 1982–2015.</p>
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<p>Temporal variations in elasticity coefficients for (<b>a</b>) precipitation ε<sub>P</sub>, (<b>b</b>) potential evapotranspiration ε<sub>ET0</sub>, (<b>c</b>) glacier change ε<sub>∆W</sub> and (<b>d</b>) landscape condition ε<span class="html-italic"><sub>w</sub></span>.</p>
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<p>Elasticity coefficients of ET to P, ET<sub>0</sub>, ∆W, and <span class="html-italic">w</span>.</p>
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<p>Contributions (<b>a</b>) and contribution rates (<b>b</b>) of the variation in P, ET<sub>0</sub>, ∆W, and <span class="html-italic">w</span> to ET variation.</p>
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<p>Relationships between annual ET/P and ET<sub>0</sub>/P in the original Budyko framework (<b>a</b>), and in the extended Budyko framework with glaciers (<b>b</b>).</p>
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<p>Contribution rate of the variation in P, ET<sub>0</sub>, and <span class="html-italic">w</span> to ET variation.</p>
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<p>Variations in controlling parameter <span class="html-italic">w</span> and NDVI (<b>a</b>); and relationship between <span class="html-italic">w</span> and NDVI (<b>b</b>) from 1982 to 2015.</p>
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14 pages, 3433 KiB  
Technical Note
Landsat TM/OLI-Based Ecological and Environmental Quality Survey of Yellow River Basin, Inner Mongolia Section
by Wenlong Gao, Shengwei Zhang, Xinyu Rao, Xi Lin and Ruishen Li
Remote Sens. 2021, 13(21), 4477; https://doi.org/10.3390/rs13214477 - 8 Nov 2021
Cited by 42 | Viewed by 3941
Abstract
The monitoring and maintenance of the Inner Mongolia section of the Yellow River Basin is of great significance to the safety and development of China’s Yellow River Economic Belt and to the protection of the Yellow River ecology. In this study, we calculated [...] Read more.
The monitoring and maintenance of the Inner Mongolia section of the Yellow River Basin is of great significance to the safety and development of China’s Yellow River Economic Belt and to the protection of the Yellow River ecology. In this study, we calculated diagnostic values from a total of 520 Landsat OLI/TM remote sensing images of the Yellow River Basin of Inner Mongolia from 2001 to 2020. Using the RSEI and the GEE Cloud Computing Jigsaw, we analyzed the spatial and temporal distribution of diagnostic values representative of the basin’s ecological status. Further, Mantel and Pearson correlations were used to analyze the significance of environmental factors in affecting the ecological quality of cities along the Yellow River within the study area. The results indicated that the overall mean of RSEI values rose at first and then fell. The RSEI grade to land area ratio was calculated to be highest in 2015 (excellent) and worst in 2001. From 2001 to 2020, ecological quality monitoring process of main cities in the Inner Mongolia region of the Yellow River Basin. Hohhot, Baotou, and Linhe all have an RSEI score greater than 0.5, considered average. However, Dongsheng had its best score (0.60, good) in 2005, which then declined and increased to an average rating in 2020. The RSEI value for Wuhai reached excellent in 2010 but then became poor in 2020, dropping to 0.28. The analysis of ecological quality in the city shows that the greenness index (NDVI) carried the most significant impact on the ecological environment, followed by the humidity index (Wet), the dryness index (NDBSI), the temperature index (Lst), land use, and then regional gross product (RGP). The significance of this study is to provide a real-time, accurate, and rapid understanding of trends in the spatial and temporal distribution of ecological and environmental quality along the Yellow River, thereby providing a theoretical basis and technical support for ecological and environmental protection and high-quality development of the Yellow River Basin. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>(<b>a</b>) Location map, (<b>b</b>) Landsat images, (<b>c</b>) elevation and cities, (<b>d</b>) land use, and (<b>e</b>) land area of the Yellow River, Inner Mongolia section.</p>
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<p>Flow chart showing the ecological quality in the Yellow River, Inner Mongolia section.</p>
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<p>Temporal and spatial distribution (<b>a</b>–<b>e</b>) and mean value (<b>f</b>) of RSEI in the Yellow River, Inner Mongolia section.</p>
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<p>Sankey remote sensing ecological index transfer matrix.</p>
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<p>Spatial and temporal distribution of RSEI in the Yellow River Basin, Inner Mongolia, from 2001 to 2020. From top to bottom: Hohhot, Baotou, Wuhai, Dongsheng, and Linhe.</p>
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<p>Correlation analysis between ecological index and potential influencing factors of cities along the Yellow River, Inner Mongolia section; line segments represent Mantel, circles represent Pearson.</p>
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15 pages, 3569 KiB  
Technical Note
Comparison of Hydrological Patterns between Glacier-Fed and Non-Glacier-Fed Lakes on the Southeastern Tibetan Plateau
by Fangdi Sun, Bin He, Caixia Liu and Yuchao Zeng
Remote Sens. 2021, 13(20), 4024; https://doi.org/10.3390/rs13204024 - 9 Oct 2021
Cited by 1 | Viewed by 1884
Abstract
Lakes on the Tibetan Plateau have experienced variations over the last several decades, and the delineation of lake dynamics is favorable for the regional water cycle and can serve as important information for plateau environmental research. This study focused on 57 lakes near [...] Read more.
Lakes on the Tibetan Plateau have experienced variations over the last several decades, and the delineation of lake dynamics is favorable for the regional water cycle and can serve as important information for plateau environmental research. This study focused on 57 lakes near the Tanggula Mountains on the southeastern Tibetan Plateau. Yearly inundations of the lakes in 1989–2019 and altimeter data available for 2003–2020 were integrated to illustrate the changing patterns of glacier-fed and non-glacier-fed lakes. These two groups of lakes presented very similar evolution stages. They both increased in 1989–1992, decreased in 1992–1996, increased rapidly in 1998–2005, and had batch-wise fluctuations since 2005, with respective areas of around 5305.28 and 1636.79 km2 in the last decade. The non-glacier-fed lakes were more sensitive to precipitation variation, and glacier-fed lakes were more sensitive to temperature changes. Based on lakes with obvious changes in water level, the whole water storage variations of the studied lakes were 1.90 Gt/y in 2003–2009, including 1.80 Gt/y for glacier-fed lakes and 0.10 Gt/y for non-glacier-fed lakes. The contribution from glacier melting in 2003–2009 amounted to 16.11% of the whole lake volume increase. In 2010–2020, water mass changes were 0.42 Gt/y for glacier-fed lakes and −0.14 Gt/y for non-glacier-fed lakes, respectively. The volume increase of glacier-fed lakes in 2010–2020 was mainly due to the expansion of Selin Co. Selin Co experienced a water increase of about 0.46 Gt/y, and the other glacier-fed lakes experienced a decreasing volume of −0.04 Gt/y. In 2010–2020, 99.43% of the glacier contribution supplied Selin Co. Full article
(This article belongs to the Special Issue Remote Sensing in Natural Resource and Water Environment)
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<p>Spatial distribution of the studied lakes, watersheds, and meteorological stations on the southeastern TP. Red points on the lake indicate that CryoSat data are available for the lake and yellow points indicate that ICESat data are available. The Arabic numbers in black circles indicate the glacier-fed basins.</p>
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<p>Comparisons between ICESat and CryoSat data and gauged measurements of Selin Co in 2000–2020 (<b>a</b>–<b>c</b>) indicate correlations between the two kinds of altimeter results and in-situ results, respectively.</p>
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<p>Comparison of areal variations for glacier-fed and non-glacier-fed lakes in 1989–2019.</p>
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<p>The obvious expansions of three representative lakes Nam Co (<b>a</b>), Selin Co (<b>b</b>), and Zige Tangco (<b>c</b>) in 1989–2019. The right two columns indicate lake boundaries of the three lakes in four years 1989, 2000, 2010, and 2019.</p>
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<p>(<b>a</b>–<b>h</b>) Time series of lake area and altimeter-derived water level of eight lakes in 2000–2020.</p>
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<p>Comparison of lake area and water level changes of Puga Co (<b>a</b>) and Ringco Ogma (<b>b</b>) in 2010–2020.</p>
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<p>Annual precipitation (<b>a</b>), lake surface evaporation (<b>b</b>), and mean temperature (<b>c</b>) in 1966–2020, derived from five meteorological stations in the study area. The five thin and dashed lines of different colors in each chart represent variables of different stations, and the solid, red and thick line is the mean value of the five color curves. “G” and “NG” in the legends indicate the area of glacier-fed and non-glacier-fed lakes, respectively.</p>
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