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12 pages, 5339 KiB  
Article
Enhance the Surface Insulation Properties of EP Materials via Plasma and Fluorine-Containing Coupling Agent Co-Fluorinated Graphene
by Manling Dong, Zhifei Yang, Guowei Xia, Jiatao Zhang, Zhenyu Zhan, Weifeng Xin, Qilin Wang, Bobin Xu, Yujin Zhang and Jun Xie
Nanomaterials 2024, 14(24), 2009; https://doi.org/10.3390/nano14242009 (registering DOI) - 14 Dec 2024
Viewed by 146
Abstract
Epoxy resin (EP) is an outstanding polymer material known for its low cost, ease of preparation, excellent electrical insulation properties, mechanical strength, and chemical stability. It is widely used in high- and ultra-high-voltage power transmission and transformation equipment. However, as voltage levels continue [...] Read more.
Epoxy resin (EP) is an outstanding polymer material known for its low cost, ease of preparation, excellent electrical insulation properties, mechanical strength, and chemical stability. It is widely used in high- and ultra-high-voltage power transmission and transformation equipment. However, as voltage levels continue to increase, EP materials are gradually failing to meet the performance demands of operational environments. Thus, the development of high-performance epoxy resin materials has become crucial. In this study, a combined treatment using plasma and a fluorine-containing coupling agent was employed to fluorinate graphene nanosheets (GNSs), resulting in DFGNSs. Different concentrations of GNSs/DFGNS-modified EP composites were prepared, and their effects on enhancing the surface insulation properties were studied. Tests on surface flashover voltage, surface charge dissipation, trap distribution, and surface resistivity demonstrated that both GNSs and DFGNSs significantly improve the insulation properties of EP materials. Optimal improvement was achieved with a DFGNS content of 0.2 wt%, where the flashover voltage increased by 16.23%. Full article
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Figure 1

Figure 1
<p>The GN ball milling treatment and GNSs fluorination treatment platform. (<b>a</b>) Graphene ball milling pretreatment process; (<b>b</b>) Co-fluorination process.</p>
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<p>The SEM test results. (<b>a</b>) GN; (<b>b</b>) GNSs; (<b>c</b>) DFGNSs.</p>
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<p>The FTIR results of GNSs before and after fluoridation.</p>
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<p>The XPS full spectrum and C1s partial peak spectrum. (<b>a</b>) GNSs full spectrum; (<b>b</b>) DFGNSs full spectrum; (<b>c</b>) C1s partial peak of GNSs; (<b>d</b>) C1s partial peak of DFGNSs.</p>
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<p>The flashover voltage test results of EP composites.</p>
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<p>The surface resistivity test results of EP composites.</p>
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<p>The surface charge dissipation curve of EP composites. (<b>a</b>) GNSs/EP; (<b>b</b>) DFGNSs/EP.</p>
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<p>The trap distribution characteristics of EP composites. (<b>a</b>) GNSs/EP; (<b>b</b>) DFGNSs/EP.</p>
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<p>The surface potential test results. (<b>a</b>) Pure EP; (<b>b</b>) 0.1% GNSs/EP; (<b>c</b>) 0.2% GNSs/EP; (<b>d</b>) 0.3% GNSs/EP; (<b>e</b>) 0.4% GNSs/EP; (<b>f</b>) 0.5% GNSs/EP; (<b>g</b>) 0.6% GNSs/EP; (<b>h</b>) 0.1% DFGNSs/EP; (<b>i</b>) 0.2% DFGNSs/EP; (<b>j</b>) 0.3% DFGNSs/EP; (<b>k</b>) 0.4% DFGNSs/EP; (<b>l</b>) 0.5% DFGNSs/EP; (<b>m</b>) 0.6% DFGNSs/EP.</p>
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<p>Schematic diagram of enhancement mechanism.</p>
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15 pages, 5693 KiB  
Article
Thermomigration Microstructure and Properties of Ni Nanoparticle-Reinforced Sn58Bi Composite Solder/Cu Solder Joint
by Yuchun Fan, Keke Zhang, Weiming Chen, Jinna Wu and Yonglei Wang
Metals 2024, 14(12), 1420; https://doi.org/10.3390/met14121420 - 11 Dec 2024
Viewed by 315
Abstract
A Sn58Bi composite solder reinforced by Ni nanoparticles was prepared using a mechanical mixing technique, and the thermomigration microstructure and properties of the solder joints were studied. The findings indicate that incorporating an appropriate quantity of Ni nanoparticles can enhance the microstructure of [...] Read more.
A Sn58Bi composite solder reinforced by Ni nanoparticles was prepared using a mechanical mixing technique, and the thermomigration microstructure and properties of the solder joints were studied. The findings indicate that incorporating an appropriate quantity of Ni nanoparticles can enhance the microstructure of the composite solder and mitigate the coarsening of Bi-phase segregation. At 0.75 weight percent Ni nanoparticle content, the composite solder’s tensile strength is 59.7 MPa and its elongation is 54.6%, both of which are noticeably greater than those of the base solder. When the thermal loading time is 576 h, the shear strength of the composite solder joint is 25.5 MPa, which is 30.1% higher than that of the base solder joint. This study reveals that the shear fracture path shifts from the boundary region between the solder seam and the IMC layer to the IMC layer itself. Concurrently, the fracture mode evolves from a mix of brittle–ductile fracture, characterized by quasi-cleavage, to a predominantly brittle fracture, marked by numerous “rock candy-like” cross-sectional features and secondary cracking. Adding Ni nanoparticles to the Sn58Bi composite solder/Cu solder junction can significantly extend its service life. Full article
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Figure 1
<p>Schematic diagram of composite solder preparation process.</p>
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<p>Size and shape of the samples (mm). (<b>a</b>) Base metal; (<b>b</b>) brazed sample.</p>
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<p>Thermomigration device and schematic diagram.</p>
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<p>Simulation of the temperature field distribution of the solder joint heated to a steady-state at an average temperature of 85 °C. (<b>a</b>) Temperature field at 1300 °C/cm; (<b>b</b>) temperature distribution curves from the hot end to the cold end at 1300 °C/cm.</p>
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<p>Microstructure of Sn58Bi-<span class="html-italic">x</span>Ni composite solder (<b>a</b>) 0.0 wt.%; (<b>b</b>) 0.25 wt.%; (<b>c</b>) 0.5 wt.%; (<b>d</b>) 0.75 wt.%; (<b>e</b>) 1 wt.%.</p>
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<p>Properties of composite solder. (<b>a</b>) Physical properties and wettability; (<b>b</b>) mechanical properties.</p>
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<p>Tensile fracture morphology of composite solder. (<b>a</b>) 0.0 wt.%; (<b>b</b>) 0.25 wt.%; (<b>c</b>) 0.5 wt.%; (<b>d</b>) 0.75 wt.%; (<b>e</b>) 1 wt.%.</p>
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<p>Microstructure of Sn58Bi-<span class="html-italic">x</span>Ni composite solder/Cu solder joints. (<b>a</b>) 0.0 wt.%; (<b>b</b>) <a href="#metals-14-01420-f008" class="html-fig">Figure 8</a>a XRD pattern; (<b>c</b>) 0.75 wt.%; (<b>d</b>) <a href="#metals-14-01420-f008" class="html-fig">Figure 8</a>c line scan EDS.</p>
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<p>IMC microstructure of Sn58Bi-0.75Ni/Cu solder joint thermomigration interface: (<b>a</b>) hot end (72 h); (<b>b</b>) hot end (144 h); (<b>c</b>) hot end (288 h); (<b>d</b>) hot end (576 h); (<b>e</b>) cold end (72 h); (<b>f</b>) cold end (144 h); (<b>g</b>) cold end (288 h); (<b>h</b>) cold end (576 h).</p>
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<p>Average IMC thickness of solder joints under thermal loading. (<b>a</b>) cold end; (<b>b</b>) hot end.</p>
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<p>Logarithmic relationship between the thickness of IMC and time during the thermomigration process of Sn58Bi-0.75Ni/Cu solder joints at 1300 °C/cm.</p>
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<p>Square root relationship between IMC layer thickness and thermal loading time. (<b>a</b>) cold end; (<b>b</b>) hot end.</p>
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<p>Solder joint shear strength under thermal loading.</p>
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<p>Shear fracture morphology of solder joints under thermal loading. (<b>a</b>) 0 h; (<b>b</b>) 144 h; (<b>c</b>) 576 h.</p>
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20 pages, 8137 KiB  
Article
A Simple and Rapid “Turn-On” Fluorescent Probe Based on Binuclear Schiff Base for Zn2+ and Its Application in Cell Imaging and Test Strips
by Jinghui Cheng, Yi Li, Zhiye Zhu, Huijuan Guan, Jinsong Zhai, Yibing Xiang and Man Wang
Molecules 2024, 29(24), 5850; https://doi.org/10.3390/molecules29245850 - 11 Dec 2024
Viewed by 305
Abstract
A series of colorful binuclear Schiff bases derived from the different diamine bridges including 1,2- ethylenediamine (bis-Et-SA, bis-Et-4-NEt2, bis-Et-5-NO2, bis-Et-Naph), 1,2-phenylenediamine (bis-Ph-SA, bis-Ph-4-NEt2, bis-Ph-5-NO2, bis-Ph-Naph), dicyano-1,2-ethenediamine (bis-CN-SA, bis-CN-4-NEt2, bis-CN-5-NO2, bis-CN-Naph) have [...] Read more.
A series of colorful binuclear Schiff bases derived from the different diamine bridges including 1,2- ethylenediamine (bis-Et-SA, bis-Et-4-NEt2, bis-Et-5-NO2, bis-Et-Naph), 1,2-phenylenediamine (bis-Ph-SA, bis-Ph-4-NEt2, bis-Ph-5-NO2, bis-Ph-Naph), dicyano-1,2-ethenediamine (bis-CN-SA, bis-CN-4-NEt2, bis-CN-5-NO2, bis-CN-Naph) have been designed and prepared. The optical properties of these binuclear Schiff base ligands were fully determined by UV–Vis absorption spectroscopy, fluorescence emission spectroscopy, and time-dependent-density functional theory (TD-DFT) calculations. The inclusion of D-A systems and/or π-extended systems in these binuclear Schiff base ligands not only enables adjustable RGB light absorption and emission spectra (300~700 nm) but also yields high fluorescence quantum efficiencies of up to 0.84 in MeCN solution. Then, with the ESIPT (excited-state intramolecular proton transfer) property, fluorescence analysis showed that the probe bis-Et-SA and bis-Ph-SA could recognize Zn2+ via the “turn on” mode in the MeCN solution. During the detection process, bis-Et-SA and bis-Ph-SA demonstrate rapid response and high selectivity upon the addition of Zn2+. The coordination of Zn2+ with the oxygen atom and Schiff base nitrogen atom in a tetrahedral geometry is confirmed by Job’s plot, FT-IR, and 1H NMR spectroscopy. In addition, the paper test and Hela cells were successfully carried out to detect Zn2+. Moreover, the sensitivity of bis-Et-SA and bis-Ph-SA is much better than that of those Schiff base ligands containing only one chelating unit [O^N^N^O]. Full article
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Figure 1
<p>Normalized absorption spectra of the bis-Schiff ligands with the same bridges and different diethylamino-phenol in MeCN.</p>
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<p>Normalized UV–Vis absorption spectra of the bis-Schiff ligands with the same diethylamino-phenol different bridges in MeCN.</p>
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<p>Images captured of the chosen binuclear Schiff base ligands in MeCN at ambient temperature. (Top: under natural sunlight; bottom: under 360 nm UV light).</p>
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<p>Normalized emission spectra were obtained for bis-Schiff ligands featuring the same bridges but varying diethylamino-phenol substituents in MeCN solvent.</p>
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<p>Normalized emission spectra were obtained for bis-Schiff ligands featuring various bridges and a consistent di-ethylamino-phenol in MeCN.</p>
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<p>Frontier molecular orbitals for the bis-Schiff ligands with the different diethylamino-phenol and same bridges in MeCN at B3LYP 6-31G(d,p) level of theory.</p>
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<p>Frontier molecular orbitals for the bis-Schiff ligands with different bridges and the same diethylamino-phenol in MeCN at B3LYP 6-31G(d,p) level of theory.</p>
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<p>The UV–Vis absorption spectra of bis-Et-SA (1.0 × 10<sup>−5</sup> mol dm<sup>−3</sup> in MeCN) were observed upon the addition of 2 equiv. of different metal ions.</p>
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<p>The UV–Vis absorption spectra of bis-Ph-SA (1.0 × 10<sup>−5</sup> mol dm<sup>−3</sup> in MeCN) were observed upon the addition of 2 equiv. of different metal ions.</p>
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<p>The emission spectra of bis-Et-SA (1.0 × 10<sup>−5</sup> mol dm<sup>−3</sup> in MeCN, excited at 360 nm) upon the addition of 2 equiv. of different metal ions.</p>
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<p>The emission spectra of bis-Ph-SA (1.0 × 10<sup>−5</sup> mol dm<sup>−3</sup> in MeCN, excited at 340 nm) were observed upon the addition of 2 equiv of various metal ions.</p>
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<p>The selectivity of bis-Et-SA (1.0 × 10<sup>−5</sup> mol dm<sup>−3</sup> in MeCN, with emission measured at 450 nm and excited at 360 nm) towards 2.0 equiv. of other metal ions, and Zn<sup>2+</sup> was investigated.</p>
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<p>Selectivity of bis-Ph-SA (1.0 × 10<sup>−5</sup> mol dm<sup>−3</sup> in MeCN, emission measured at 405 nm and excited at 340 nm) toward 2.0 equiv. of other metal ions and Zn<sup>2+</sup>.</p>
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<p>Plot of (I − I0)/I (emission at 450 nm) as a function of Zn<sup>2+</sup> concentration based on bis-Et-SA (1.0 × 10<sup>−5</sup> mol dm<sup>−3</sup> in MeCN).</p>
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<p>Plot of emission intensity at 405 nm as a function of Zn<sup>2+</sup> concentration based on bis-Ph-SA (1.0 × 10<sup>−5</sup> mol dm<sup>−3</sup> in MeCN).</p>
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<p>Job’s plot of bis-Et-SA and Zn<sup>2+</sup> in CH<sub>3</sub>CN solution. The total concentration of bis-Et-SA and Zn<sup>2+</sup> was 10 μM. The emission intensity at 450 nm.</p>
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<p>Job’s plot of bis-Ph-SA and Zn<sup>2+</sup> in CH<sub>3</sub>CN solution. The total concentration of bis-Ph-SA and Zn<sup>2+</sup> was 10 μM. The emission intensity at 405 nm.</p>
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<p>The fraction <sup>1</sup>HNMR spectroscopy of bis-Et-SA and bis-Et-SA+Zn<sup>2+</sup> in DMSO-d<sub>6</sub>.</p>
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<p>The IR spectra of bis-Et-SA and bis-Et-SA+Zn<sup>2+</sup>.</p>
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<p>Energy level diagram for the frontier molecular orbitals of bis-Et-SA (<b>left</b>) and its zinc complex (<b>right</b>) calculated by using the B3LYP/6–31G basis set.</p>
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<p>The proposed binding mechanism of bis-Et-SA with Zn<sup>2+</sup>.</p>
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<p>Fluorescent images were captured of Hela cells. (1) Bis-Ph-SA (30 μM) was added to the culture medium and incubated with Hela cells for 40 min. (2) Prior to treatment, Hela cells were exposed to bis-Ph-SA (30 μM) for 40 min, followed by an additional 40 min incubation with Zn<sup>2+</sup> ions (60 μM).</p>
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<p>The cytotoxicity test of bis-Ph-SA.</p>
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<p>Pictures of bis-Et-SA and bis-Ph-SA test strips treated with Zn<sup>2+</sup>. The photographs were captured upon exposure to 360 nm UV light.</p>
Full article ">Scheme 1
<p>The synthetic route and chemical structures of binuclear Schiff base ligands in this work.</p>
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20 pages, 2598 KiB  
Article
Spatiotemporal Evolution and Influencing Factors of New-Quality Productivity
by Nan Feng, Mingyue Yan and Mingtao Yan
Sustainability 2024, 16(24), 10852; https://doi.org/10.3390/su162410852 - 11 Dec 2024
Viewed by 325
Abstract
New-quality productivity (NQP) serves as a critical indicator for measuring the level of high-quality economic development. Gaining insights into the spatial and temporal patterns along with the key drivers of NQP is essential for promoting the global industrial transformation and revitalizing old cities. [...] Read more.
New-quality productivity (NQP) serves as a critical indicator for measuring the level of high-quality economic development. Gaining insights into the spatial and temporal patterns along with the key drivers of NQP is essential for promoting the global industrial transformation and revitalizing old cities. This study utilized spatial analysis, Dagum Gini coefficient, Markov chains, and optimal parameter geographical detectors to analyze spatial patterns and influencing factors of NQP across 271 Chinese prefecture-level cities from 2011 to 2021. Findings reveal that the average index of NQP increased from 0.045 in 2011 to 0.072 in 2021, with spatial patterns showing higher levels in coastal regions compared to inland areas. The overall disparity of NQP has diminished, although significant internal imbalances persist, particularly in the eastern region, where the pronounced gap between eastern and central areas remains the primary source of variation. Local NQP development is strongly influenced by proximity to adjacent areas, characterized by path dependence and club convergence effects. Additionally, cultural foundation, urbanization, and economic development play pivotal roles in fostering NQP, with their interactions exhibiting notable nonlinear and dual-factor enhancement effects. These findings provide valuable theoretical and practical insights for advancing NQP levels in China and globally. Full article
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<p>Theoretical framework for the NQP indicator system.</p>
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<p>NQP levels in Chinese cities from 2011 to 2021. (<b>a</b>) 2011; (<b>b</b>) 2021.</p>
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<p>Evolutionary characteristics of spatial clustering in NQP from 2011 to 2021. (<b>a</b>) 2011; (<b>b</b>) 2021.</p>
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<p>The detection of factors and interactions influencing NQP from 2011 to 2021. (<b>a</b>) Factor detection; (<b>b</b>) interaction detection.</p>
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15 pages, 16510 KiB  
Article
Mosaicking and Correction Method of Gaofen-3 ScanSAR Images in Coastal Areas with Subswath Overlap Range Constraints
by Jiajun Wang, Guowang Jin, Xin Xiong, Jiahao Li, Hao Ye and He Yang
J. Mar. Sci. Eng. 2024, 12(12), 2277; https://doi.org/10.3390/jmse12122277 - 11 Dec 2024
Viewed by 286
Abstract
The ScanSAR mode image obtained by the Gaofen-3 (GF-3) satellite has an imaging width of up to 130–500 km, which is of great significance in monitoring oceanography, meteorology, water conservancy, and transportation. To address the issues of subswath misalignment and the inability to [...] Read more.
The ScanSAR mode image obtained by the Gaofen-3 (GF-3) satellite has an imaging width of up to 130–500 km, which is of great significance in monitoring oceanography, meteorology, water conservancy, and transportation. To address the issues of subswath misalignment and the inability to correct in the processing of GF-3 ScanSAR images in coastal areas using software such as PIE, ENVI, and SNAP, a method for mosaicking and correcting GF-3 ScanSAR images with subswaths that overlap within specified range constraints is proposed. This method involves correlating the coefficients of each subswath thumbnail image in order to determine the extent of the overlap range. Given that the matching points are constrained to the overlap between subswaths, the normalized cross-correlation (NCC) matching algorithm is utilized to calculate the matching points between subswaths. Subsequently, the random sampling consistency (RANSAC) algorithm is employed to eliminate the mismatching points. Subsequently, the subswaths should be mosaicked together with the stitching translation of subswaths, based on the coordinates of the matching points. The image brightness correction coefficient is calculated based on the average grayscale value of pixels in the overlapping region. This is performed in order to correct the grayscale values of adjacent subswaths and thereby reducing the brightness difference at the junction of subswaths. The entire ScanSAR slant range image is produced. By employing the Range–Doppler model for indirect orthorectification, corrected images with geographic information are generated. The experiment utilized three coastal GF-3 ScanSAR images for mosaicking and correction, and the results were contrasted with those attained through PIE software V7.0 processing. This was conducted to substantiate the efficacy and precision of the methodology for mosaicking and correcting coastal GF-3 ScanSAR images. Full article
(This article belongs to the Special Issue Ocean Observations)
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Figure 1
<p>Workflow of this study.</p>
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<p>Mapping relationship between image-matching windows.</p>
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<p>Mosaic relationship between subswaths.</p>
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<p>Distribution diagrams of image connection points obtained by the method presented in this paper: (<b>a</b>) the distribution diagram of image connection points in image 1; (<b>b</b>) the distribution diagram of image connection points in image 2; (<b>c</b>) the distribution diagram of image connection points in image 3.</p>
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<p>Distribution diagrams of wrong image connection points obtained by the method presented in study [<a href="#B17-jmse-12-02277" class="html-bibr">17</a>]: (<b>a</b>) the distribution diagram of image connection points in image 1; (<b>b</b>) the distribution diagram of image connection points in image 2; (<b>c</b>) the distribution diagram of image connection points in image 3.</p>
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<p>The result of PIE software processing of the mosaicking dislocation: (<b>a</b>) mosaic misalignment in image 1; (<b>b</b>) mosaic misalignment in image 1; (<b>c</b>) mosaic misalignment in image 2; (<b>d</b>) mosaic misalignment in image 2; (<b>e</b>) mosaic misalignment in image 2; (<b>f</b>) mosaic misalignment in image 3.</p>
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<p>Area 1 image-mosaicking results: (<b>a</b>) the results of the method presented in this paper before brightness correction; (<b>b</b>) the results of the method presented in this paper after brightness correction; (<b>c</b>) the results of PIE software, and the differences in image widths are caused by its mosaicking errors; (<b>d</b>) the results of the method presented in study [<a href="#B17-jmse-12-02277" class="html-bibr">17</a>], and the differences in image widths are caused by its mosaicking errors.</p>
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<p>Area 2 image-mosaicking results: (<b>a</b>) the results of the method presented in this paper before brightness correction; (<b>b</b>) the results of the method presented in this paper after brightness correction; (<b>c</b>) the results of PIE software, and the differences in image widths are caused by its mosaicking errors; (<b>d</b>) the results of the method presented in study [<a href="#B17-jmse-12-02277" class="html-bibr">17</a>], and the differences in image widths are caused by its mosaicking errors.</p>
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<p>Area 3 image-mosaicking results: (<b>a</b>) the results of the method presented in this paper before brightness correction; (<b>b</b>) the results of the method presented in this paper after brightness correction; (<b>c</b>) the results of PIE software, and the differences in image widths are caused by its mosaicking errors; (<b>d</b>) the results of the method presented in study [<a href="#B17-jmse-12-02277" class="html-bibr">17</a>], and the differences in image widths are caused by its mosaicking errors.</p>
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<p>Image correction results of the method presented in this paper: (<b>a</b>) image 1 correction result; (<b>b</b>) image 2 correction result; (<b>c</b>) image 3 correction result.</p>
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<p>The corrected subswath image obtained by the RPC correcting.</p>
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<p>Result with incorrect rotations.</p>
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19 pages, 324 KiB  
Review
A Review on Remediation Technology and the Remediation Evaluation of Heavy Metal-Contaminated Soils
by Lei Xu, Feifei Zhao, Xiangyu Xing, Jianbiao Peng, Jiaming Wang, Mingfei Ji and B. Larry Li
Toxics 2024, 12(12), 897; https://doi.org/10.3390/toxics12120897 - 10 Dec 2024
Viewed by 699
Abstract
With the rapid development of industry and agriculture, soil contamination has become a significant environmental issue, and the heavy metal contamination of soils is an important part of it. The main methods for the remediation of heavy metal-contaminated soils include physical methods, chemical [...] Read more.
With the rapid development of industry and agriculture, soil contamination has become a significant environmental issue, and the heavy metal contamination of soils is an important part of it. The main methods for the remediation of heavy metal-contaminated soils include physical methods, chemical methods, biological methods, and combined remediation methods have been proposed as research deepens. However, the standards and evaluation methods for the remediation of heavy metal-contaminated soils are still not well-established. This article discusses the sources and contamination status of heavy metals in soils, the advantages and disadvantages of remediation technology for heavy metal-contaminated soils, remediation standards, and post-remediation evaluation methods. It also proposes scientific issues to be addressed in future research and provides an outlook on future development, hoping to assist in subsequent remediation studies of heavy metal-contaminated soils. Full article
16 pages, 9484 KiB  
Article
Variability of Interpolation Errors and Mutual Enhancement of Different Interpolation Methods
by Yunxia He, Mingliang Luo, Hui Yang, Leichao Bai and Zhongsheng Chen
Appl. Sci. 2024, 14(24), 11493; https://doi.org/10.3390/app142411493 - 10 Dec 2024
Viewed by 331
Abstract
Data interpolation methods are important statistical analysis tools that can fill in data gaps and missing areas by predicting and estimating unknown data points, thereby improving the accuracy and credibility of data analysis and research. Different interpolation methods are widely used in related [...] Read more.
Data interpolation methods are important statistical analysis tools that can fill in data gaps and missing areas by predicting and estimating unknown data points, thereby improving the accuracy and credibility of data analysis and research. Different interpolation methods are widely used in related fields, but the error between different interpolation methods and their interpolation fusion optimization have a significant impact on the interpolation accuracy, which still deserves further exploration. This study is based on two different types of point data: PM2.5 (PM2.5 refers to particulate matter in the atmosphere with a diameter of 2.5 μm or less, also known as inhalable particles or fine particulate matter) in Xinyang City, Henan Province, and the elevation of typical gullies in Yuanmou County, Yunnan Province. Using relative difference coefficients and hotspot analysis methods, the differences in error characteristics among four interpolation methods, ordinary kriging (OK), universal kriging (UK), inverse distance weighted (IDW), and radial basis functions (RBFs), were compared, and the influence of interpolation fusion methods on the accuracy of interpolation results was explored. The results show that after interpolation of PM2.5 concentration and gully elevation, the error difference between OK and UK is the smallest in both datasets. For PM2.5 concentration data, IDW and UK interpolation errors have the largest difference; for elevation data, the differences between RBF and UK interpolation are the largest. The weighted fusion results show that the interpolation error accuracy of PM2.5 concentration data with an interpolation point density of 0.009 points per square kilometer is improved, and the root mean square error (RMSE) after fusion is reduced from 0.374 μg/m3 to 0.004 μg/m3. However, the error accuracy of the elevation data of the gully with an interpolation point density of 0.76 points/m2 did not improve significantly. This indicates that characteristics such as the density of the original data are important factors that affect the accuracy of interpolation. In the case of sparse interpolation points, it is possible to consider fusing the interpolation results with different error patterns to improve their accuracy. This study provides a new idea for improving the accuracy of interpolation errors. Full article
(This article belongs to the Section Earth Sciences)
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Figure 1
<p>Distribution of PM<sub>2.5</sub> in Xinyang City.</p>
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<p>Histogram of PM<sub>2.5</sub>.</p>
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<p>Elevation data of Shadi Village in Yuanmou County.</p>
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<p>Histogram of elevation data.</p>
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<p>Similarity in interpolation error results: (<b>a</b>) is the PM<sub>2.5</sub> concentration and (<b>b</b>) is the elevation data.</p>
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<p>PM<sub>2.5</sub> error hotspot distribution by the four methods.</p>
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<p>Hotspot distribution of elevation errors of the four methods.</p>
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20 pages, 12892 KiB  
Article
Understanding Agricultural Water Consumption Trends in Henan Province: A Spatio-Temporal and Determinant Analysis Using Geospatial Models
by Yanbin Li, Yuhang Han, Hongxing Li and Kai Feng
Agriculture 2024, 14(12), 2253; https://doi.org/10.3390/agriculture14122253 - 9 Dec 2024
Viewed by 446
Abstract
In the context of water scarcity, understanding the mechanisms influencing and altering agricultural water consumption can offer valuable insights into the scientific management of limited water resources. Using Henan Province as a case study, this research applies the Mann–Kendall test method, the spatial [...] Read more.
In the context of water scarcity, understanding the mechanisms influencing and altering agricultural water consumption can offer valuable insights into the scientific management of limited water resources. Using Henan Province as a case study, this research applies the Mann–Kendall test method, the spatial Markov transfer chain model, the optimal parameter geo-detector model, and the Logarithmic Mean Divisia Index (LMDI) decomposition method to investigate the evolution characteristics of agricultural water consumption in Henan Province and its key influencing factors. The findings revealed the following: (1) Agricultural water consumption has shown a significant decline from 1999 to 2022. (2) According to observations, the stability of agricultural water consumption exceeds the spillover effect, and cross-border grade transfer is challenging. Moreover, this phenomenon is influenced by the neighboring regions. (3) The key influencing factors of added agricultural value are the sown area of food crops, total sown area, irrigated area, and average annual air temperature. (4) Among the decomposition effects on agricultural water consumption, the contribution of each decomposition effect to changes in agricultural water consumption and the role of spatial distribution exhibit notable differences. Overall, these findings provide theoretical references for the efficient use of agricultural water resources and sustainable development in the region. Full article
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<p>Geographic location of Henan Province.</p>
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<p>Spatial distribution of agricultural water consumption by Mann–Kendall test.</p>
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<p><math display="inline"><semantics> <mrow> <mi>q</mi> </mrow> </semantics></math>-value results for each index.</p>
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<p>Key impact factor interactive detection results.</p>
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<p>Spatial distribution map of the direction of action of each decomposition variable of agricultural water consumption in Henan Province. (<b>a</b>) Agrometeorological stress effects; (<b>b</b>) Agrometeorological economic effects; (<b>c</b>) Scale effects in agricultural development; (<b>d</b>) Agricultural irrigation capacity effects; (<b>e</b>) Agricultural cropping structure effects; (<b>f</b>) Agricultural food security effects.</p>
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<p>Spatial distribution map of the contribution of each decomposition variable of agricultural water consumption in Henan Province. (<b>a</b>) Agrometeorological stress effects; (<b>b</b>) Agrometeorological economic effects; (<b>c</b>) Scale effects in agricultural development; (<b>d</b>) Agricultural irrigation capacity effects; (<b>e</b>) Agricultural cropping structure effects; (<b>f</b>) Agricultural food security effects.</p>
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14 pages, 3451 KiB  
Article
Multiple Nitrogen Sources Application Inhibits Increasing Ammonia Volatilization Under Reducing Irrigation
by Taotao Chen, Erping Cui, Ke Sun, Chao Hu, Siyi Li, Ping Li, Zhijuan Zhao, Chuncheng Liu, Bingjian Cui and Xiangyang Fan
Agronomy 2024, 14(12), 2927; https://doi.org/10.3390/agronomy14122927 - 8 Dec 2024
Viewed by 334
Abstract
Farmland ammonia (NH3) volatilization is an important source of NH3, and the application of chemical fertilizer nitrogen (N) is the main factor affecting NH3 volatilization. The optimal substitution of chemical fertilizer with organic manure and straw reportedly reduces [...] Read more.
Farmland ammonia (NH3) volatilization is an important source of NH3, and the application of chemical fertilizer nitrogen (N) is the main factor affecting NH3 volatilization. The optimal substitution of chemical fertilizer with organic manure and straw reportedly reduces NH3 volatilization, while reducing irrigation increases NH3 volatilization. However, the combined effect of nitrogen fertilizer substitution and reducing irrigation on NH3 volatilization and the role of microorganisms in this process remains unclear. In a soil column experiment, NH3 volatilization and microbial composition were measured under both multiple N sources and different irrigation levels by the vented-chamber method and metagenomic sequencing. The results revealed that multiple N sources application reduced cumulative NH3 volatilization by 16.5–75.4% compared to single chemical fertilizer application, and the decreasing trend of NH3 volatilization under reduced irrigation conditions was greater. Microorganisms had a more important effect on NH3 volatilization of reduced irrigation than conventional irrigation. The abundance of nirA, arcC, E3.5.1.49, and E3.5.5.1 (ammonia-producing) genes varied significantly at the two irrigation levels. Overall, multiple N sources could inhibit NH3 volatilization increasing under reducing irrigation compared to a single chemical fertilizer. Our findings contribute valuable insights into the combined effect of reduced irrigation and multiple N sources on NH3 volatilization. Full article
(This article belongs to the Section Water Use and Irrigation)
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<p>Temporal variation of NH<sub>3</sub> flux under reduced irrigation (<b>A</b>) and conventional irrigation (<b>B</b>), the NH<sub>3</sub> cumulative volatilization (<b>C</b>) and the linear regression analysis of the cumulative NH<sub>3</sub> volatilization and the amount of chemical fertilizer applied (<b>D</b>). S: straw retention; M: manure substitution; W1: reduced irrigation; W2: conventional irrigation. No uppercase S or M represents straw non-retention or no manure substitution. Different lowercase letters above the column meant significant differences between treatments (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Visualization of soil microorganisms and nitrogen form networks (<b>A</b>), the nodes and edges of networks (<b>B</b>), and the random forest analysis of the core functional microorganisms affecting NH<sub>3</sub> at the genus level (<b>C</b>). The IncMSE value represents the degree of core microorganisms.</p>
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<p>The N functional genes are directly related to NH<sub>3</sub> volatilization (<b>A</b>), gene abundance heatmap (<b>B</b>), and the gene relative abundance of <span class="html-italic">nirA</span>, <span class="html-italic">arcC</span>, <span class="html-italic">E3.5.1.49</span>, and <span class="html-italic">E3.5.5.1</span> (<b>C</b>–<b>F</b>). S: straw retention; M: manure substitution; W1: reduced irrigation; W2: conventional irrigation. No uppercase S or M represents straw non-retention or no manure substitution. Different lowercase letters in <a href="#agronomy-14-02927-f003" class="html-fig">Figure 3</a>C–F indicate significant differences between treatments (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Network analysis showing the relationships between microorganisms at the genus level and NH<sub>3</sub> volatilization functional genes under different irrigation levels (<b>A</b>), the edge numbers of different genes (<b>B</b>), and the correlation analysis between key genes and core microorganisms (<b>C</b>). * and ** represent significant differences at <span class="html-italic">p</span> &lt; 0.05 and <span class="html-italic">p</span> &lt; 0.01, respectively.</p>
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13 pages, 432 KiB  
Article
A Comprehensive Evaluation of Water-Saving Society Construction in Xinxiang, Henan Province, China
by Mingliang Jiang and Chengcai Zhang
Sustainability 2024, 16(23), 10737; https://doi.org/10.3390/su162310737 - 6 Dec 2024
Viewed by 521
Abstract
Water is a crucial and fundamental resource. It is well known that agricultural cultivation, industrial production, and human daily life are not possible without water. Efficiently utilizing water resources is of great significance for achieving global Sustainable Development Goals (SDGs). In order to [...] Read more.
Water is a crucial and fundamental resource. It is well known that agricultural cultivation, industrial production, and human daily life are not possible without water. Efficiently utilizing water resources is of great significance for achieving global Sustainable Development Goals (SDGs). In order to improve water use efficiency in various industries and promote water-saving development, China has been implementing water-saving society construction since 2002. Henan Province is the main grain-producing area in China, with wheat production accounting for a quarter of the country’s total. As the core area of “Central Plains Agricultural Valley” in Henan Province, Xinxiang City plays an important role in agricultural technology innovation and agricultural production. However, Xinxiang City is facing problems of water scarcity and pollution, which constrain the sustainability of agricultural production. Therefore, building a water-saving society can solve the current water problems faced by Xinxiang City and ensure the sustainable development of the economy and society. This study built an evaluation index system for water-saving society construction in Xinxiang, Henan Province, China. The proposed evaluation index system includes 20 evaluation indices from six aspects—integrated, agricultural water, industrial water, domestic water, water ecology and environment, and water-saving management—and then divides its development level into several stages. The Analytical Hierarchy Process (AHP) was adopted to calculate the index weight. Then, a comprehensive evaluation model for water-saving society construction in Xinxiang City was established by combining it with grey relative analysis (GRA). The results showed that the overall level of water-saving society construction in Xinxiang City is in the excellent stage, whereas water consumption per CNY 10,000 of GDP, the effective utilization coefficient of irrigation water, the reuse rate of industrial water, and the leakage rate of urban water supply network are all in the good stage. However, the urban recycled water utilization rate is still in the poor stage. These research results can effectively and reasonably reflect the development level of water-saving society construction in Xinxiang City and guide the continued implementation of water-saving society construction. At the same time, the comprehensive evaluation of water-saving society construction helps to formulate and adjust water resource management policies and measures; it also holds significant value for sustainable water management and combating water scarcity. Full article
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<p>Methodology adopted in this study.</p>
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32 pages, 7429 KiB  
Article
Isotope Geochemistry and Metallogenic Model of the Bailugou Vein-Type Zn-Pb-Ag Deposit, Eastern Qinling Orogen, China
by Yan Yang, Hui Chen, Nana Guo, Donghao Wu, Zhenshan Pang and Yanjing Chen
Minerals 2024, 14(12), 1244; https://doi.org/10.3390/min14121244 - 6 Dec 2024
Viewed by 320
Abstract
The large-scale vein-type Zn-Pb-Ag deposit in the Eastern Qinling Orogen (EQO) has sparked a long-standing debate over whether magmatism or metamorphism was the primary control or factor in its formation. Among the region’s vein-type deposits, the large-sized Bailugou deposit offers a unique opportunity [...] Read more.
The large-scale vein-type Zn-Pb-Ag deposit in the Eastern Qinling Orogen (EQO) has sparked a long-standing debate over whether magmatism or metamorphism was the primary control or factor in its formation. Among the region’s vein-type deposits, the large-sized Bailugou deposit offers a unique opportunity to study this style of mineralization. Similar to other deposits in the area, the vein-type orebodies of the Bailugou deposit are hosted in dolomitic marbles (carbonate–shale–chert association, CSC) of the Mesoproterozoic Guandaokou Group. Faults control the distribution of the Bailugou deposit but do not show apparent spatial links to the regional Yanshanian granitic porphyry. This study conducted comprehensive H–O–C–S–Pb isotopic analyses to constrain the sources of the ore-forming metals and metal endowments of the Bailugou deposit. The δ34SCDT values of sulfides range from 1.1‰ to 9.1‰ with an average of 4.0‰, indicating that the sulfur generated from homogenization during the high-temperature source acted on host sediments. The Pb isotopic compositions obtained from 31 sulfide samples reveal that the lead originated from the host sediments rather than from the Mesozoic granitic intrusions. The results indicate that the metals for the Bailugou deposit were jointly sourced from host sediments of the Mid-Late Proterozoic Meiyaogou Fm. and the Nannihu Fm. of the Luanchuan Group and Guandaokou Group, as well as lower crust and mantle materials. The isotopic composition of carbon, hydrogen, and oxygen collectively indicate that the metallogenic constituents of the Bailugou deposit were contributed by ore-bearing surrounding rocks, lower crust, and mantle materials. In summary, the study presents a composite geologic-metallogenic model suggesting that the Bailugou mineral system, along with other lead-zinc-silver deposits, porphyry-skarn molybdenum-tungsten deposits, and the small granitic intrusions in the Luanchuan area, are all products of contemporaneous hydrothermal diagenetic mineralization. This mineralization event transpired during a continental collision regime between the Yangtze and the North China Block (including syn- to post-collisional settings), particularly during the transition from collisional compression to extension around 140 Ma. The Bailugou lead-zinc-silver mineralization resembles an orogenic-type deposit formed by metamorphic fluid during the Yanshanian Orogeny. Full article
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<p>Geological map of the Bailugou deposit (modified from Duan et al. [<a href="#B31-minerals-14-01244" class="html-bibr">31</a>]).</p>
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<p>Geologic scheme of the Bailugou Zn–Pb deposit (modified from Yan [<a href="#B35-minerals-14-01244" class="html-bibr">35</a>]; Zhang [<a href="#B36-minerals-14-01244" class="html-bibr">36</a>]).</p>
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<p><span class="html-italic">δ</span>D<sub>w</sub> (‰) versus <span class="html-italic">δ</span><sup>18</sup>O<sub>w</sub> (‰) in the ore-forming fluids of the Bailugou deposit (based on Taylor [<a href="#B51-minerals-14-01244" class="html-bibr">51</a>]). Data are from <a href="#minerals-14-01244-t003" class="html-table">Table 3</a>. Unclear stage from [<a href="#B27-minerals-14-01244" class="html-bibr">27</a>,<a href="#B45-minerals-14-01244" class="html-bibr">45</a>].</p>
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<p>Compilation histograms of <span class="html-italic">δ</span><sup>13</sup>C<sub>PDB</sub> (‰) values in sulfides from ores, ore-bearing host sediments, and regional porphyries of the Bailugou deposit. Data are from <a href="#minerals-14-01244-t001" class="html-table">Table 1</a>.</p>
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<p>Compilation histograms of <span class="html-italic">δ</span><sup>18</sup>O<sub>SMOW</sub> (‰) values in sulfides from ores, ore-bearing host sediments, and regional porphyries of the Bailugou deposit. Data are from <a href="#minerals-14-01244-t003" class="html-table">Table 3</a>.</p>
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<p>Compilation histograms of <span class="html-italic">δ</span><sup>34</sup>S values in sulfides from ores, ore-bearing strata, and regional porphyries of the Bailugou deposit. Data are from <a href="#minerals-14-01244-t001" class="html-table">Table 1</a>.</p>
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<p>Values of <sup>207</sup>Pb/<sup>204</sup>Pb vs. <sup>206</sup>Pb/<sup>204</sup>Pb and <sup>208</sup>Pb/<sup>204</sup>Pb vs. <sup>206</sup>Pb/<sup>204</sup>Pb for sulfides of the Bailugou deposit plotted on diagrams proposed by Zartman and Doe [<a href="#B65-minerals-14-01244" class="html-bibr">65</a>]. Note that the different lines enclose the present Pb isotope ranges for the host rocks and granitoids in the study region. The lead isotopic data are from <a href="#minerals-14-01244-t002" class="html-table">Table 2</a>.</p>
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<p>Histograms of the Pb isotope model age calculated by the Holmes–Houtermans method according to the single-stage evolution model of the Bailugou deposit.</p>
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<p>Lead isotope pattern for the Bailugou deposit and adjacent rocks (plotted on diagrams proposed by Zartman and Doe [<a href="#B65-minerals-14-01244" class="html-bibr">65</a>]). (<b>A</b>,<b>B</b>) the display of sulfides from the ores versus the ore-hosting Luanchuan Group; (<b>C</b>,<b>D</b>) the display of sulfides from the ores versus the ore-hosting Guandaokou Group; (<b>E</b>,<b>F</b>) the display of sulfides from the ores versus the K-feldspar and galena in Nannihu porphyry and Shangfanggou porphyry.</p>
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<p><span class="html-italic">δ</span><sup>13</sup>C<sub>PDB</sub> (‰) versus <span class="html-italic">δ</span><sup>18</sup>O<sub>SMOW</sub> (‰) of the Bailugou deposit and adjacent rocks (modified from Mao et al., [<a href="#B77-minerals-14-01244" class="html-bibr">77</a>]; Sun et al., [<a href="#B79-minerals-14-01244" class="html-bibr">79</a>]; Liu and Liu [<a href="#B80-minerals-14-01244" class="html-bibr">80</a>]; Liu et al., [<a href="#B81-minerals-14-01244" class="html-bibr">81</a>]).</p>
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<p>Tectonic evolution and genetic model for the Bailugou deposit and the Luanchuan polymetal belt. (<b>A</b>) Opening of the Erlangping Sea back arc basin and deposition of the Luanchuan and Guandaokou Groups along the passive continental margin, while the Shang-Dan Ocean is subducted beneath the Central Qinling Terrane (figure revised from Chen et al. [<a href="#B10-minerals-14-01244" class="html-bibr">10</a>]). (<b>B</b>) Schematic representation of CMF (collisional orogeny, metallogeny, and fluid flow) illustrating the relationships between ore-hosting structures, granitoids, porphyries, and deposits in the Luanchuan area. Fluids, released from subducted slab and ocean floor sediment, or the hydrated mantle wedge, ascend along the interface between the slab and the overlying wedge or base of the lithosphere. The over-pressured ore fluids intersect deep crustal faults and then advect upwards to form orogenic deposits in second-order structures or hydraulically fractured rock bodies.</p>
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20 pages, 10283 KiB  
Article
Coupling and Coordination Analysis of Land Use Function and Ecological Quality in Yellow River Basin, Henan Province, China
by Yue Wang, Xiang Jia, Zheng Wang, Jingxu Wang, Shike Qiu, Zhun Guo and Jun Du
Sustainability 2024, 16(23), 10699; https://doi.org/10.3390/su162310699 - 6 Dec 2024
Viewed by 363
Abstract
As economic development and urbanization continue to accelerate, the Yellow River Basin experiences increasing challenges in balancing land use with ecological environmental protection. Understanding their interactions is crucial for sustainable regional development. This study adopts an integrated evaluation system and a coupling model [...] Read more.
As economic development and urbanization continue to accelerate, the Yellow River Basin experiences increasing challenges in balancing land use with ecological environmental protection. Understanding their interactions is crucial for sustainable regional development. This study adopts an integrated evaluation system and a coupling model to examine the dynamic interactions between land use functions and ecological quality in the Yellow River Basin section of Henan Province, China, from 2000 to 2020. The primary findings are as follows: (1) Land use functions improved from 0.276 to 0.303, with high-land-use-function areas expanding eastward. (2) Ecological quality initially declined but subsequently improved, with areas having good and excellent ecological quality increasing from 44.47% to 72.61%. (3) Coupling coherence stabilized, with moderate coordination covering 69.80% of the area by 2020. (4) The fractional vegetation cover and leaf area index were identified as critical influencing factors. Overall, these results highlight the importance of balanced land use planning and targeted ecological conservation strategies. This study provides valuable insights for policymakers aiming to enhance sustainable regional development, emphasizing the importance of integrating ecological security with economic growth in rapidly urbanizing areas. Full article
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<p>Location of the study area.</p>
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<p>Land use function of the study area over time: (<b>a</b>) change in area and (<b>b</b>) change in the number of cities.</p>
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<p>Spatial distributions of the land use function of the study area from 2000 to 2020.</p>
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<p>Temporal evolution in the ecological quality of the study area.</p>
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<p>Spatial distributions of the ecological quality of the study area from 2000 to 2020.</p>
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<p>Coupling coherence of the Yellow River Basin in Henan Province from 2000 to 2020.</p>
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<p>Factor contribution rates in the study area. (Note: The values of X correspond to those detailed in <a href="#sustainability-16-10699-t007" class="html-table">Table 7</a>).</p>
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<p>Coupling interaction factor detection in the study area.</p>
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20 pages, 5748 KiB  
Review
Nanolabels Prepared by the Entrapment or Self-Assembly of Signaling Molecules for Colorimetric and Fluorescent Immunoassays
by Ning Xia, Yadi Li, Cancan He and Dehua Deng
Biosensors 2024, 14(12), 597; https://doi.org/10.3390/bios14120597 - 6 Dec 2024
Viewed by 432
Abstract
Nanomaterials have attracted significant attention as signal reporters for immunoassays. They can directly generate detectable signals or release a large number of signaling elements for readout. Among various nanolabels, nanomaterials composed of multiple signaling molecules have shown great potential in immunoassays. Generally, signaling [...] Read more.
Nanomaterials have attracted significant attention as signal reporters for immunoassays. They can directly generate detectable signals or release a large number of signaling elements for readout. Among various nanolabels, nanomaterials composed of multiple signaling molecules have shown great potential in immunoassays. Generally, signaling molecules can be entrapped in nanocontainers or self-assemble into nanostructures for signal amplification. In this review, we summarize the advances of signaling molecules-entrapped or assembled nanomaterials for colorimetric and fluorescence immunoassays. The nanocontainers cover liposomes, polymers, mesoporous silica, metal–organic frameworks (MOFs), various nanosheets, nanoflowers or nanocages, etc. Signaling molecules mainly refer to visible and/or fluorescent organic dyes. The design and application of immunoassays are emphasized from the perspective of nanocontainers, analytes, and analytical performances. In addition, the future challenges and research trends for the preparation of signaling molecules-entrapped or assembled nanolabels are briefly discussed. Full article
(This article belongs to the Special Issue Biosensors Based on Self-Assembly and Boronate Affinity Interaction)
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<p>(<b>A</b>) Schematic of the liposome-amplified plasmonic immunoassay (LAPIA). The detection steps include the capture (<b>a</b>) and recognition (<b>b</b>) of the target, attachment of streptavidin (<b>c</b>), coupling of biotin-conjugated cysteine-contained liposomes (<b>d</b>), breakdown of the liposomes (<b>e</b>), and release of cysteine to trigger the aggregation of AuNPs (<b>f</b>) [<a href="#B27-biosensors-14-00597" class="html-bibr">27</a>]. Copyright 2015 American Chemical Society. (<b>B</b>) Schematic illustration of signal-on competitive-type colorimetric immunoassay for the detection of streptomycin (STR) on monoclonal anti-STR antibody-coated microplate using glucose-loaded liposome as the signal tracer labeled with STR-bovine serum albumin (BSA) conjugate: (<b>a</b>) competitive-type immunoreaction and (<b>b</b>) glucose oxidase (GOx)-triggered the change of the Fe(II)-Phen system in the absorbance and visual color by the reaction of the produced H<sub>2</sub>O<sub>2</sub> with iron(II) [<a href="#B41-biosensors-14-00597" class="html-bibr">41</a>]. Copyright 2018 Elsevier.</p>
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<p>Schematic presentation of the heterogeneous sandwich immunoassay with PSP for loading load C153, hemin, or microperoxidase MP11 based on different signal generation strategies and photo/chemiluminescence detection [<a href="#B51-biosensors-14-00597" class="html-bibr">51</a>]. Copyright 2024 American Chemical Society.</p>
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<p>(<b>A</b>) (<b>a</b>) Synthesis and derivatization of TP@PEI/Ab<sub>2</sub>-MSNs and (<b>b</b>) steps of the enzyme-free immunosorbent assay of PSA using for amplified colorimetric detection in a 96-well plate [<a href="#B63-biosensors-14-00597" class="html-bibr">63</a>]. Copyright 2018 American Chemical Society. (<b>B</b>) Schematic illustration of the magnetic bead (MB)-based colorimetric immunoassay of PSA by the redox cycling with Ab<sub>2</sub>-MSN-PQQ as the nanolabel [<a href="#B64-biosensors-14-00597" class="html-bibr">64</a>]. Copyright 2019 Elsevier. (<b>C</b>) Schematic illustration of the fluorescence immunoassay based on target-induced competitive displacement reaction between glucose and mannose for Con A accompanying cargo (rhodamine B) release from magnetic mesoporous silica nanoparticles (MMSNs) [<a href="#B65-biosensors-14-00597" class="html-bibr">65</a>]. Copyright 2013 American Chemical Society.</p>
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<p>(<b>A</b>) (<b>a</b>) Preparation of MOFs NH<sub>2</sub>-MIL-53(Al) and (<b>b</b>) schematic illustration of competitive FIA of AFB1 [<a href="#B81-biosensors-14-00597" class="html-bibr">81</a>]. Copyright 2019 American Chemical Society. (<b>B</b>) Schematic illustration of the synthetic procedure of MILL-88@TcP nanozyme-based detection probe (<b>top</b>) and the procedure of this developed N-ELISA for <span class="html-italic">S. typhimurium</span> detection in milk (<b>bottom</b>) [<a href="#B89-biosensors-14-00597" class="html-bibr">89</a>]. Copyright 2024 Elsevier.</p>
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<p>(<b>A</b>) Schematic representation of MPDA@TP-linked immunosorbent assay (MLISA) for α-fetoprotein (AFP) on anti-AFP capture antibody (CAb)-modified microplate using anti-AFP detection antibody (DAb)-labeled MPDA@TP with a sandwich-type immunoreaction mode [<a href="#B92-biosensors-14-00597" class="html-bibr">92</a>]. Copyright 2018 American Chemical Society. (<b>B</b>) The synthesis of UiO, UiOL, UiOL@AIEgens, and UiOL@AIEgens-mAbs probe (<b>a</b>), and the UiOL@AIEgens-based POC LFIS for visual and quantitative dual-modal detection of AFB1 (<b>b</b>) [<a href="#B96-biosensors-14-00597" class="html-bibr">96</a>]. Copyright 2024 Elsevier.</p>
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<p>(<b>A</b>) (<b>a</b>) The preparation process for the signal label of PP-Ab<sub>2</sub>-cC<sub>3</sub>N<sub>4</sub>, and (<b>b</b>) schematic illustration of the PILISA for the detection of CEA in 96-well PS plates [<a href="#B100-biosensors-14-00597" class="html-bibr">100</a>]. Copyright 2017 Elsevier. (<b>B</b>) Schematic of AuNF@Fluorescein@SA preparation, and AuNF@Fluorescein@SA-based dual-mode fluorescent and colorimetric immunoassay [<a href="#B101-biosensors-14-00597" class="html-bibr">101</a>]. Copyright 2018 Elsevier.</p>
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<p>(<b>A</b>) Synthetic procedure for SAD carriers and their applications in ICAs. (<b>B</b>) Comparison of SAD-ICAs with three modes and a traditional nanomaterial—ICA (take AuNPs as an example)—for the detection of ZEN [<a href="#B102-biosensors-14-00597" class="html-bibr">102</a>]. Copyright 2021 American Chemical Society.</p>
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<p>(<b>A</b>) Principle of immunoassay using antigen-decorated perylene microparticles [<a href="#B109-biosensors-14-00597" class="html-bibr">109</a>]. Copyright 2000 Elsevier. (<b>B</b>) Principle of a sandwich fluorescent immunoassay using nanocrystalline fluorescein diacetate (FDA) conjugates [<a href="#B103-biosensors-14-00597" class="html-bibr">103</a>]. Copyright 2004 American Chemical Society.</p>
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<p>(<b>A</b>) Workflow of porphyrin nanoparticle-based signal amplification sandwich assays for the detection of biomolecules [<a href="#B112-biosensors-14-00597" class="html-bibr">112</a>]. Copyright 2016 American Chemical Society. (<b>B</b>) Scheme of sandwich-type TLISA for the detection of IL-6 [<a href="#B115-biosensors-14-00597" class="html-bibr">115</a>]. Copyright 2019 American Chemical Society.</p>
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<p>(<b>A</b>) Schematic diagram illustrating the principle of using organic nanoparticles as biolabels for immunodipsticks [<a href="#B119-biosensors-14-00597" class="html-bibr">119</a>]. Copyright 2011 Elsevier. (<b>B</b>) Schematic representation of the strategy of integrating an SAN-LFA for the detection of cardiac biomarkers [<a href="#B120-biosensors-14-00597" class="html-bibr">120</a>]. Copyright 2016 American Chemical Society.</p>
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32 pages, 35891 KiB  
Article
Analysis of the Trends and Driving Factors of Cultivated Land Utilization Efficiency in Henan Province from 2000 to 2020
by Henggang Zhang, Chenhui Zhu, Tianyu Jiao, Kaiyue Luo, Xu Ma and Mingyu Wang
Land 2024, 13(12), 2109; https://doi.org/10.3390/land13122109 - 5 Dec 2024
Viewed by 590
Abstract
Amid persistent global food security challenges, the efficient utilization of cultivated land resources has become increasingly critical, as optimizing Cultivated Land Utilization Efficiency (CLUE) is paramount to ensuring food supply. This study introduced a cultivated land utilization index (CLUI) based on Fractional Vegetation [...] Read more.
Amid persistent global food security challenges, the efficient utilization of cultivated land resources has become increasingly critical, as optimizing Cultivated Land Utilization Efficiency (CLUE) is paramount to ensuring food supply. This study introduced a cultivated land utilization index (CLUI) based on Fractional Vegetation Cover (FVC) to assess the spatiotemporal variations in Henan Province’s CLUE. The Theil–Sen slope and the Mann–Kendall test were used to analyze the spatiotemporal variations of CLUE in Henan Province from 2000 to 2020. Additionally, we used a genetic algorithm optimized Artificial Neural Network (ANN) and a particle swarm optimization-based Random Forest (RF) model to assess the comprehensive in-fluence between topography, climate, and human activities on CLUE, in which incorporating Shapley Additive Explanations (SHAP) values. The results reveal the following: (1) From 2000 to 2020, the CLUE in Henan province showed an overall upward trend, with strong spatial heterogeneity across various regions: the central and eastern areas generally showed decline, the northern region remained stable with slight increases, the western region saw significant growth, while the southern area exhibited complex fluctuations. (2) Natural and economic factors had notable impacts on CLUE in Henan province. Among these factors, population and economic factors played a dominant role, whereas average temperature exerted an inhibitory effect on CLUE in most parts of the province. (3) The influenced factors on CLUE varied spatially, with human activity impacts being more concentrated, while topographical and climatic influences were relatively dispersed. These findings provide a scientific basis for land management and agricultural policy formulation in major grain-producing areas, offering valuable insights into enhancing regional CLUE and promoting sustainable agricultural development. Full article
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<p>Overview of the study area: (<b>a</b>) location of Henan Province; (<b>b</b>) true-color satellite image of Henan Province; (<b>c</b>–<b>g</b>) typical cultivated land areas in central, northern, western, southern, and eastern regions of Henan Province.</p>
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<p>Flow chart of technical route.</p>
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<p>Interannual changes in CLUI in Henan Province from 2000 to 2020. (<b>a</b>) Representing the spatial differences of CLUI in Henan Province in 2000; (<b>b</b>) Representing the spatial differences of CLUI in Henan Province in 2002; (<b>c</b>) Representing the spatial differences of CLUI in Henan Province in 2004; (<b>d</b>) Representing the spatial differences of CLUI in Henan Province in 2006; (<b>e</b>) Representing the spatial differences of CLUI in Henan Province in 2008; (<b>f</b>) Representing the spatial differences of CLUI in Henan Province in 2010; (<b>g</b>) Representing the spatial differences of CLUI in Henan Province in 2012; (<b>h</b>) Representing the spatial differences of CLUI in Henan Province in 2014; (<b>i</b>) Representing the spatial differences of CLUI in Henan Province in 2016; (<b>j</b>) Representing the spatial differences of CLUI in Henan Province in 2018; (<b>k</b>) Representing the spatial differences of CLUI in Henan Province in 2020.</p>
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<p>Interannual change trend of CLUI index from 2000 to 2020: (<b>a</b>) represents the interannual change of the maximum value of CLUI, and (<b>b</b>) represents the interannual change of the average CLUI.</p>
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<p>CLUI Sen-MK trend test from 2000 to 2020: (<b>a</b>) represents central Henan Province; (<b>b</b>) represents northern Henan Province; (<b>c</b>) represents western Henan Province; (<b>d</b>) represents central Henan Province; (<b>e</b>) represents southern Henan Province.</p>
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<p>Variable importance ranking chart before and after optimization: (<b>a</b>) represents the variable importance ranking before ANN optimization; (<b>b</b>) represents the variable importance ranking after ANN optimization; (<b>c</b>) represents the variable importance ranking before RF optimization; (<b>d</b>) represents RF. Ranking of variable importance after optimization.</p>
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<p>Average variable importance ranking.</p>
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<p>Interannual changes of main factors: (<b>a</b>) represents the age change of the maximum value of Pop. Dens.; (<b>b</b>) represents the age change of the average value of Pop. Dens.; (<b>c</b>) represents the age change of the maximum value of GBR; (<b>d</b>) represents the age change of the average value of GBR; (<b>e</b>) represents the maximum SI value age change; (<b>f</b>) represents the SI average age change; (<b>g</b>) represents the Reg. Pop. maximum age change; (<b>h</b>) represents the Reg. Pop. average age change; (<b>i</b>) represents the GBE maximum age change; (<b>j</b>) represents the GBE average age change; (<b>k</b>) represents the age change of the maximum value of PC; (<b>l</b>) represents the age change of the average PC value; (<b>m</b>) represents the age change of the maximum value of Avg. Temp, and (<b>n</b>) represents the age change of the average value of Avg. Temp.</p>
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<p>Correlation analysis between main driving factors and CLUI: (<b>a</b>) represents the correlation analysis between Pop. Dens. and CLUE; (<b>b</b>) represents the correlation analysis between GBR and CLUE; (<b>c</b>) represents the correlation analysis between SI and CLUI; (<b>d</b>) represents the correlation analysis between Reg. Pop. and CLUI; (<b>e</b>) represents the correlation analysis between GBE and CLUI; (<b>f</b>) represents the correlation analysis between PC and CLUI; (<b>g</b>) represents the correlation analysis between Avg. Temp and CLUI.</p>
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15 pages, 3187 KiB  
Article
Study on Watershed Ecological Compensation for Water Pollution Considering Population Flow: A Case Study in the Lower Yellow River Basin
by Peng Lu, Bo Qu, Ying Liu and Mingtang Liu
Water 2024, 16(23), 3507; https://doi.org/10.3390/w16233507 - 5 Dec 2024
Viewed by 417
Abstract
Watershed ecological compensation (WEC) mechanisms can help coordinate the distribution of revenue among different regions and realize the collaborative treatment of water pollution. However, limited research has examined the influence of population flow on the design of ecological compensation mechanisms. In this paper, [...] Read more.
Watershed ecological compensation (WEC) mechanisms can help coordinate the distribution of revenue among different regions and realize the collaborative treatment of water pollution. However, limited research has examined the influence of population flow on the design of ecological compensation mechanisms. In this paper, the differential game method is used to construct a model of water pollution control in upstream and downstream regions with the consideration of population flow. The Lower Yellow River Basin (LYRB), which includes Henan and Shandong Provinces, is taken as a case study, and relevant data are used for simulation analysis. The constraints and population flow factors that influence the establishment of a WEC mechanism between upstream and downstream governments are explored. The results show that (1) the implementation of WEC can stimulate the upstream government’s efforts to treat pollutants, and the amount of pollutants eliminated and the revenue of the upstream and downstream governments increase; (2) with the continuous flow of population from the upstream region to the downstream region, the amount of pollutants eliminated and the revenue of the downstream government decrease; and (3) in the absence of external incentive measures, when the population flow exceeds a certain threshold, the WEC mechanism of the upstream and downstream governments cannot be spontaneously carried out. The conclusions of this study can provide scientific guidance for improving the WEC mechanism between the upstream and downstream governments within a basin. Full article
(This article belongs to the Section Water Resources Management, Policy and Governance)
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<p>Research framework.</p>
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<p>Study area.</p>
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<p>Impact of population flow on the pollution treatment efforts of the upstream and downstream governments. (<b>a</b>) The pollution treatment efforts of the upstream government. (<b>b</b>) The pollution treatment efforts of the downstream government. (<b>c</b>) The impact of population flow on upstream pollution treatment efforts. (<b>d</b>) The impact of population flow on downstream pollution treatment efforts.</p>
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<p>Impact of population flow on the amounts of pollutants eliminated. (<b>a</b>) The amounts of water pollutants eliminated by the upstream and downstream governments when P = 0. (<b>b</b>) The amounts of water pollutants eliminated by the upstream and downstream governments when P = 50.</p>
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<p>Impact of population outflow on revenue in upstream Henan Province. (<b>a</b>) The revenue of the Henan Province when P = 0. (<b>b</b>) The revenue of the Henan Province when P = 20. (<b>c</b>) The revenue of the Henan Province when P = 50.</p>
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<p>Impact of population flow on the revenue of Shandong Province. (<b>a</b>) The revenue of the Shandong Province when P = 0. (<b>b</b>) The revenue of the Shandong Province when P = 20. (<b>c</b>) The revenue of the Shandong Province when P = 50.</p>
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