[go: up one dir, main page]
More Web Proxy on the site http://driver.im/
You seem to have javascript disabled. Please note that many of the page functionalities won't work as expected without javascript enabled.
 
 
Sign in to use this feature.

Years

Between: -

Subjects

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Journals

Article Types

Countries / Regions

Search Results (63)

Search Parameters:
Keywords = Jianghan Plain

Order results
Result details
Results per page
Select all
Export citation of selected articles as:
20 pages, 7089 KiB  
Article
Landscape Character Classification with a Deep Neural Network: A Case Study of the Jianghan Plain
by Wenke Qin, Wenpeng Li, Zhuohao Zhang, Weiya Chen and Min Wan
Land 2024, 13(12), 2024; https://doi.org/10.3390/land13122024 - 27 Nov 2024
Viewed by 525
Abstract
Grounded in the theoretical and methodological frameworks of landscape character identification from the European Landscape Map (LANMAP) and landscape character assessment (LCA), this study developed an AI-based tool for landscape character analysis to classify the Jianghan Plain’s landscape more effectively. The proposed method [...] Read more.
Grounded in the theoretical and methodological frameworks of landscape character identification from the European Landscape Map (LANMAP) and landscape character assessment (LCA), this study developed an AI-based tool for landscape character analysis to classify the Jianghan Plain’s landscape more effectively. The proposed method leveraged a deep learning model, the artificial intelligence-based landscape character (AI-LC) classifier, along with specific naming and coding rules for the unique landscape character of the Jianghan Plain. Experimental results showed a significant improvement in classification accuracy, reaching 89% and 86% compared to traditional methods. The classifier identified 10 macro-level and 18 meso-level landscape character types within the region, which were further categorized into four primary zones—a lake network river basin, a hillfront terrace, surrounding mountains, and a lake network island hill—based on natural and social features. These advancements contributed to the theoretical framework of landscape character assessment, offering practical insights for landscape planning and conservation while highlighting AI’s transformative potential in environmental research and management. Full article
Show Figures

Figure 1

Figure 1
<p>Map of the Jianghan Plain and its specific administrative boundaries.</p>
Full article ">Figure 2
<p>Description of system architecture. (<b>a</b>) Landscape character classification and recognition system; (<b>b</b>) remote sensing images of different channels; (<b>c</b>) convolutional neural network model used in classification system.</p>
Full article ">Figure 3
<p>Distribution of landscape character area thresholds in the Jianghan Plain.</p>
Full article ">Figure 4
<p>Naming and coding rules of landscape characters for Jianghan Plain.</p>
Full article ">Figure 5
<p>Maps showing (<b>a</b>) a landscape character distribution map of the Jianghan Plain. (<b>b</b>) Landscape character labeling process for the Jianghan Plain.</p>
Full article ">Figure 6
<p>Landscape character classification of the 4 km × 4 km area.</p>
Full article ">Figure 7
<p>Examples of right and wrong classification results.</p>
Full article ">Figure 8
<p>Maps showing (<b>a</b>) low-elevation farmland of 4 km × 4 km unit. (<b>b</b>) New added water landscapes of 2 km × 2 km unit. (<b>c</b>) New added city landscapes of 2 km × 2 km unit.</p>
Full article ">Figure 9
<p>Same landscape character at different research scales.</p>
Full article ">
24 pages, 265 KiB  
Article
The Impact of Agricultural Socialization Services on the Ecological Protection of Rice Farmland in Jianghan Plain, China
by Wenjun Zhuo, Zhi Zeng and Xinsheng Pang
Sustainability 2024, 16(21), 9206; https://doi.org/10.3390/su16219206 - 23 Oct 2024
Viewed by 789
Abstract
The ecological protection of cultivated land is crucial for advancing high-quality agricultural development. This study analyzes the impact of agricultural socialization services on the ecological conservation of farmland, focusing on the reduction of chemical fertilizers and pesticides among rice farmers in the Jianghan [...] Read more.
The ecological protection of cultivated land is crucial for advancing high-quality agricultural development. This study analyzes the impact of agricultural socialization services on the ecological conservation of farmland, focusing on the reduction of chemical fertilizers and pesticides among rice farmers in the Jianghan Plain area. Utilizing data from 743 farmer household surveys conducted in 2023, the findings reveal that agricultural socialization services significantly encourage farmers to reduce chemical input usage. For every 1% increase in the level of agricultural social services, the average fertilizer use per hectare will decrease by 14% and the average pesticide use per hectare will decrease by 16.4%. The study identifies scale operation, factor substitution, and alleviation of capital constraints as mediating factors enhancing the efficacy of these services. Furthermore, heterogeneity analysis indicates that these services are more effective in reducing chemical inputs among large-scale and newer-generation farmers compared to their small-scale and older counterparts. Additionally, technology-intensive socialized services exhibit a stronger impact on reducing chemical inputs than labor-intensive services. Full article
17 pages, 5340 KiB  
Article
Early-Stage Mapping of Winter Canola by Combining Sentinel-1 and Sentinel-2 Data in Jianghan Plain China
by Tingting Liu, Peipei Li, Feng Zhao, Jie Liu and Ran Meng
Remote Sens. 2024, 16(17), 3197; https://doi.org/10.3390/rs16173197 - 29 Aug 2024
Viewed by 771
Abstract
The early and accurate mapping of winter canola is essential in predicting crop yield, assessing agricultural disasters, and responding to food price fluctuations. Although some methods have been proposed to map the winter canola at the flowering or later stages, mapping winter canola [...] Read more.
The early and accurate mapping of winter canola is essential in predicting crop yield, assessing agricultural disasters, and responding to food price fluctuations. Although some methods have been proposed to map the winter canola at the flowering or later stages, mapping winter canola planting areas at the early stage is still challenging, due to the insufficient understanding of the multi-source remote sensing features sensitive for winter canola mapping. The objective of this study was to evaluate the potential of using the combination of optical and synthetic aperture radar (SAR) data for mapping winter canola at the early stage. We assessed the contributions of spectral features, backscatter coefficients, and textural features, derived from Sentinel-2 and Sentinel-1 SAR images, for mapping winter canola at early stages. Random forest (RF) and support vector machine (SVM) classification models were built to map winter canola based on early-stage images and field samples in 2017 and then the best model was applied to corresponding satellite data in 2018–2022. The following results were obtained: (1) The red edge and near-infrared-related spectral features were most important for the mapping of early-stage winter canola, followed by VV (vertical transmission, vertical reception), DVI (Difference vegetation index), and GOSAVI (Green Optimized Soil Adjusted Vegetation Index); (2) based on Sentinel-1 and Sentinel-2 data, winter canola could be mapped as early as 130 days prior to ripening (i.e., early overwinter stage), with the F-score over 0.85 and the OA (Overall Accuracy) over 81%; (3) adding Sentinel-1 could improve the OA by about 2–4% and the F-score by about 1–2%; and (4) based on the classifier transfer approach, the F-scores of winter canola mapping in 2018–2022 varied between 0.75 and 0.97, and the OAs ranged from 79% to 86%. This study demonstrates the potential of early-stage winter canola mapping using the combination of Sentinel-2 and Sentinel-1 images, which could enable the large-scale early mapping of canola and provide valuable information for stakeholders and decision makers. Full article
(This article belongs to the Special Issue Within-Season Agricultural Monitoring from Remotely Sensed Data)
Show Figures

Figure 1

Figure 1
<p>Flowchart of the study.</p>
Full article ">Figure 2
<p>Study area (from Globe Land30 2010 dataset).</p>
Full article ">Figure 3
<p>Optical image coverage and spatial distribution of samples in Jianghan Plain from 2017 to 2022.</p>
Full article ">Figure 4
<p>RGB images showing phenological stages of winter canola in the experiment.</p>
Full article ">Figure 5
<p>Backscatter coefficient distributions of winter canola during different phenological stages across different land types (Different letters represent significant differences between crops).</p>
Full article ">Figure 6
<p>Textural features of winter canola and other land types at different phenological stages (Different letters represent significant differences between crops).</p>
Full article ">Figure 7
<p>Spectral features and significant difference tests of land types at different phenological stages (Different letters represent significant differences between crops).</p>
Full article ">Figure 8
<p>Mapping accuracy of winter canola at different phenological stages based on Sentinel-1 data.</p>
Full article ">Figure 9
<p>Mapping accuracy of winter canola in 2018–2022 based Sentinel-1 and Sentinel-2 data.</p>
Full article ">Figure 10
<p>Maps of winter canola in 2017–2022.</p>
Full article ">
33 pages, 17476 KiB  
Article
Driving Analysis and Multi Scenario Simulation of Ecosystem Carbon Storage Changes Based on the InVEST-PLUS Coupling Model: A Case Study of Jianli City in the Jianghan Plain of China
by Jun Shao, Yuxian Wang, Mingdong Tang and Xinran Hu
Sustainability 2024, 16(16), 6736; https://doi.org/10.3390/su16166736 - 6 Aug 2024
Viewed by 1280
Abstract
The carbon storage capacity of terrestrial ecosystems serves as a crucial metric for assessing ecosystem health and their resilience to climate change. By evaluating the effects of land use alterations on this storage, carbon management strategies can be improved, thereby promoting carbon reduction [...] Read more.
The carbon storage capacity of terrestrial ecosystems serves as a crucial metric for assessing ecosystem health and their resilience to climate change. By evaluating the effects of land use alterations on this storage, carbon management strategies can be improved, thereby promoting carbon reduction and sequestration. While county-level cities are pivotal to ecological conservation and high-quality development, they often face developmental challenges. Striking a balance between economic growth and meeting peak carbon emissions and carbon neutrality objectives is particularly challenging. Consequently, there is an urgent need to bolster research into carbon storage management. The study focuses on Jianli City, employing the InVEST model and land use data to examine the response patterns of land use changes and terrestrial system carbon storage from 2000 to 2020. Using the PLUS model, the study simulated the land use and carbon storage in Jianli City for the year 2035 under three scenarios: Natural Development scenario, Urban Expansion scenario, and Ecology and food security scenario. Our findings indicate the following: (1) Between 2000 and 2020, significant shifts in land use were observed in Jianli City. These changes predominantly manifested as the interchange between Cropland and Water areas and the enlargement of impervious surfaces, leading to a decrease of 691,790.27 Mg in carbon storage. (2) Under the proposed scenarios—Natural Development scenario, Urban Expansion scenario, and Ecology and food security scenario—the estimated carbon storage capacities in Jianli City were 39.95 Tg, 39.90 Tg, and 40.14 Tg, respectively. When compared with the 2020 data, all these estimates showed an increase. In essence, our study offers insights into optimizing land use structures from a carbon storage standpoint to ensure stability in Jianli’s carbon storage levels while mitigating the risks associated with carbon fixation. This has profound implications for the harmonious evolution of regional eco-economies. Full article
Show Figures

Figure 1

Figure 1
<p>Study area.</p>
Full article ">Figure 2
<p>Research framework.</p>
Full article ">Figure 3
<p>Land use transfer chord map from 2000 to 2020.</p>
Full article ">Figure 4
<p>Land use transfer sankey map from 2000 to 2020.</p>
Full article ">Figure 5
<p>Land use status from 2000 to 2020.</p>
Full article ">Figure 5 Cont.
<p>Land use status from 2000 to 2020.</p>
Full article ">Figure 6
<p>Expansion probability of each land use type.</p>
Full article ">Figure 7
<p>Land use status under three scenarios.</p>
Full article ">Figure 8
<p>Variations in carbon storage and geo-averaged carbon density of terrestrial systems from 2000 to 2020.</p>
Full article ">Figure 9
<p>Spatial distribution of carbon storage from 2000 to 2020.</p>
Full article ">Figure 10
<p>Carbon stock changes from 2000 to 2020.</p>
Full article ">Figure 10 Cont.
<p>Carbon stock changes from 2000 to 2020.</p>
Full article ">Figure 11
<p>The change in carbon storage and carbon sink economy caused by land use type conversion from 2000 to 2020.</p>
Full article ">Figure 11 Cont.
<p>The change in carbon storage and carbon sink economy caused by land use type conversion from 2000 to 2020.</p>
Full article ">Figure 12
<p>Spatial distribution of carbon storage under three scenarios.</p>
Full article ">Figure 13
<p>The change in carbon storage and carbon sink economy caused by land use type conversion under three scenarios.</p>
Full article ">Figure 13 Cont.
<p>The change in carbon storage and carbon sink economy caused by land use type conversion under three scenarios.</p>
Full article ">Figure 14
<p>Driving factors.</p>
Full article ">Figure 15
<p>Importance of driving factors for each land use type.</p>
Full article ">
29 pages, 29985 KiB  
Article
Research on Jianghan Plain Water System Dynamics and Influences with Multiple Landsat Satellites
by Feiyan Dong, Jie Huang, Linkui Meng, Linyi Li and Wen Zhang
Remote Sens. 2024, 16(15), 2770; https://doi.org/10.3390/rs16152770 - 29 Jul 2024
Viewed by 877
Abstract
The study of the spatio-temporal distribution and evolution trends of water resources in large regions plays an important role in the study of regional water resource planning, regional economic and social development, and water disasters. In this study, a Landsat multi-index relationship and [...] Read more.
The study of the spatio-temporal distribution and evolution trends of water resources in large regions plays an important role in the study of regional water resource planning, regional economic and social development, and water disasters. In this study, a Landsat multi-index relationship and water probability thresholding method is developed based on the Google Earth Engine (GEE) platform, which can support the integration of multiple Landsat satellites. The algorithm jointly combines multiple remote sensing metrics along with the calculation of water probability to produce an interannual water body product for the Jianghan Plain on a 20-year time series. The results indicate that the Landsat multi-index relationship algorithm used in this study has high accuracy in extracting long-term water bodies in extensive, flat terrain areas such as the Jianghan Plain, with an overall accuracy (OA) of 97.23%. By analyzing the water body products and landscape patterns, we have identified the following features: (1) From 2002 to 2021, the changes in river water bodies in the Jianghan Plain were relatively small, and some lakes experienced a shrinkage in area. Overall, there is a strong correlation between water distribution and precipitation. (2) The complexity index of water bodies shows a strong negative correlation with effective irrigation area and population, indicating a strong mutual influence between water bodies and socio-economic activities. (3) Through the study of the distribution characteristics of built-up areas and the water system, it was found that for large rivers, the larger the size of the river, the more built-up areas are nearby. Most extensive built-up areas are located near large rivers. This study contributes to providing methods and data support for urban planning, water resource management, and disaster research in the Jianghan Plain. Full article
(This article belongs to the Section Remote Sensing for Geospatial Science)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Schematic map of Jianghan Plain.</p>
Full article ">Figure 2
<p>Algorithm flow chart.</p>
Full article ">Figure 3
<p>Water images obtained with different thresholds. (<b>a</b>) The water system range of Jianghan Plain when the threshold is 1. (<b>b</b>) The water system range of Jianghan Plain when the threshold is 0.4.</p>
Full article ">Figure 4
<p>Sample point display.</p>
Full article ">Figure 5
<p>Comparison of 10-year water extraction accuracy among three methods (excluding SDWI Index). (<b>a</b>) Landsat Multi-Index Relationship and Water Probability Thresholding Method. (<b>b</b>) JRC Dataset. (<b>c</b>) Landsat 8 Forever.</p>
Full article ">Figure 5 Cont.
<p>Comparison of 10-year water extraction accuracy among three methods (excluding SDWI Index). (<b>a</b>) Landsat Multi-Index Relationship and Water Probability Thresholding Method. (<b>b</b>) JRC Dataset. (<b>c</b>) Landsat 8 Forever.</p>
Full article ">Figure 6
<p>Sources of error in water body extraction results. (<b>a</b>) Original image. (<b>b</b>) Range of incorrect extraction of water bodies in 2021. (<b>c</b>) Original image. (<b>d</b>) Scope of narrow water extraction in 2021.</p>
Full article ">Figure 7
<p>Water area of the Jianghan Plain from 2002 to 2021.</p>
Full article ">Figure 8
<p>Comparison of water system changes in Jianghan Plain between 2002 and 2021.</p>
Full article ">Figure 9
<p>Water system of the Jianghan Plain from 2002 to 2021.</p>
Full article ">Figure 9 Cont.
<p>Water system of the Jianghan Plain from 2002 to 2021.</p>
Full article ">Figure 9 Cont.
<p>Water system of the Jianghan Plain from 2002 to 2021.</p>
Full article ">Figure 9 Cont.
<p>Water system of the Jianghan Plain from 2002 to 2021.</p>
Full article ">Figure 10
<p>Overall water body landscape index of the Jianghan Plain region from 2002 to 2021.</p>
Full article ">Figure 11
<p>Excess water bodies in 2016 compared to 2005.</p>
Full article ">Figure 12
<p>Water landscape index in the Jianghan Plain region in 2021.</p>
Full article ">Figure 13
<p>The precipitation in Hannan District and Honghu City.</p>
Full article ">Figure 14
<p>Water system of Caidian District and Honghu City. (<b>a</b>) Distribution of water systems in Caidian District. (<b>b</b>) Caidian District Water Landscape Index. (<b>c</b>) Distribution of water systems in Honghu City. (<b>d</b>) Honghu City Water Landscape Index.</p>
Full article ">Figure 15
<p>Scatter plot of urban economic attributes and water body landscape index. (<b>a</b>) Correlation Analysis between Shape Index and Effective Irrigation Area. (<b>b</b>) Correlation Analysis between Shape Indes and Registered Residence Population. (<b>c</b>) Correlation Analysis between Shape Index and Permanent Population. (<b>d</b>) Correlation Analysis between Water Area and Land Area. (<b>e</b>) Correlation Analysis between Water Area and Primary Industry. (<b>f</b>) Correlation Analysis between Water Area andEffective lrrigation Area. (<b>g</b>) Correlation Analysis between Shape Index and Land Area. (<b>h</b>) Correlation Analysis between Shape Index and Cultivated Land Area.</p>
Full article ">Figure 15 Cont.
<p>Scatter plot of urban economic attributes and water body landscape index. (<b>a</b>) Correlation Analysis between Shape Index and Effective Irrigation Area. (<b>b</b>) Correlation Analysis between Shape Indes and Registered Residence Population. (<b>c</b>) Correlation Analysis between Shape Index and Permanent Population. (<b>d</b>) Correlation Analysis between Water Area and Land Area. (<b>e</b>) Correlation Analysis between Water Area and Primary Industry. (<b>f</b>) Correlation Analysis between Water Area andEffective lrrigation Area. (<b>g</b>) Correlation Analysis between Shape Index and Land Area. (<b>h</b>) Correlation Analysis between Shape Index and Cultivated Land Area.</p>
Full article ">Figure 16
<p>Relationship between distance to major rivers and area of built-up areas. (<b>a</b>) the closest distance to the Yangtze River. (<b>b</b>)the nearest distance to the Han River. (<b>c</b>) the closest distance to the Hanbei River. (<b>d</b>) the closest distance to the Nejing River. (<b>e</b>) the closest distance to the Dongjing Rivel.</p>
Full article ">Figure 17
<p>The spatial distribution of water system and built-up areas in Jianghan Plain.</p>
Full article ">Figure 18
<p>The area of urban development near large lakes.</p>
Full article ">Figure 19
<p>The distribution of the distance between Changhu and Honghu and the city center: (<b>a</b>) the distance between Jingzhou City and the Yangtze River and Changhu; (<b>b</b>) the distance between Honghu City and the Yangtze River and Honghu.</p>
Full article ">
15 pages, 1021 KiB  
Article
A Study of the Income Effect of Continuous Adoption of Rice–Crayfish Co-Culture Technology: Based on the Moderating Effect of Non-Farm Employment
by Zhuoya Tian, Xicong Wang, Zekui Lei, Zhenhong Qi and Zhe Liu
Agriculture 2024, 14(8), 1224; https://doi.org/10.3390/agriculture14081224 - 25 Jul 2024
Viewed by 647
Abstract
The income effect of rice–crayfish co-culture technology (RCT) is directly related to rate of adoption of farmers and the process of China’s green development of agriculture. The aim of this study is to explore the income effect and income growth mechanism of rice–crayfish [...] Read more.
The income effect of rice–crayfish co-culture technology (RCT) is directly related to rate of adoption of farmers and the process of China’s green development of agriculture. The aim of this study is to explore the income effect and income growth mechanism of rice–crayfish co-culture technology from the perspective of continuous adoption. With the treatment effect model (TEM), this paper empirically analyzes the income effect and income-generating mechanisms of RCT using field survey data from 736 farmers in the Jianghan Plain. As a result of this study, it was discovered that RCT will increase farmers’ net agricultural income by RMB 83,430 if they continue to adopt it. Further examinations indicate that the optimal adoption period for RCT is four and a half years. Additionally, it has also been shown that non-farm employment positively moderates the relationship between continuous adoption of RCT and net agricultural income. Farmers who participate in non-farm employment and continue to adopt the RCT will experience an increase in net agricultural income by RMB 104,510. Therefore, our results suggest that it is necessary to encourage farmers to continuously adopt RCT and actively participate in non-farm employment to enhance the income effect of RCT. Full article
(This article belongs to the Section Agricultural Economics, Policies and Rural Management)
Show Figures

Figure 1

Figure 1
<p>The relationship between several adoption behaviors.</p>
Full article ">Figure 2
<p>Diagram of the theoretical analysis framework.</p>
Full article ">Figure 3
<p>The cumulative distribution function of net agricultural income.</p>
Full article ">
16 pages, 5752 KiB  
Article
Low-Permeability Layered Clay Soil Hinders Organic Macromolecular Pollutant Migration in the Transition Zone of the Jianghan Plain–Dabie Mountain Area
by Tingting Shi, Wenyan Liu, Yulin Yang, Yongyi Liu, Mengru Li, Tianwen Liu, Zhichen Wu and Qing Wang
Water 2024, 16(11), 1522; https://doi.org/10.3390/w16111522 - 25 May 2024
Viewed by 1009
Abstract
With the development of industry and agriculture, the level of organic pollutants in groundwater exceeds the standard in some parts of the transition zone of the Jianghan Plain–Dabie Mountain area. To investigate the ability of low-permeability layered clay soil in the study area [...] Read more.
With the development of industry and agriculture, the level of organic pollutants in groundwater exceeds the standard in some parts of the transition zone of the Jianghan Plain–Dabie Mountain area. To investigate the ability of low-permeability layered clay soil in the study area to hinder the migration of organic macromolecular pollutants, the traditional tracer fluorescein sodium was used to represent organic macromolecular pollutants. The adsorption and migration behavior of organic macromolecular pollutants in the layered soil were explored through indoor experiments. Additionally, a one-dimensional soil column solute transport model was established for the study area using HYDRUS-1D to obtain the dispersivities and dispersion coefficients of organic macromolecular pollutants in layered clay soil. The results showed that the breakthrough duration of sodium fluorescein was up to 116 days in silty clay soil, while the breakthrough duration in sandy sub-sandy soil was only 2.6 days. The dispersion coefficient of organic macromolecular pollutants was only 0.0038 cm2/d in silty clay soil, while the dispersion coefficient was up to 4.724 cm2/d in sandy sub-sandy soil. The dispersion coefficient decreased with the increasing clay fraction of the soil. Compared with homogeneous soil, the dispersivity of organic macromolecular pollutants in clayed soil decreased, and the dispersion coefficient also changed. It indicates that the layered clay soil in the study area effectively hinders the downward migration of organic macromolecular pollutants due to its low permeability and pollutant adsorption capacity. Simultaneously, the lateral transport of water at different soil interfaces in layered soil prolongs the time for organic macromolecular pollutants to reach the underlying aquifer. Low-permeability clay soil may act as a short-term barrier to the migration of organic pollutants to deeper soil and groundwater in the study area. This study provides data support and a theoretical basis for future pollution prevention and control in the Jianghan Plain–Dabie Mountain area. Full article
(This article belongs to the Section Hydrogeology)
Show Figures

Figure 1

Figure 1
<p>Geological map of study area with location of field test site.</p>
Full article ">Figure 2
<p>Schematic sketch of the experimental set-up of the column leaching experiments.</p>
Full article ">Figure 3
<p>Kinetic adsorption properties of fluorescein sodium on the soil samples.</p>
Full article ">Figure 4
<p>Isotherm adsorption properties of fluorescein sodium on the soil samples.</p>
Full article ">Figure 5
<p>Fluorescein sodium breakthrough curves of soil columns. (<b>a</b>) Breakthrough curves of homogeneous soil columns; (<b>b</b>) breakthrough curves of layered soil columns.</p>
Full article ">
19 pages, 27146 KiB  
Article
Analysis of Lake Area Dynamics and Driving Forces in the Jianghan Plain Based on GEE and SEM for the Period 1990 to 2020
by Minghui He and Yi Liu
Remote Sens. 2024, 16(11), 1892; https://doi.org/10.3390/rs16111892 - 24 May 2024
Viewed by 1034
Abstract
The lakes of Jianghan Plain, as an important component of the water bodies in the middle and lower reaches of the Yangtze River plain, have made significant contributions to maintaining the ecological health and promoting the sustainable development of the Jianghan Plain. However, [...] Read more.
The lakes of Jianghan Plain, as an important component of the water bodies in the middle and lower reaches of the Yangtze River plain, have made significant contributions to maintaining the ecological health and promoting the sustainable development of the Jianghan Plain. However, there is a relatively limited understanding regarding the trends of lake area change for different types of lakes and their dominant factors over the past three decades in the Jianghan Plain. Based on the Google Earth Engine (GEE) platform, combined with the water body index method, the changes in area of three different types of lakes (area > 1 km2) in the Jianghan Lake Group from 1990 to 2020 were extracted and analyzed. Additionally, the Partial least squares structural equation model (PLS-SEM) was utilized to analyze the driving factors affecting the changes in water body area of these lakes. The results show that from 1990 to 2020, the area of the lakes of the wet season and level season exhibited a decreasing trend, decreasing by 893.1 km2 and 77.9 km2, respectively. However, the area of dry season lakes increased by 59.27 km2. The areas of all three types of lakes reached their minimum values in 2006. According to the PLS-SEM results, the continuous changes in the lakes’ area are mainly controlled by environmental factors overall. Furthermore, human factors mainly influence the mutation of the lakes’ area. This study achieved precise extraction of water body areas and accurate analysis of driving factors, providing a basis for a comprehensive understanding of the dynamic changes in the lakes of Jianghan Plain, which is beneficial for the rational utilization and protection of water resources. Full article
Show Figures

Figure 1

Figure 1
<p>The location map of the study area.</p>
Full article ">Figure 2
<p>A flowchart showing the study’s conceptual framework and procedures.</p>
Full article ">Figure 3
<p>Changes in the lakes’ area from 1990 to 2020. The W-W is the area change trends of the wet seasonal lakes. The L-W is the area change trends of the level seasonal lakes. The D-W is the area change trends of the dry seasonal lakes.</p>
Full article ">Figure 4
<p>The M–K mutation test of W-W (<b>a</b>), L-W (<b>b</b>), and D-W (<b>c</b>). UF stands for upward trend, UB stands for downward trend, and the two red dashed lines represent the 95% confidence interval.</p>
Full article ">Figure 5
<p>The Pearson correlation analysis results of all the factors.</p>
Full article ">Figure 6
<p>The continuous wavelet transform of all the factors. The black line represents the wavelet boundary effect about the cone of influence. The vertical axis of the image represents the cycle of change, while the horizontal axis represents the years. The color of a point on the graph indicates the strength of the energy of the change cycle for that year. The closer the color is to red, the stronger the energy of the cycle change, and vice versa.</p>
Full article ">Figure 7
<p>(<b>a</b>) The wet seasonal lake structural equation model. (<b>b</b>) The level seasonal lake structural equation model. (<b>c</b>) The dry seasonal lake structural equation model (Orange lines indicate positive path coefficients; light green lines indicate negative path coefficients). * indicates that <span class="html-italic">p</span> &lt; 0.05, the path is significant.</p>
Full article ">
24 pages, 6087 KiB  
Article
Spatial Analysis on Resource Utilization, Environmental Consequences and Sustainability of Rice–Crayfish Rotation System in Jianghan Plain, China
by Hang Shi, Guang Han, Naijuan Hu, Shuyang Qu and Liqun Zhu
Agronomy 2024, 14(5), 1071; https://doi.org/10.3390/agronomy14051071 - 18 May 2024
Cited by 1 | Viewed by 1253
Abstract
The rice–crayfish rotation system (RCR), originating in the Jianghan Plain, is developing rapidly in various regions of China and has been characterized by unbalanced regional development, which has also led to widespread concerns and discussion on its environmental impacts and sustainability. This study [...] Read more.
The rice–crayfish rotation system (RCR), originating in the Jianghan Plain, is developing rapidly in various regions of China and has been characterized by unbalanced regional development, which has also led to widespread concerns and discussion on its environmental impacts and sustainability. This study selects representative RCR production areas in the Jianghan Plain, including Jianli, Qianjiang, Shishou, Shayang, Gong’an and Honghu, to analyze resource inputs, resource utilization efficiency, environmental impacts and sustainability by employing the emergy analysis method. Our analysis of Jianli, Honghu, Qianjiang, Gong’an, Shishou and Shayang reports total emergy inputs ranging from 6.46 × 1016 to 8.25 × 1016, with renewable rates between 78.38% and 84.34%. Shishou leads in the unit emergy value (5.58 × 10−1) and the emergy yield ratio (5.30). The sustainability evaluation finds that the environmental loading ratio is from 0.19 to 0.28 and the emergy index for sustainable development varies between 1.27 and 3.00. This analysis indicates that the southern regions have higher inputs and efficiency, with southeastern areas showing lower environmental impact and higher sustainability. We also underscore the impact of non-renewable resources on environmental outcomes and sustainability, suggesting tailored development strategies for the rice–crayfish rotation system’s optimization and sustainable growth. Full article
(This article belongs to the Section Agroecology Innovation: Achieving System Resilience)
Show Figures

Figure 1

Figure 1
<p>Location of the study area in China.</p>
Full article ">Figure 2
<p>Energy flow diagram of RCR.</p>
Full article ">Figure 3
<p>Structure and value of resource inputs in each region for RCR (Sejx10<sup>16</sup>).</p>
Full article ">Figure 4
<p>Proportion of resources invested in each region for RCR.</p>
Full article ">Figure 5
<p>Spatial distribution of total inputs (U) for RCR (Sej).</p>
Full article ">Figure 6
<p>Spatial distribution of renewable fraction (%R) for RCR.</p>
Full article ">Figure 7
<p>Detailed emergy value of economic purchased resource for RCR in each region (Sejx10<sup>16</sup>).</p>
Full article ">Figure 8
<p>Detailed emergy proportion of economic purchased resources for RCR in each region.</p>
Full article ">Figure 9
<p>Spatial distribution of unit emergy value (UEV) for RCR.</p>
Full article ">Figure 10
<p>Spatial distribution of emergy yield ratio (EYR) for RCR.</p>
Full article ">Figure 11
<p>Spatial distribution of environmental load ratio (ELR) for RCR.</p>
Full article ">Figure 12
<p>Spatial distribution of emergy index for sustainable development (EISD) for RCR.</p>
Full article ">
18 pages, 15707 KiB  
Article
Unraveling the Coupled Dynamics between DOM Transformation and Arsenic Mobilization in Aquifer Systems during Microbial Sulfate Reduction: Evidence from Sediment Incubation Experiment
by Xingguo Du, Hui Li, Yue Jiang, Jianfei Yuan and Tianliang Zheng
Water 2024, 16(9), 1266; https://doi.org/10.3390/w16091266 - 28 Apr 2024
Viewed by 1426
Abstract
Geogenic arsenic (As)-rich groundwater poses a significant environmental challenge worldwide, yet our understanding of the interplay between dissolved organic matter (DOM) transformation and arsenic mobilization during microbial sulfate reduction remains limited. This study involved microcosm experiments using As-rich aquifer sediments from the Singe [...] Read more.
Geogenic arsenic (As)-rich groundwater poses a significant environmental challenge worldwide, yet our understanding of the interplay between dissolved organic matter (DOM) transformation and arsenic mobilization during microbial sulfate reduction remains limited. This study involved microcosm experiments using As-rich aquifer sediments from the Singe Tsangpo River basin (STR) and Jianghan Plain (JHP), respectively. The findings revealed that microbial sulfate reduction remarkably increased arsenic mobilization in both STR and JHP sediments compared to that in unamended sediments. Moreover, the mobilization of As during microbial sulfate reduction coincided with increases in the fluorescence intensity of two humic-like substances, C2 and C3 (R = 0.87/0.87 and R = 0.73/0.66 in the STR and JHP sediments, respectively; p < 0.05), suggesting competitive desorption between DOM and As during incubation. Moreover, the transformations in the DOM molecular characteristics showed significant increases in CHOS molecular and low-O/C-value molecular intensities corresponding to the enhancement of microbial sulfate reduction and the possible occurrence of methanogenesis processes, which suggests a substantial bioproduction contribution to DOM components that is conducive to As mobilization during the microbial sulfate reduction. The present results thus provide new insights into the co-evolution between As mobilization and DOM transformations in alluvial aquifer systems under strong microbial sulfate reduction conditions. Full article
(This article belongs to the Section Water Quality and Contamination)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Geographical location of sediment sampling sites in the Singe Tsangpo River basin and the Jianghan Plain. (<b>a</b>) The geographic locations of sediment sampling sites. (<b>b</b>) The vertical section of shallow alluvial aquifers from the STR. (<b>c</b>) The aquifer medium structure of JHP.</p>
Full article ">Figure 2
<p>Variations in As<sub>total</sub>, SO<sub>4</sub><sup>2−</sup>, and Fe(II)<sub>total</sub> concentrations from different microcosm groups during the incubation period.</p>
Full article ">Figure 3
<p>Variations in the concentrations of As(III) and As(V) species from different microcosm groups during the incubation period.</p>
Full article ">Figure 4
<p>The variations in <span class="html-italic">dsrB</span>, <span class="html-italic">arsM,</span> and <span class="html-italic">arrA</span> gene abundance during the incubation.</p>
Full article ">Figure 5
<p>The variations in the fluorescence intensities of C1, C2, and C3 during the incubation.</p>
Full article ">Figure 6
<p>The van Krevelen diagram of DOM molecular distribution (<b>a</b>) and the variations in the relative abundance of DOM identified as different organic components and molecular compositions (<b>b</b>).</p>
Full article ">Figure 7
<p>The variations in the molecular compositions before and after incubation in the JHP_NA/STR_NA and JHP_CS/STR_CS groups.</p>
Full article ">
25 pages, 18893 KiB  
Article
Understanding the Spatiotemporal Dynamics and Influencing Factors of the Rice–Crayfish Field in Jianghan Plain, China
by Fang Luo, Yiqing Zhang and Xiang Zhao
Remote Sens. 2024, 16(9), 1541; https://doi.org/10.3390/rs16091541 - 26 Apr 2024
Viewed by 1115
Abstract
The rice–crayfish co-culture system, a representative of Agri-aqua food systems, has emerged worldwide as an effective strategy for enhancing agricultural land use efficiency and boosting sustainability, particularly in China and Southeast Asia. Despite its widespread adoption in China’s Jianghan Plain, the exact spatiotemporal [...] Read more.
The rice–crayfish co-culture system, a representative of Agri-aqua food systems, has emerged worldwide as an effective strategy for enhancing agricultural land use efficiency and boosting sustainability, particularly in China and Southeast Asia. Despite its widespread adoption in China’s Jianghan Plain, the exact spatiotemporal dynamics and factors influencing this practice in this region are yet to be clarified. Therefore, understanding the spatiotemporal dynamics and influencing factors of the rice–crayfish fields (RCFs) is crucial for promoting the rice–crayfish co-culture system, and optimizing land use policies. In this study, we identified the spatial distribution of RCF using Sentinel-2 images and land use spatiotemporal data to analyze its spatiotemporal dynamics during the period of 2016–2020. Additionally, we used the Multiscale Geographically Weighted Regression model to explore the key factors influencing RCF’s spatiotemporal changes. Our findings reveal that (1). the RCF area in Jianghan Plain expanded from 1216.04 km2 to 2429.76 km2 between 2016 and 2020, marking a 99.81% increase. (2). RCF in Jianghan Plain evolved toward a more contiguous and clustered spatial pattern, suggesting a clear industrial agglomeration in this area. (3). The expansion of the RCFs was majorly influenced by its landscape and local agricultural conditions. Significantly, the Aggregation and Landscape Shape Indexes positively impacted this expansion, whereas proximity to rural areas and towns had a negative impact. This study provides a solid foundation for promoting the rice–crayfish co-culture system and sustainably developing related industries. To ensure the sustainable development of rice–crayfish co-culture industries in Jianghan Plain, we recommend that local governments optimize the spatial layout of rural settlements, improve transportation infrastructure, and enhance regional agricultural water sources and irrigation system construction, all in line with the national strategy of rural revitalization and village planning. Additionally, promoting the concentration and contiguity of RCF through land consolidation can achieve efficient development of these industries. Full article
Show Figures

Figure 1

Figure 1
<p>Location of the study area.</p>
Full article ">Figure 2
<p>Cultivation process of RCF system and lotus root.</p>
Full article ">Figure 3
<p>Flowchart of the extraction of RCF.</p>
Full article ">Figure 4
<p>Distribution of validation samples for RCF extraction results in Jianghan Plain: (<b>a</b>) samples from 2016; (<b>b</b>) samples from 2020.</p>
Full article ">Figure 5
<p>Spatial distribution of RCFs in Jianghan Plain in 2016 (<b>a</b>) and 2020 (<b>b</b>).</p>
Full article ">Figure 6
<p>Regional distribution and changes of RCF area in Jianghan Plain (2016–2020).</p>
Full article ">Figure 7
<p>Changes in the spatial distribution of RCF in Jianghan Plain from 2016 to 2020: (<b>a</b>) the loss of RCF; (<b>b</b>) the expansion of RCF.</p>
Full article ">Figure 8
<p>Spatial distribution and statistical probability density of landscape indices for RCFs in Jianghan Plain: (<b>a</b>) PD in 2016, (<b>b</b>) LSI in 2016, (<b>c</b>) AI in 2016, (<b>d</b>) PD in 2020, (<b>e</b>) LSI in 2020, (<b>f</b>) AI in 2020, (<b>g</b>) PD, (<b>h</b>) LSI and (<b>i</b>) AI.</p>
Full article ">Figure 9
<p>The LISA map of RCF in Jianghan Plain in 2016 (<b>a</b>) and 2020 (<b>b</b>).</p>
Full article ">Figure 10
<p>Spatial distribution of local R-Square for the MGWR model.</p>
Full article ">Figure 11
<p>Statistical distribution of the regression coefficients of influential factors.</p>
Full article ">Figure 12
<p>Spatial distribution of the regression coefficients of influential factors: (<b>a</b>) AI, (<b>b</b>) LSI, (<b>c</b>) PD, (<b>d</b>) DWS, (<b>e</b>) DCT, (<b>f</b>) DR, (<b>g</b>) DRS, and (<b>h</b>) PCL.</p>
Full article ">
14 pages, 2189 KiB  
Article
Adult Feeding Experience Determines the Fecundity and Preference of the Henosepilachna vigintioctopunctata (F.) (Coleoptera: Coccinellidae)
by Jingwei Qi, Xiangping Wang, Tingjia Zhang, Chuanren Li and Zailing Wang
Biology 2024, 13(4), 250; https://doi.org/10.3390/biology13040250 - 9 Apr 2024
Viewed by 1145
Abstract
Both larvae and adults of the Henosepilachna vigintioctopunctata feed on leaves of potatoes, tomatoes, and eggplants. Given the variation in planting times of host plants in the Jianghan Plain, host switching between larvae and adults of H. vigintioctopunctata is inevitable to ensure continuous [...] Read more.
Both larvae and adults of the Henosepilachna vigintioctopunctata feed on leaves of potatoes, tomatoes, and eggplants. Given the variation in planting times of host plants in the Jianghan Plain, host switching between larvae and adults of H. vigintioctopunctata is inevitable to ensure continuous food availability. We evaluated the effect of consistent versus diverse larval and adult host plant feeding experience on growth performance, fecundity, longevity, and feeding preferences of H. vigintioctopunctata through match-mismatch experiments. Host plant quality significantly influences larval development and adult reproduction. Potatoes are identified as the optimal host plant for H. vigintioctopunctata, whereas eggplants significantly negatively affect the adult fecundity. Adult stage host feeding experience determines the fecundity of H. vigintioctopunctata, irrespective of the larval feeding experience. The fecundity of H. vigintioctopunctata adults on eggplant leaves remains significantly lower than that observed on potato leaves. Similarly, adult H. vigintioctopunctata demonstrate a preference for consuming potato leaves, irrespective of the larval feeding experience. Although host switching between larval and adult stages offers lesser benefits for the performance of herbivorous insects compared to a consistent diet with potato leaves, it maintains H. vigintioctopunctata population continuity amidst shortages of high-quality potato hosts. Full article
Show Figures

Figure 1

Figure 1
<p>Each group, consisting of 300 <span class="html-italic">H. vigintioctopunctata</span> larvae, was raised on a different host plant leaf: potato, eggplant, or tomato, until all larvae reached pupation. Subsequently, we divided the emerging adults from the same host plants into three equal groups for match-mismatch experiments. <span class="html-italic">H. vigintioctopunctata</span> larvae were initially fed potato leaves, with one-third of the newly emerged adults subsequently fed potato leaves (Potato-Potato, PP), while the remaining two groups were fed egg-plant leaves (Potato-Eggplant, PE) and tomato leaves (Potato-Tomato, PT), respectively. Similarly, <span class="html-italic">H. vigintioctopunctata</span> larvae were initially fed on eggplant leaves, and then one-third of the newly emerged adults were fed eggplant (Eggplant-Eggplant, EE), potato (Eggplant-Potato, EP), and tomato (Eggplant-Tomato, ET) leaves, respectively. In a similar vein, larvae fed on tomato leaves, and then one-third of the newly emerged adults were fed tomato (Tomato-Tomato, TT), potato (Tomato-Potato, TP), and eggplant (Tomato-Eggplant, TE) leaves, respectively.</p>
Full article ">Figure 2
<p>The effects of host plants on pupal weight, length and width of <span class="html-italic">H. vigintioctopunctata</span>. “ns” indicates no significant difference in the pupal length of <span class="html-italic">H. vigintioctopunctata</span> when fed on tomato, eggplant, and potato. “*” means significant difference in the pupal weight and pupal width of <span class="html-italic">H. vigintioctopunctata</span> when fed on tomato, eggplant, and potato.</p>
Full article ">Figure 3
<p>The effect of larval and adult host plant experiences on the oviposition period (<b>A</b>) and fecundity (<b>B</b>) of <span class="html-italic">H. vigintioctopunctata</span> adults. Post-hoc analyses based on the GLMM were used to compare significant differences in the oviposition period and fecundity of <span class="html-italic">H. vigintioctopunctata</span> adults across different treatments. <span class="html-italic">H. vigintioctopunctata</span> were reared either continuously as larvae and adults on potato (PP), tomato (TT), or eggplant (EE), or as larvae on potato and then as adults on tomato (PT) and eggplant (PE), as larvae on tomato and then as adults on potato (TP) and eggplant (TE), or as larvae on eggplant and then as adults on potato (EP) and tomato (ET). The box plots display the mean with whiskers extending from the minimum to the maximum value.</p>
Full article ">Figure 4
<p>The selection ratio of <span class="html-italic">H. vigintioctopunctata</span> adults with different larval host experience. The upper x-axis represents the larval host feeding experience. Yellow, purple, green, and orange indicate the selection ratio for potato, tomato, eggplant, and nochoice within 24 h and 48 h, respectively. NoChoice indicates that the <span class="html-italic">H. vigintioctopunctata</span> adults were not found on the host plants but elsewhere.</p>
Full article ">Figure 5
<p>The weight consumed by <span class="html-italic">H. vigintioctopunctata</span> adult on different host plants in the preference experiment. * Indicates a significant difference at 0.05 level.</p>
Full article ">Figure 6
<p>The contents of water and nutrient components in the leaves of different host plants of <span class="html-italic">H. vigintioctopunctata</span>. The different lowercase letters indicate significant differences in water and nutritional content among potato, tomato, and eggplant. The presence of different lowercase letters on water and nutritional content indicates of potato significant differences. The y-axis on the left illustrates the water content across various host plants, whereas the right y-axis depicts the levels of crude fat, protein, carbohydrates, and total amino acids in these plants.</p>
Full article ">
26 pages, 49819 KiB  
Article
Comparison of Cloud-Mask Algorithms and Machine-Learning Methods Using Sentinel-2 Imagery for Mapping Paddy Rice in Jianghan Plain
by Xinyi Gao, Hong Chi, Jinliang Huang, Yifei Han, Yifan Li and Feng Ling
Remote Sens. 2024, 16(7), 1305; https://doi.org/10.3390/rs16071305 - 8 Apr 2024
Cited by 3 | Viewed by 1928
Abstract
Southern China, one of the traditional rice production bases, has experienced significant declines in the area of rice paddy since the beginning of this century. Monitoring the rice cropping area is becoming an urgent need for food security policy decisions. One of the [...] Read more.
Southern China, one of the traditional rice production bases, has experienced significant declines in the area of rice paddy since the beginning of this century. Monitoring the rice cropping area is becoming an urgent need for food security policy decisions. One of the main challenges for mapping rice in this area is the quantity of cloud-free observations that are vulnerable to frequent cloud cover. Another relevant issue that needs to be addressed is determining how to select the appropriate classifier for mapping paddy rice based on the cloud-masked observations. Therefore, this study was organized to quickly find a strategy for rice mapping by evaluating cloud-mask algorithms and machine-learning methods for Sentinel-2 imagery. Specifically, we compared four GEE-embedded cloud-mask algorithms (QA60, S2cloudless, CloudScore, and CDI (Cloud Displacement Index)) and analyzed the appropriateness of widely accepted machine-learning classifiers (random forest, support vector machine, classification and regression tree, gradient tree boost) for cloud-masked imagery. The S2cloudless algorithm had a clear edge over the other three algorithms based on its overall accuracy in evaluation and visual inspection. The findings showed that the algorithm with a combination of S2cloudless and random forest showed the best performance when comparing mapping results with field survey data, referenced rice maps, and statistical yearbooks. In general, the research highlighted the potential of using Sentinel-2 imagery to map paddy rice with multiple combinations of cloud-mask algorithms and machine-learning methods in a cloud-prone area, which has the potential to broaden our rice mapping strategies. Full article
Show Figures

Figure 1

Figure 1
<p>Overview map of the study area. The grids are Sentinel-2 footprints in MGRS (Military Grid Reference System) with an area of 100 km × 100 km square. Land cover data was from the optimal mapping results of this study.</p>
Full article ">Figure 2
<p>The workflow of the study included data preprocessing and cloud mask algorithm evaluation, sample selection and feature selection, extraction of rice phenology and image compositing, comparisons of machine-learning algorithms in rice mapping and validation of rice maps (validation of field data samples, comparison of 10 m rice maps, and comparison of statistical data).</p>
Full article ">Figure 3
<p>Paddy rice phenological stages derived from the fitted curves of five spectral indices based on the cloud-masked TOA dataset in 2021 (field photographs were taken at <math display="inline"><semantics> <mrow> <mn>112</mn> <mo>.</mo> <msup> <mn>8804</mn> <mo>∘</mo> </msup> </mrow> </semantics></math>E, <math display="inline"><semantics> <mrow> <mn>30</mn> <mo>.</mo> <msup> <mn>0690</mn> <mo>∘</mo> </msup> </mrow> </semantics></math>N).</p>
Full article ">Figure 4
<p>Results of four cloud-mask algorithms in the tile of 49REP, 49RFP, and 49RGP (the specific locations of these footprints in the study area are shown in <a href="#remotesensing-16-01305-f001" class="html-fig">Figure 1</a>). Each row shows the cloud identification results based on 49REP’s May 2018 TOA data, 49RFP’s July 2021 TOA data, and 49RGP’s September 2021 SR data using QA60, S2cloudless, CloudScore, and CDI cloud mask algorithms, respectively.</p>
Full article ">Figure 5
<p>Results of four cloud-mask algorithms in three subregions across the tiles of 49REP, 49RFP, and 49RGP with different land cover characteristics. Panels a, b, and c show the results in a region mixed with built-up area and paddy rice, a region mixed with dryland and paddy rice, and a region mixed with paddy rice and aquaculture area, respectively.</p>
Full article ">Figure 6
<p>J-M values of paddy rice and other land cover types to cloud-free datasets for different cloud-mask algorithms.</p>
Full article ">Figure 7
<p>Percentages of the specified land cover area to the total area in different land cover types were estimated from the different combinations of cloud-mask algorithms and machine-learning algorithms. The bars show the percentage in area of water body, built-up area, forest land, dryland, and paddy rice from left to right, respectively.</p>
Full article ">Figure 8
<p>J-sim values between the reference rice maps and the maps generated from different algorithm combinations.</p>
Full article ">Figure 9
<p>Comparisons of rice area between statistical data and mapping results.</p>
Full article ">Figure A1
<p>Rice distribution results based on 2018 TOA data.</p>
Full article ">Figure A2
<p>Rice distribution results based on 2021 TOA data.</p>
Full article ">Figure A3
<p>Rice distribution results based on 2021 SR data.</p>
Full article ">
14 pages, 6137 KiB  
Article
Assessing the Accuracy and Consistency of Cropland Products in the Middle Yangtze Plain
by Haixia Xu, Luguang Jiang and Ye Liu
Land 2024, 13(3), 301; https://doi.org/10.3390/land13030301 - 28 Feb 2024
Cited by 2 | Viewed by 1185
Abstract
With the evolution of remote sensing, more data products concerning cropland distribution are becoming available. However, the accuracy and consistency across all datasets in crucial regions are inherently uncertain. We delved into the Middle Yangtze Plain, a complex and vital agricultural area with [...] Read more.
With the evolution of remote sensing, more data products concerning cropland distribution are becoming available. However, the accuracy and consistency across all datasets in crucial regions are inherently uncertain. We delved into the Middle Yangtze Plain, a complex and vital agricultural area with relatively high cultivation intensities in China. We used confusion matrices and consistency analysis to compare the accuracy and consistency of four multi-year cropland distribution data products. These include Global Land Analysis & Discovery Cropland Data (GLAD), Annual Global Land Cover (AGLC), the China Land Cover Dataset (CLCD), and China’s Annual Cropland Dataset (CACD). Key findings include the following: GLAD has the highest precision at 96.09%, the CLCD has the highest recall at 98.41%, and AGLC and CACD perform well in achieving a balance between precision and recall, with F1 scores of 90.30% and 90.74%, respectively. In terms of consistency, GLAD and the CLCD show inconsistency at 69.58%. When all four products unanimously classify a pixel as cropland, the identified cropland area closely corresponds to the statistical data reported in the yearbook. The Jianghan Plain holds the majority of cropland in the Middle Yangtze Plain, constituting 50.88%. From 2003 to 2019, the cropland area experienced fluctuating and ascending trends. Shangrao City witnessed the most notable rise in cropland area, with an increase of 323.0 km2, whereas Wuhan City underwent the most substantial decline, amounting to 185.8 km². These findings contribute valuable insights into the precision and consistency of existing cropland distribution products, offering a foundation for further research. Full article
Show Figures

Figure 1

Figure 1
<p>The geographical and topographic characteristics of the study area (Projection: Krasovsky 1940 Albers; Geodetic System: WGS 84).</p>
Full article ">Figure 2
<p>The distribution of sample points.</p>
Full article ">Figure 3
<p>Consistency in cropland proportions across products (The blue points illustrate the percentage of cropland in small hexagons defined by the <span class="html-italic">x</span>-axis and <span class="html-italic">y</span>-axis. The black line represents the fitted regression line for these cropland percentage data points.).</p>
Full article ">Figure 4
<p>Consistency between GLAD and the CLCD (the distribution plot above and on the right illustrates the inconsistent area (in square kilometers) across longitude and latitude. Different colors represent varying slopes: blue corresponds to 0–2°, green to 2–6°, yellow to 6–15°, orange to 6–25°, and red to slopes greater than 25°).</p>
Full article ">Figure 5
<p>Comparison between different cropland scenarios and yearbook statistical data (The blue points represent the cropland area obtained by the <span class="html-italic">x</span>-axis and <span class="html-italic">y</span>-axis. The dotted line corresponds to the 1:1 relationship.).</p>
Full article ">Figure 6
<p>The changed area and proportion in counties and prefectures.</p>
Full article ">
23 pages, 6987 KiB  
Article
Moisture Migration and Recharge Pattern of Low-Permeability Thick Cohesive Soil in Northern Margin of the Jianghan Plain
by Tianwen Liu, Ningtao Wang, Cheng Hu, Qing Wang, Kun Huang, Zhihua Chen and Tingting Shi
Appl. Sci. 2023, 13(23), 12720; https://doi.org/10.3390/app132312720 - 27 Nov 2023
Cited by 1 | Viewed by 1193
Abstract
An extremely low hydraulic conductivity of cohesive soil causes a low transport rate of water and solute, with a time-consuming result, as we all know. Stable isotopes (δD and δ18O) and in situ monitoring systems of the data about soil water, [...] Read more.
An extremely low hydraulic conductivity of cohesive soil causes a low transport rate of water and solute, with a time-consuming result, as we all know. Stable isotopes (δD and δ18O) and in situ monitoring systems of the data about soil water, rainfall, and groundwater were used to analyze the soil moisture migration pattern, using a conceptual model in the field test site, simulated by Hydrus 1D. The results show that multiple rainfalls’ accumulations can cause the water to recharge from soil moisture to micro-confined groundwater, gradually. The soil moisture dynamic change is composed of a dehydration period and absorption period; the cohesive soil water content below 5.0 m was affected by the micro-confined groundwater level and dehydrated in advance due to the level decline. The thick cohesive soil profile can be divided into a shallow mixing zone (0–2 m), steady zone (2–5 m), and deep mixing zone (5–15 m). The effective precipitation recharge was 234 mm and the average infiltration recharge coefficient (Rc) was 0.1389, but the water exchange between the cohesive soil moisture and groundwater was 349 mm in two hydrological years. This paper reveals the moisture migration and recharge pattern of low-permeability thick cohesive soil in a humid area with a micro-confined groundwater aquifer; this is of great significance for groundwater resources evaluation and environmental protection in humid climate plain areas. Full article
(This article belongs to the Special Issue State-of-the-Art Earth Sciences and Geography in China)
Show Figures

Figure 1

Figure 1
<p>Monitoring and data collection systems of the field test site. The number “①–⑧” in the north-eastern part of this figure are the numbers of horizontal holes for instrument installation. The CS257 and CS650 probes were installed inside holes “⑤–⑥” at the east direction of WELL 3.</p>
Full article ">Figure 2
<p>(<b>a</b>) The dynamic changes in rainfall, groundwater level, and soil volume water content of monitoring layers in profile 3E; (<b>b</b>) the dynamic changes in rainfall, groundwater level, and soil total water potential of monitoring layers in profile 3E.</p>
Full article ">Figure 3
<p>The dynamic change diagram of rainfall, soil volume water content, and capillary zone roof elevation in profile 3E. Light blue dashed line and light orange dashed line represent the soil layer elevations at the depths of 6.0 m and 5.0 m.</p>
Full article ">Figure 4
<p>Transition times of soil water at monitoring layers and groundwater response times to rain in the field test site. The vertical dashed line in color referring to the soil volume water content dynamic data of the cohesive soil layer stands for the water absorption period and dehydration period transition time of this layer, whereas the vertical solid line stands for the dehydration period and water absorption period transition time. GWL stands for groundwater level.</p>
Full article ">Figure 5
<p>Soil volume water content and total water potential of thick cohesive layers are shown in the test site from January to July 2020. The left side is the soil water volume content’s dynamic change in monitoring layers on the 15th of each month from January to July 2020, and the right side is the total water potential.</p>
Full article ">Figure 6
<p>Vertical variations of stable isotope values (δD, δ<sup>18</sup>O) and soil volume water content in the test site on 5 July 2020. The red dashed lines are dividing lines of different zones.</p>
Full article ">Figure 7
<p>Conceptual model of vertical movement of cohesive soil water in the field test site (modified from Yuan et al., 2012). The blue dashed line stands for the micro-confined groundwater level with certain fluctuations within 530 cm. The deeper the blue color is, the higher was the soil moisture saturation of this layer in the profile. The red dashed line stands for the elevation of the capillary saturation roof with certain fluctuations caused by groundwater level changes.</p>
Full article ">Figure 8
<p>Vertical hydrogeological conceptual model of the field test site.</p>
Full article ">Figure 9
<p>Comparison between observed field measurements and simulation result of 4 critical layers in 3 mass balance zones.</p>
Full article ">Figure 10
<p>Water migration simulation results of critical depths of mass balance zones.</p>
Full article ">
Back to TopTop