[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

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
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Article Types

Countries / Regions

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

Search Results (5,031)

Search Parameters:
Keywords = ion-selective

Order results
Result details
Results per page
Select all
Export citation of selected articles as:
15 pages, 587 KiB  
Review
Progress in Research on Metal Ion Crosslinking Alginate-Based Gels
by Yantao Wang, Zhenpeng Shen, Huili Wang, Zhaoping Song, Dehai Yu, Guodong Li, Xiaona Liu and Wenxia Liu
Gels 2025, 11(1), 16; https://doi.org/10.3390/gels11010016 (registering DOI) - 27 Dec 2024
Abstract
Alginate is an important natural biopolymer and metal ion-induced gelation is one of its most significant functional properties. Alginate-based hydrogels crosslinked with metal ions are commonly utilized in the food, biomedical, tissue engineering, and environment fields. The process of metal ion-induced alginate gelation [...] Read more.
Alginate is an important natural biopolymer and metal ion-induced gelation is one of its most significant functional properties. Alginate-based hydrogels crosslinked with metal ions are commonly utilized in the food, biomedical, tissue engineering, and environment fields. The process of metal ion-induced alginate gelation has been the subject of thorough research over the last few decades. This review aims to summarize the mechanisms of alginate hydrogels induced by different cations (primarily including Ca2+, Ba2+, Cu2+, Sr2+, Fe2+/Fe3+, and Al3+). Metal ion-induced alginate gelation shows different preferences for α-L-guluronic acid (G), β-D-mannuronic acid (M), and GM blocks. Some metal ions can also selectively bind to the carboxyl groups of guluronic acid. The properties and applications of these alginate-based hydrogels are also discussed. The primary objective of this review is to provide useful information for exploring the practical applications of alginate. Full article
(This article belongs to the Special Issue Recent Research on Alginate Hydrogels in Bioengineering Applications)
12 pages, 5359 KiB  
Article
Electrical Characteristics of Solution-Based Thin-Film Transistors with a Zinc-Tin Oxide/Carbon Nanotube Stacked Nanocomposite Active Layer
by Yong-Jae Kim and Woon-Seop Choi
Nanomaterials 2025, 15(1), 22; https://doi.org/10.3390/nano15010022 - 27 Dec 2024
Viewed by 1
Abstract
A stacked nanocomposite zinc-tin oxide/single-walled carbon nanotubes (ZTO/SWNTs) active layer was fabricated for thin-film transistors (TFTs) as an alternative to the conventional single-layer structure of mixed ZTO and SWNTs. The stacked nanocomposite of the solution-processed TFTs was prepared using UV/O3 treatment and [...] Read more.
A stacked nanocomposite zinc-tin oxide/single-walled carbon nanotubes (ZTO/SWNTs) active layer was fabricated for thin-film transistors (TFTs) as an alternative to the conventional single-layer structure of mixed ZTO and SWNTs. The stacked nanocomposite of the solution-processed TFTs was prepared using UV/O3 treatment and multiple annealing steps for each layer. The electrical properties of the stacked device were superior to those of the single-layer TFT. The ZTO/SWNT TFT, fabricated using a stacked structure with ZTO on the top and SWNT at the bottom layer, showed a significant improvement in the field-effect mobility of 15.37 cm2/V·s (factor of three increase) and an Ion/Ioff current ratio of 8.83 × 108 with improved hysteresis. This outcome was attributed to the surface treatment and multiple annealing of the selected active layer, resulting in improved contact and a dense structure. This was also attributed to the controlled dispersion of SWNT, as electron migration paths without dispersants. This study suggests the potential expansion of applications, such as flexible electronics and low-cost fabrication of TFTs. Full article
(This article belongs to the Special Issue Nanoelectronics: Materials, Devices and Applications (Second Edition))
Show Figures

Figure 1

Figure 1
<p>Schematic cross-section views of the bottom gate staggered structure for (<b>a</b>) sample A (ZTO only), (<b>b</b>) sample B (ZTO/SWNTs mixed), (<b>c</b>) sample C (Top SWNT bottom ZTO), (<b>d</b>) sample D (Top ZTO bottom SWNT). (S: Source, D: Drain).</p>
Full article ">Figure 2
<p>(<b>a</b>) Optical microscopy images of annealed sample C at various SWNT concentrations (0.01–0.07 wt.%), (<b>b</b>) Optical microscopy images of annealed sample D at various SWNT concentrations (0.01–0.07 wt.%).</p>
Full article ">Figure 3
<p>SEM images, mapping, and EDX elements of ZTO/SWNT film with 0.07 wt.% SWNTs concentration with a scale bar of 200 nm.</p>
Full article ">Figure 4
<p>Transmittance and absorption spectra of ZTO/SWNT thin films on glass with different SWNT concentrations.</p>
Full article ">Figure 5
<p>Resistivity of ZTO/SWNT thin films with different SWNT concentrations.</p>
Full article ">Figure 6
<p>Transfer characteristics and output characteristics of a SWNT/ZTO TFTs with 0.07 wt.% SWNT concentration. (<b>a</b>,<b>d</b>) sample A (ZTO only) (<b>b</b>,<b>e</b>) sample C (Top SWNT bottom ZTO) (<b>c</b>,<b>f</b>) sample D (Top ZTO bottom SWNT).</p>
Full article ">Figure 7
<p>(<b>a</b>) Field-effect mobility vs. SWNT concentration. (<b>b</b>) I<sub>on</sub>/I<sub>off</sub> current ratio vs. SWNTs concentration. (<b>c</b>) Vth vs. SWNT concentrations. (<b>d</b>) Off current vs. SWNT concentrations. All for the ZTO/SWNT nanocomposite TFTs.</p>
Full article ">Figure 8
<p>Hysteresis characteristics of a ZTO only and ZTO/SWNTs (0.07 wt.%) TFTs. (<b>a</b>) sample A (ZTO only), (<b>b</b>) sample B (ZTO/SWNTs mixed), (<b>c</b>) sample C (Top SWNTs bottom ZTO), (<b>d</b>) sample D (Top ZTO bottom SWNTs).</p>
Full article ">Figure 9
<p>Approach to a solution-based ZTO through a blend of SWNT as carrier transport rods to increase the electrical performance, (<b>a</b>) SWNT mixed ZTO TFT (<b>b</b>) top SWNTs bottom ZTO TFT (<b>c</b>) top ZTO bottom SWNTs TFT. (S: Source, D: Drain).</p>
Full article ">
15 pages, 2845 KiB  
Article
Study on Impurity Removal from Lepidolite Leaching Solution and the Extraction Process of Rubidium
by Wen Tan, Yanbo Yang, Donghui Liang, Wei Weng, Xiaopeng Chi and Shuiping Zhong
Minerals 2025, 15(1), 19; https://doi.org/10.3390/min15010019 - 27 Dec 2024
Viewed by 29
Abstract
Efficient removal of iron and aluminum impurities is critical for the extraction of lithium and rubidium from zinnwaldite, a lithium-bearing mineral. In this study, solvent extraction using P507 was employed to remove iron and aluminum from zinnwaldite leaching solutions. However, stripping iron from [...] Read more.
Efficient removal of iron and aluminum impurities is critical for the extraction of lithium and rubidium from zinnwaldite, a lithium-bearing mineral. In this study, solvent extraction using P507 was employed to remove iron and aluminum from zinnwaldite leaching solutions. However, stripping iron from the organic phase proved challenging due to the strong interaction between iron ions and the extractant. To address this, a novel reduction stripping method was developed using ascorbic acid (AA) as a reductant. This method exploits the reduction of Fe3+ to Fe2+ in the aqueous phase, weakening the binding between iron ions and the organic phase, thus enabling efficient stripping. The optimized process achieved over 99.99% removal of iron and aluminum impurities. Subsequently, rubidium was selectively extracted using t-BAMBP, with a total recovery rate of 88.53%. Scaling-up experiments confirmed the feasibility of the process for industrial applications, demonstrating high efficiency and reagent recyclability. This study offers a promising approach for the efficient extraction and separation of valuable metals from zinnwaldite, with potential for broader applications in metal processing. Full article
(This article belongs to the Section Mineral Processing and Extractive Metallurgy)
Show Figures

Figure 1

Figure 1
<p>Effect of oscillation frequency on extraction rate.</p>
Full article ">Figure 2
<p>Layering phenomenon observed after extraction at different oscillation frequencies: (<b>a</b>) rpm = 100, (<b>b</b>) rpm = 200, (<b>c</b>) rpm = 300.</p>
Full article ">Figure 3
<p>Influence of various factors on the extraction rate: (<b>a</b>) extraction time, (<b>b</b>) P507 concentration, (<b>c</b>) initial pH, (<b>d</b>) O/A ratio.</p>
Full article ">Figure 4
<p>Effect of various conditions on aluminum extraction rate: (<b>a</b>) pH; (<b>b</b>) O/A ratio.</p>
Full article ">Figure 5
<p>Effect of various conditions on the stripping rate: (<b>a</b>) concentration of H₂SO₄; (<b>b</b>) A/O ratio.</p>
Full article ">Figure 6
<p>Influence of various conditions on the extraction rate: (<b>a</b>) NaOH concentration, (<b>b</b>) extractant concentration, (<b>c</b>) O/A ratio, and (<b>d</b>) extraction time.</p>
Full article ">Figure 7
<p>Extraction isotherm of rubidium.</p>
Full article ">Figure 8
<p>The influence of various conditions on the extraction rate of metal ions: (<b>a</b>) washing water pH, (<b>b</b>) sulfuric acid concentration.</p>
Full article ">Figure 9
<p>Process flow diagram for impurity removal and rubidium separation from zinnwaldite leaching solution.</p>
Full article ">
15 pages, 7520 KiB  
Article
A Novel Fluorescent Chemosensor Based on Rhodamine Schiff Base: Synthesis, Photophysical, Computational and Bioimaging Application in Live Cells
by Oyedoyin Aduroja, Roosevelt Shaw, Sisay Uota, Isaac Abiye, James Wachira and Fasil Abebe
Inorganics 2025, 13(1), 5; https://doi.org/10.3390/inorganics13010005 - 27 Dec 2024
Viewed by 84
Abstract
A novel rhodamine-6G derivative RdN was synthesized by condensing rhodamine glyoxal and 3-hydroxy-2-naphthoic hydrazide using a microwave irradiation-assisted reaction. Colorimetric and photophysical studies have demonstrated that the molecule produced can selectively sense Pb2+ and Cu2+ ions in a solution of CH [...] Read more.
A novel rhodamine-6G derivative RdN was synthesized by condensing rhodamine glyoxal and 3-hydroxy-2-naphthoic hydrazide using a microwave irradiation-assisted reaction. Colorimetric and photophysical studies have demonstrated that the molecule produced can selectively sense Pb2+ and Cu2+ ions in a solution of CH3CN/H2O (9:1, v/v). The spirolactam ring of RdN opens upon complexation with the cations, forming a highly fluorescent complex and a visible color change in the solution. The compound RdN was further studied with the help of computational methods such as the Density Functional Theory (DFT) method and time-dependent density theory (TD-DFT) calculations to study the binding interactions and properties of the molecule. DFT calculations and job plot data supported the 2:1 complex formation between RdN and Pb2+/Cu2+. The limit of detection for Pb2+ was determined to be 0.112 µM and 0.130 µM for Cu2+. The probe RdN was applied to the image of Pb2+ and Cu2+ ions in living cells and is safe for biomedical applications. It is used to monitor Pb2+ in environmental water samples. Full article
(This article belongs to the Special Issue Synthesis and Application of Luminescent Materials, 2nd Edition)
Show Figures

Figure 1

Figure 1
<p>(<b>a</b>) UV-Vis absorption spectra of <b>RdN</b> (10 µM) with various cations. (<b>b</b>) UV-Vis absorption titration of <b>RdN</b> (10 µM) with Pb<sup>2+</sup> (0–20 µM) in acetonitrile-water (9:1 <span class="html-italic">v</span>/<span class="html-italic">v</span>) buffer solution.</p>
Full article ">Figure 2
<p>The visual color of sensor <b>RdN</b> (<b>a</b>) and the fluorescence under UV illumination after adding various metal ions (<b>b</b>).</p>
Full article ">Figure 3
<p>(<b>a</b>) Fluorescence spectra of <b>RdN</b> (5 µM) with cations (λ<sub>exc</sub>: 490 nm). (<b>b</b>) Fluorescence emission titration of <b>RdN</b> with Pb<sup>2+</sup> (0–15 µM) acetonitrile-water (9:1 <span class="html-italic">v</span>/<span class="html-italic">v</span>) solution.</p>
Full article ">Figure 4
<p>(<b>a</b>) Effect of pH on fluorescence intensity of sensor <b>RdN</b> (10 µM) (<b>b</b>) Fluorescence spectra of <b>RdN</b>-Pb<sup>2+</sup> complex (1:1) in the presence of various anions (Cl<sup>−</sup>, Br<sup>−</sup>, F<sup>−</sup>, CH<sub>3</sub>COO<sup>−</sup>, HSO<sub>4</sub><sup>−</sup>, CN<sup>−</sup>, ClO<sub>3</sub><sup>−</sup>, NO<sub>2</sub><sup>−</sup>, S<sup>−2</sup>, N<sub>3</sub><sup>−</sup>, CO<sub>3</sub><sup>2−</sup>).</p>
Full article ">Figure 5
<p>(<b>a</b>) Job’s plot analysis of <b>RdN</b> versus Pb<sup>2+</sup> at a total concentration of 10 µM. (<b>b</b>) Job’s plot analysis of <b>RdN</b> versus Cu<sup>2+</sup> at a total concentration of 10 µM.</p>
Full article ">Figure 6
<p>FTIR spectra of free <b>RdN</b> and in the presence of Pb<sup>2+</sup> and Cu<sup>2+</sup> ions.</p>
Full article ">Figure 7
<p>Optimized Structures and Frontier Molecular Orbitals of <b>RdN II</b> and <b>bis-(RdN II)<sub>2</sub> Pb<sup>+2</sup></b> complex in Gas State.</p>
Full article ">Figure 8
<p>Optimized Structures and Frontier Molecular Orbitals of <b>RdN II</b>, <b>bis-(RdN II)<sub>2</sub>Pb<sup>+2</sup></b> complex in simulated water medium, and <b>bis-(RdN II)<sub>2</sub> Pb<sup>+2</sup></b> complex in simulated CH<sub>3</sub>CN medium.</p>
Full article ">Figure 9
<p>Optimized Structures and Frontier Molecular Orbitals of <b>bis-(RdN)<sub>2</sub>Cu<sup>+2</sup></b> in the Gas State.</p>
Full article ">Figure 10
<p>Optimized Structures and Frontier Molecular Orbitals of <b>RdN II</b>, <b>bis-(RdN II)<sub>2</sub> Cu<sup>+2</sup></b> complex in simulated water medium, and <b>RdN II</b>, <b>bis-(RdN II)<sub>2</sub> Cu<sup>+2</sup></b> complex in simulated CH<sub>3</sub>CN medium.</p>
Full article ">Figure 11
<p>The compound <b>RdN</b> cytotoxicity study on CAD cells in 24 h.</p>
Full article ">Figure 12
<p>Confocal laser scanning for bright field and fluorescence imaging in Cath-a-differentiated cells (<b>a</b>) Cath-a-differentiated cells were incubated with <b>RdN</b> (10 µM) for 30 min at 37 °C. (<b>b</b>) The bright-field image of cells is shown in panel a. (<b>c</b>) Fluorescent images of cells with 10 µM <b>RdN</b> and further incubated with Pb<sup>2+</sup> (10 µM) for 30 min at 37 °C. (<b>d</b>) an overlay image of (<b>b</b>,<b>c</b>).</p>
Full article ">Figure 13
<p>Confocal laser scanning for bright field and fluorescence imaging in Cath-a-differentiated cells (<b>a</b>) Cath-a-differentiated cells were incubated with <b>RdN</b> (10 µM) for 30 min at 37 °C. (<b>b</b>) The bright-field image of cells is shown in panel a. (<b>c</b>) Fluorescent images of cells with 10 µM <b>RdN</b> and incubated with Cu<sup>2+</sup> (10 µM) for 30 min at 37 °C. (<b>d</b>) an overlay image of (<b>b</b>,<b>c</b>).</p>
Full article ">Scheme 1
<p>Microwave irradiation-assisted synthesis of <b>RdN</b>.</p>
Full article ">Scheme 2
<p>The 1:2 binding stoichiometry of lead/copper ions and reversibility of CN<sup>−</sup> on <b>RdN</b>-cation complex.</p>
Full article ">Scheme 3
<p>Optimized Equilibrium conformers <b>RdN I</b> and <b>RdN II</b> of Sensor <b>RdN</b> in the gas state and both simulated water and acetonitrile.</p>
Full article ">
22 pages, 5146 KiB  
Review
Active Polymers Decorated with Major Acid Groups for Water Treatment: Potentials and Challenges
by Avneesh Kumar and Dong Wook Chang
Polymers 2025, 17(1), 29; https://doi.org/10.3390/polym17010029 - 26 Dec 2024
Viewed by 418
Abstract
Polymers exhibiting ion-conduction capabilities are essential components of water-purifying devices. These polymers not only transport selective ions but are also mechanically robust; thus, they can be processed as membranes. In this review, we highlight major acidic polymers and their engineered morphologies and optimized [...] Read more.
Polymers exhibiting ion-conduction capabilities are essential components of water-purifying devices. These polymers not only transport selective ions but are also mechanically robust; thus, they can be processed as membranes. In this review, we highlight major acidic polymers and their engineered morphologies and optimized properties, including metal selectivity and water permeation or retention. Crucial phenomena, such as self-assembly in acid-group-functionalized polymers for driving water transportation, are discussed. It was observed that the phosphonic acid groups containing polymers are rather suitable for the selective adsorption of toxic metals, and thus, are superior to their sulfonated counterparts. Additionally, due to their amphoteric nature, phosphonated polymers displayed several modes of metal complexations, which makes them appropriate for eliminating a wide range of metals. Further observation indicates that aromatic-acid-functionalized polymers are more durable. Temperature- and pH-responsive polymers were also found to be promising candidates for a controlled water-treatment process. Nevertheless, considering the morphology, water retention, and metal adsorption, acid-functionalized polymers, especially phosphonated ones, have the potential to remain as the materials of choice after additional advancements. Further perspectives regarding improvements in acidic polymers and their fabricated membranes for water treatment are presented. Full article
(This article belongs to the Special Issue Advanced Polymer Materials for Water and Wastewater Treatment)
Show Figures

Figure 1

Figure 1
<p>Ionic polymers as a medium (beads or membrane) in which they can acquire a suitable superstructure that can facilitate a favorable water flux in which the toxic metal ions from the water are adsorbed by the medium; thus, the water is purified. These polymeric membranes have ionic channels and suitable thermal/mechanical properties for long-term usage.</p>
Full article ">Figure 2
<p>Representative examples of synthetic and bio-based sulfonated, phosphonated, and carboxylated polymers used as ionic or acidic precursor to fabricate their products for water treatment. Among these functional polymers, the sulfonated derivatives display a higher ionic dissociation but lower selectivity toward a specific metal. The water retention power of each polymer is directly related to the nature of the acidic groups.</p>
Full article ">Figure 3
<p>Widely used methods for casting membranes from respective polymeric precursors. Few processes are implemented to form beads or capsules of the ionic polymer. (<b>A</b>) A polymeric membrane can be fabricated by polymerizing (interfacial polymerization) the monomer at the interface of the organic–aqueous phase in which the nanocapsules with aligned polymer chains are deposited on a porous substrate. (<b>B</b>) Polymeric solution is deposited on a substrate, and a free-standing film or membrane can be obtained by evaporating the solvent either via precipitation in a non-solvent (deionized water) or under controlled heat. (<b>C</b>) Industrial methods, such as solvent-free extrusion of a polymer in its molten state, can also generate aligned fibers in a membrane. (<b>D</b>) An advanced version of extrusion involves applying an electric field (high-voltage DC) via which the fibers of the polymer can be produced on a substrate to cast a membrane as the final product.</p>
Full article ">Figure 4
<p>Biomaterial- and artificial-polymer-based sulfonated membranes and fibers for water treatment. (<b>a</b>,<b>b</b>) Artistic view of a membrane and fibers made up of sulfonated cellulose producing a porous structure through which water can pass and the metallic ions can chelate with the sulfonic acid groups. (<b>c</b>) Polymeric covalent organic frameworks fabricated as a membrane for water purification. (<b>d</b>) Ion-exchange performance of a sulfonated cellulose membrane. (<b>e</b>) Different modes of metal-ion chelation with the sulfonic acid group. (<b>f</b>) Membrane based on high-performance polyamide and metal adsorption from polluted water. Adapted with permission from <span class="html-italic">Adv. Sustainable Syst.</span> [<a href="#B91-polymers-17-00029" class="html-bibr">91</a>], Copyright 2022 Wiley-VCH GmbH. This is an open access article. Reprinted with permission from <span class="html-italic">npj Clean Water</span> [<a href="#B94-polymers-17-00029" class="html-bibr">94</a>], Copyright 2023 Nature Portfolio. This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution, and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate whether changes were made. Adapted with permission from <span class="html-italic">ACS Appl. Polym. Mater.</span> [<a href="#B96-polymers-17-00029" class="html-bibr">96</a>], Copyright 2022 American Chemical Society.</p>
Full article ">Figure 5
<p>(<b>a</b>) Artistic view of a representative membrane or water-purification system based on polymers containing phosphonic acid groups. (<b>b</b>) Chemical structure of an ionic polymer used for removing metals from water. (<b>c</b>,<b>d</b>) Biopolymer (functionalized chitosan)-based assemblies for eliminating metals from water. (<b>e</b>) Metal-ion adsorption and selectivity of a (<b>f</b>) phosphonated covalent organic framework with well-defined pores and a programed architecture. Adapted with permission from <span class="html-italic">Carbohydrate Polymers</span> [<a href="#B102-polymers-17-00029" class="html-bibr">102</a>], Copyright 2021 Elsevier Ltd., and [<a href="#B106-polymers-17-00029" class="html-bibr">106</a>], Copyright 2019 CCS Chem.</p>
Full article ">Figure 6
<p>Examples of a few polymers containing major carboxylic acid groups and covalent organic frameworks for water purification. (<b>a</b>) Crosslinked polyacrylic system with an artistic picture of the membrane, and (<b>b</b>) metal-ion adsorption tests on a crosslinked membrane. (<b>c</b>) Chemical structure of crosslinked resin consisting of poly(iminodiacetic acid) and poly(glycidyl methacrylate). (<b>d</b>) Carbohydrate-based pH-responsive membrane for water purification, and (<b>e</b>) carboxylated, precisely functionalized, and ordered covalent organic frameworks with a porous network of nanochannels. (<b>f</b>) Various modes of interaction between the metal and carboxylic acid group. Adapted with permission from the <span class="html-italic">Journal of Environmental Sciences</span> [<a href="#B111-polymers-17-00029" class="html-bibr">111</a>], Copyright 2018 Elsevier Ltd.; <span class="html-italic">ACS Cent. Sci.</span> [<a href="#B117-polymers-17-00029" class="html-bibr">117</a>], Copyright 2024, American Chemical Society; and <span class="html-italic">Journal of Membrane Science</span> [<a href="#B118-polymers-17-00029" class="html-bibr">118</a>], Copyright 2020 Elsevier B.V.</p>
Full article ">Figure 7
<p>Correlations between the various properties and functions of an acidic-group-bearing polymer fabricated as a membrane for water treatment. These properties must not be compromised when designing a new polymer. Therefore, further advancements are still needed to obtain a polymeric system, in which all the properties are combined in a holistic approach to achieve the highest performance for a water-filtering device.</p>
Full article ">
13 pages, 4507 KiB  
Article
A Mechanical–Electrochemical Dual-Model E-Skin for the Monitoring of Cardiovascular Healthcare
by Jianxiao Fang, Yunting Jia, Zelong Liao, Bairui Qi and Tao Huang
Biosensors 2025, 15(1), 5; https://doi.org/10.3390/bios15010005 - 26 Dec 2024
Viewed by 167
Abstract
The early monitoring of cardiovascular biomarkers is essential for the prevention and management of some cardiovascular diseases. Here, we present a novel, compact, and highly integrated skin electrode as a mechanical–electrochemical dual-model E-skin, designed for the real-time monitoring of heart rate and sweat [...] Read more.
The early monitoring of cardiovascular biomarkers is essential for the prevention and management of some cardiovascular diseases. Here, we present a novel, compact, and highly integrated skin electrode as a mechanical–electrochemical dual-model E-skin, designed for the real-time monitoring of heart rate and sweat ion concentration, two critical parameters for assessing cardiovascular health. As a pressure sensor, this E-skin is suitable for accurate heart rate monitoring, as it exhibits high sensitivity (25.2 pF·kPa−1), a low detection limit of 6 Pa, and a rapid response time of ~20 ms, which is attributed to the iontronic sensing interface between the skin and the electrode. Additionally, the electrode functions as a potassium ion-selective electrode based on chemical doping, achieving an enhanced response of 11 mV·mM−1. A test based on the real-time monitoring of a subject riding an indoor bike demonstrated the device’s capability to monitor heart rate and sweat potassium ion levels reliably and accurately. This advancement in wearable technology offers significant potential for enhancing patient care based on the early detection and proactive management of cardiovascular conditions. Full article
Show Figures

Figure 1

Figure 1
<p>Brief introduction and working principle of DMSE-skin. (<b>a</b>) Schematic description of DMSE-skin’s structure and its possible usage in CVD monitoring; (<b>b</b>) photos showing the DMSE-skin on the skin and the thickness of different layers; (<b>c</b>) working principles of mechano-sensing for pulse and electrochemical sensing for K<sup>+</sup> recording.</p>
Full article ">Figure 2
<p>Mechano-sensing performance. (<b>a</b>) Diagram showing the sensing iontronic structure; (<b>b</b>) Δ<span class="html-italic">C</span>-<span class="html-italic">P</span> response curve of this sensor; (<b>c</b>) limit of detection (~6 Pa); (<b>d</b>) response time and recovery time; (<b>e</b>) change rate of sensitivity before and after rubbing with sandpaper; (<b>f</b>) change rate of sensitivity under 0°, 45°, and 90° bending angle on finger skin; (<b>g</b>) variation in sensitivity of sensors on the dry and sweaty finger skin; (<b>h</b>) cyclic loading–unloading of Δ<span class="html-italic">C</span>-<span class="html-italic">P</span> response under 3 kPa.</p>
Full article ">Figure 3
<p>Potassium ion sensing performance. (<b>a</b>) Diagram illustrating the K<sup>+</sup> sensing mechanism; (<b>b</b>) potential variation versus time curves of PEDOT:PSS-WPU-Valino, PEDOT:PSS-WPU, and Pt electrode in PBS solution with different addition of K<sup>+</sup>; (<b>c</b>) fitted potential variation versus log K<sup>+</sup> concentration; (<b>d</b>) FT-IR results of valinomycin before and after absorption of K<sup>+</sup>; (<b>e</b>) Bode plot and (<b>f</b>) Nyquist plot of PEDOT:PSS-WPU-Valino, PEDOT:PSS-WPU, and Pt electrodes; (<b>g</b>) enlarged nyquist plot of PEDOT:PSS-WPU-Valino electrode.</p>
Full article ">Figure 4
<p>Immunity from the interference of DMSE-skin. (<b>a</b>) Long-time K<sup>+</sup> response stability of the sensor; (<b>b</b>) repeatability under different K<sup>+</sup> concentrations during perspiration; (<b>c</b>) potential variation in different periods of exercise; (<b>d</b>) potential responses of the sensor with pressing every 5 s; (<b>e</b>) signal-to-noise ratio of signals generated by sweat and pressing; (<b>f</b>) signal under different bending angle; (<b>g</b>) enlarged view of pulse wave signal under different bending angle.</p>
Full article ">Figure 5
<p>Application of DMSE-skin. (<b>a</b>) Photos of the sensor on fingertip under different preload. The inserting showing the ideal curve for a single pulse wave and the AIr for future cardiovascular analysis; (<b>b</b>) the pulse wave signal under different preload conditions; (<b>c</b>) AIr analysis of different preload conditions; (<b>d</b>) photos showing the test environment of the real-time exercising; (<b>e</b>) the real-time potassium ion responses and the pulse wave signal with the 40 min exercising and rest.</p>
Full article ">
18 pages, 4856 KiB  
Article
Performance and Mechanism of In Situ Prepared NF@CoMnNi-LDH Composites to Activate PMS for Degradation of Enrofloxacin in Water
by Yiqiong Yang, Yubin Zhang, Xuyang Gao, Zitong Yang, Haozhou Wang and Xiaodong Zhang
Water 2025, 17(1), 24; https://doi.org/10.3390/w17010024 - 26 Dec 2024
Viewed by 173
Abstract
To overcome the disadvantage of difficult recovery of powder catalysts and improve catalyst utilization, the selection of foam metal substrates as supports can reduce the difficulty of material recovery and effectively inhibit the leaching of metal ions. Herein, CoMnNi-layered double hydroxide (LDH) derived [...] Read more.
To overcome the disadvantage of difficult recovery of powder catalysts and improve catalyst utilization, the selection of foam metal substrates as supports can reduce the difficulty of material recovery and effectively inhibit the leaching of metal ions. Herein, CoMnNi-layered double hydroxide (LDH) derived from Co-Mn ZIF was immobilized onto nickel foam (NF) through in situ synthesis. The results of XRD and SEM analyses of the samples indicated that the LDH was successfully grown on the nickel foam matrix, and the material could maintain its original morphology to the maximum extent after loading. By comparing the XPS of the material before and after the reaction, it was confirmed that the surface hydroxyl group and C=O of the material were involved in the activation of peroxymonosulfate (PMS). The results of the quenching reaction showed that SO4•− and 1O2 are the main active substances in the oxidation of enrofloxacin (ENR). When the dosage of NF@CoMnNi-LDH was 0.4 g/L, the pH of the solution was 6.82, and when the dosage of PMS was 2.0 mM, the degradation rate of ENR reached 82.6% within 30 min. This research offers novel insights into the degradation of antibiotics from water using a monolithic catalyst supported by metal foam. Full article
Show Figures

Figure 1

Figure 1
<p>Schematic diagram of the preparation of NF@CoMnNi-LDH.</p>
Full article ">Figure 2
<p>XRD patterns (<b>a</b>) and FT-IR spectra (<b>b</b>) of different LDHs/NF.</p>
Full article ">Figure 3
<p>SEM images of NF (<b>a</b>–<b>d</b>), NF@CoMnNi-LDH (<b>e</b>–<b>h</b>), EPX (<b>i</b>) and elemental mapping images of NF@CoMnNi-LDH (<b>j</b>–<b>p</b>).</p>
Full article ">Figure 4
<p>XPS spectra of NF@CoMnNi-LDH: full-spectrum scans (<b>a</b>), Co 2p (<b>b</b>), Mn 2p (<b>c</b>), Ni 2p (<b>d</b>), O 1s (<b>e</b>) and C 1s (<b>f</b>).</p>
Full article ">Figure 5
<p>Degradation efficiency of ENR by (<b>a</b>) different catalysts/nickel foam activated PMS and (<b>b</b>) different metals (Fe, Al, Zn, Ni) (catalysts = 0.4 g/L, ENR = 50 mg/L, PMS = 2 mM); the error bar represents the standard deviation.</p>
Full article ">Figure 6
<p>Effect of different oxidants (<b>a</b>), catalyst dosing (<b>b</b>), PMS dose (<b>c</b>) and pH (<b>d</b>) on the degradation of ENR (experimental conditions: ENR = 50 mg/L, PMS = 2 mM, M-Co-Mn-Ni/NF = 0.4 g/L, initial pH = 6.76); the error bar represents the standard deviation.</p>
Full article ">Figure 7
<p>Effects of inorganic ions H<sub>2</sub>PO<sub>4</sub><sup>−</sup>, HCO<sub>3</sub><sup>−</sup>, NO<sub>3</sub><sup>−</sup>, Cl<sup>−</sup>, CO<sub>3</sub><sup>2−</sup> and SO<sub>4</sub><sup>2−</sup> on the degradation of enrofloxacin by NF@CoMnNi-LDH-activated PMS; the error bar represents the standard deviation.</p>
Full article ">Figure 8
<p>Effects of organic (<b>a</b>) and different water bodies (<b>b</b>) on the degradation of enrofloxacin by NF@CoMnNi-LDH/PMS; the error bar represents the standard deviation.</p>
Full article ">Figure 9
<p>Radical trapping experiments of NF@CoMnNi-LDH/PMS system (<b>a</b>), first-order kinetic constants of ENR degradation (<b>b</b>) and contribution of various active species in different reaction systems (<b>c</b>).</p>
Full article ">Figure 10
<p>XPS spectra of NF@CoMnNi-LDH before and after the reaction: full-spectrum scans (<b>a</b>), Co 2p (<b>b</b>), Mn 2p (<b>c</b>), Ni 2p (<b>d</b>), O 1s (<b>e</b>) and C 1s (<b>f</b>).</p>
Full article ">Figure 10 Cont.
<p>XPS spectra of NF@CoMnNi-LDH before and after the reaction: full-spectrum scans (<b>a</b>), Co 2p (<b>b</b>), Mn 2p (<b>c</b>), Ni 2p (<b>d</b>), O 1s (<b>e</b>) and C 1s (<b>f</b>).</p>
Full article ">Figure 11
<p>The mechanism of ENR degradation by NF@CoMnNi-LDH.</p>
Full article ">Figure 12
<p>Possible degradation path of ENR in the NF@CoMnNi-LDH/PMS system.</p>
Full article ">Figure 13
<p>Acute toxicity (<b>a</b>), bioaccumulation factor (<b>b</b>), developmental toxicity (<b>c</b>) and mutagenicity (<b>d</b>) of ENR and intermediates in the NF@CoMnNi-LDH/PMS system.</p>
Full article ">Figure 14
<p>Degradation efficiency of different antibiotics by NF@CoMnNi-LDH catalyst-activated PMS (<b>a</b>,<b>b</b>).</p>
Full article ">
22 pages, 20237 KiB  
Article
Essential Oils from Citrus Peels Promote Calcium Overload-Induced Calcicoptosis in U251 Cells
by Yurong Li, Juanjuan Wei, Zimao Ye, Chen Ji, Wenji Li, Li Xu and Zhiqin Zhou
Antioxidants 2025, 14(1), 11; https://doi.org/10.3390/antiox14010011 - 25 Dec 2024
Viewed by 174
Abstract
Citrus peel essential oils (CPEOs) have demonstrated substantial medicinal potential for glioblastoma treatment because of their extensive antitumor effects, low potential for drug resistance, and ability to cross the human blood–brain barrier. In this study, the chemical compositions of five CPEOs were analyzed [...] Read more.
Citrus peel essential oils (CPEOs) have demonstrated substantial medicinal potential for glioblastoma treatment because of their extensive antitumor effects, low potential for drug resistance, and ability to cross the human blood–brain barrier. In this study, the chemical compositions of five CPEOs were analyzed via gas chromatography–mass spectrometry (GC-MS). CCK8 assays were used to evaluate the ability of five CPEOs to inhibit U251 human glioblastoma cells, and XLB and RA were selected for further investigation. Through wound healing assays and cell cycle and apoptosis analyses via flow cytometry, it was revealed that these CPEOs inhibited cell migration, arrested the cell cycle at G1/G0, and induced apoptosis with similar levels of inhibition. After CPEOs treatment, the intracellular Ca2+ content and reactive oxygen species levels in U251 cells increased significantly, whereas the mitochondrial membrane potential decreased. Additionally, the antioxidant enzyme system (SOD, POD, CAT, and GR) and the nonenzymatic defense system (GSH) were inhibited, leading to an increase in lipid peroxidation. qRT–PCR indicated the significant upregulation of intracellular calcium ion signaling pathways and the upregulation of mitochondrial apoptosis-related genes. Additionally, the activation of calcicoptosis-related indicators induced by the CPEOs could be reversed by inhibitor treatment, confirming that both of the selected CPEOs inhibit tumors by activating calcicoptosis-related pathways. These findings highlight the immense potential of CPEOs in healthcare and pharmaceutical applications by not only providing a scientific basis for the potential application of CPEOs in the treatment of glioblastoma but also offering new insights for the development of novel antitumor drugs. Full article
(This article belongs to the Section Natural and Synthetic Antioxidants)
Show Figures

Figure 1

Figure 1
<p>The relative content and composition of five CPEOs. (<b>A</b>) Phenotype of five citrus fruits. (<b>B</b>) The colors of the five CPEOs. (<b>C</b>) The differences in the relative content and composition of five EOs components. FJ: FengJieQiCheng peel essential oil; JC26: JinCheng26 peel essential oil; STJ: ShaTangJu peel essential oil; XLB: XingLuBiXiYou peel essential oil; and RA: RongAnJinDan fruit peel essential oil.</p>
Full article ">Figure 2
<p>Effect of five CPEOs on the growth of U251 cells. (<b>A</b>–<b>E</b>) U251 cells were treated with various concentrations of FJ, JC26, STJ, XLB, and RA EOs for 24 h. (<b>F</b>) The control was treated with 0.5% DMSO. The data represent the mean ± SD. The green dashed line indicated a cell viability rate of 50%.</p>
Full article ">Figure 3
<p>Effect of the CPEOs on proliferation and migration in U251 cells. (<b>A</b>) XLB and RA EOs can inhibit cell proliferation. Proliferating cells and cell nuclei were stained with BeyoClick™ EdU-555 kit and Hoechst 33342. (<b>B</b>) The cell migration ability of U251 cells was determined using the wound healing assay, where the cells were treated with XLB and RA EOs in serum-free medium for 24 h. (<b>C</b>) Statistical data of migration rate (%). The concentrations of XLB40 and RA40 were 40 µg/mL, while those of XLB80 and RA80 were 80 µg/mL. CK was treated with 0.5% DMSO. The data represent the mean ± SD. Values followed by different superscripts (a,b) are significantly different (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 4
<p>Effects of the CPEOs on the U251 cells cycle. (<b>A</b>–<b>E</b>) Determination of cell cycle distribution by flow cytometry. (<b>F</b>) The proportions of cell populations in G0/G1, S, and G2/M phases after treatment with XLB and RA EOs. The concentrations of XLB40 and RA40 were 40 µg/mL, while those of XLB80 and RA80 were 80 µg/mL. CK was treated with 0.5% DMSO. The data are presented as mean ± SD. Values followed by different superscripts (a–d) are significantly different (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 5
<p>Effects of the CPEOs on U251 cell apoptosis. (<b>A</b>–<b>E</b>) Apoptotic cells were assessed by flow cytometry after Annexin V-FITC and PI staining. Q1 represents necrotic cells; Q2 represents late apoptotic cells; Q3 represents early apoptotic cells; Q4 represents viable cells. (<b>F</b>) Living cells, early and late apoptotic cell rates. The concentration of XLB40 and RA40 was 40 µg/mL, while that of XLB80 and RA80 was 80 µg/mL. CK was treated with 0.5% DMSO. The data are presented as the mean ± SD. Values followed by different superscripts (a–e) are significantly different (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 6
<p>Effects of the CPEOs on Ca<sup>2+</sup> levels, ROS generation, and the MMP in U251 cells. (<b>A</b>) The cell nuclei and intracellular Ca<sup>2+</sup> in U251 cells after CPEOs treatment were stained with DAPI (blue) and Fluo-4 AM (green), respectively. (<b>B</b>) Average fluorescence intensity of Ca<sup>2+</sup> in different treatment groups. (<b>C</b>) Using DCFH-DA (green) to stain ROS in U251 cells treated with CPEOs. (<b>D</b>) Fluorescence images of U251 incubated with JC-1 after treatment with XLB and RA EOs. (<b>E</b>) MMP quantified by measuring green fluorescence intensity and red fluorescence intensity. XLB80 = 80 µg/mL, RA80 = 80 µg/mL, XLB80 + A23187, XLB80 + NIP, RA80 + A23187, and XLB80 + NIP represents pretreatment with 10 µM of A23187 and NIP for 1.5 h before adding XLB and RA EOs. The data are presented as mean ± SD. Values followed by different superscripts (a–e) are significantly different (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 7
<p>Effects of the CPEOs on MDA (<b>A</b>); GSH levels (<b>B</b>); and GR (<b>C</b>), POD (<b>D</b>), SOD (<b>E</b>), and CAT (<b>F</b>) activities in U251 cells. XLB80 = 80 µg/mL, RA80 = 80 µg/mL, XLB80 + A23187, XLB80 + NIP, RA80 + A23187, and XLB80 + NIP represents pretreatment with 10 µM of A23187 and NIP for 1.5 h before adding XLB and RA EOs. The data are presented as mean ± SD. Values followed by different superscripts (a–f) are significantly different (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 8
<p>Effect of the CPEOs on the expression of the <span class="html-italic">CHRNA7</span> (<b>A</b>), <span class="html-italic">MICU1</span> (<b>B</b>), <span class="html-italic">MICU2</span> (<b>C</b>), <span class="html-italic">BAX</span> (<b>D</b>), <span class="html-italic">Caspase-9</span> (<b>E</b>), <span class="html-italic">Caspase-7</span> (<b>F</b>), and <span class="html-italic">Caspase-3</span> (<b>G</b>) in U251 cells. XLB80 = 80 µg/mL, RA80 = 80 µg/mL, XLB80 + A23187, XLB80 + NIP, RA80 + A23187, and XLB80 + NIP represents pretreatment with 10 µM of A23187 and NIP for 1.5 h before adding XLB and RA EOs. The data are presented as mean ± SD. Values followed by different superscripts (a–g) are significantly different (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">
17 pages, 481 KiB  
Article
Angular Distributions and Polarization of Fluorescence in an XUV Pump–XUV Probe Scheme
by Cristian Iorga and Viorica Stancalie
Atoms 2025, 13(1), 1; https://doi.org/10.3390/atoms13010001 - 24 Dec 2024
Viewed by 15
Abstract
This work provides theoretical calculations of fluorescence angular distribution and polarization within an XUV pump–XUV probe scheme designed for determining ultra-short lifetimes of highly charged heavy ions. The initial pumping leads to a non-zero alignment in the excited levels. After the probing stage, [...] Read more.
This work provides theoretical calculations of fluorescence angular distribution and polarization within an XUV pump–XUV probe scheme designed for determining ultra-short lifetimes of highly charged heavy ions. The initial pumping leads to a non-zero alignment in the excited levels. After the probing stage, the anisotropies in angular distribution and polarization of subsequent fluorescence are significantly enhanced due to the existence of a previous alignment. Furthermore, two-photon sequential excitation from a ground state with zero angular momentum to a level with angular momentum one by two aligned linearly polarized photon beams is strictly prohibited by the selection rules and may be used as a diagnostic tool to determine beam misalignment. The present approach is based on the density matrix and statistical tensor framework. We provide the analytical form for the alignment parameters caused by successive photoexcitation either with linearly polarized photon beams, or with unpolarized photons. The analytical results can generally be used to compute angular distribution asymmetry parameters and linear polarization of subsequent fluorescence for a large array of atomic systems used in pump–probe experiments. Full article
Show Figures

Figure 1

Figure 1
<p>The XUV pump–XUV probe scheme. Rapid photoexcitation occurs during the pumping stage <math display="inline"><semantics> <mrow> <mo>(</mo> <msub> <mi>t</mi> <mn>1</mn> </msub> <mo>)</mo> </mrow> </semantics></math> followed by fluorescence emission during the controllable temporal delay period <math display="inline"><semantics> <mrow> <mo>(</mo> <msub> <mi>T</mi> <mi>d</mi> </msub> <mo>)</mo> </mrow> </semantics></math>. Next, another rapid photoexcitation process occurs during the probing stage <math display="inline"><semantics> <mrow> <mo>(</mo> <msub> <mi>t</mi> <mn>2</mn> </msub> <mo>)</mo> </mrow> </semantics></math>, followed by a secondary fluorescence emission <math display="inline"><semantics> <mrow> <mo>(</mo> <mi>T</mi> <mo>→</mo> <mo>∞</mo> <mo>)</mo> </mrow> </semantics></math>.</p>
Full article ">Figure 2
<p>Angular distribution of fluorescence corresponding to individual <math display="inline"><semantics> <mrow> <msubsup> <mi>J</mi> <mrow> <mi>f</mi> </mrow> <mi>e</mi> </msubsup> <mo>→</mo> <msubsup> <mi>J</mi> <mrow> <mi>r</mi> </mrow> <mi>o</mi> </msubsup> </mrow> </semantics></math> transitions with <math display="inline"><semantics> <mrow> <msubsup> <mi mathvariant="script">A</mi> <mrow> <mn>2</mn> </mrow> <mrow> <mi>U</mi> <mi>P</mi> </mrow> </msubsup> <mrow> <mo>(</mo> <msub> <mi>α</mi> <mi>b</mi> </msub> <msub> <mi>J</mi> <mi>b</mi> </msub> <mo>)</mo> </mrow> <mo>=</mo> <mn>0</mn> </mrow> </semantics></math> (<b>upper</b>) and <math display="inline"><semantics> <mrow> <msubsup> <mi mathvariant="script">A</mi> <mrow> <mn>2</mn> </mrow> <mrow> <mi>U</mi> <mi>P</mi> </mrow> </msubsup> <mrow> <mo>(</mo> <msub> <mi>α</mi> <mi>b</mi> </msub> <msub> <mi>J</mi> <mi>b</mi> </msub> <mo>)</mo> </mrow> <mo>=</mo> <mstyle scriptlevel="0" displaystyle="true"> <mfrac> <mn>1</mn> <msqrt> <mn>2</mn> </msqrt> </mfrac> </mstyle> </mrow> </semantics></math> (<b>lower</b>) intermediate alignment, respectively. The values for asymmetry parameters <math display="inline"><semantics> <msub> <mi>β</mi> <mn>2</mn> </msub> </semantics></math> are written explicitly together with the transition type.</p>
Full article ">Figure 3
<p>Linear polarization of fluorescence corresponding to individual <math display="inline"><semantics> <mrow> <msubsup> <mi>J</mi> <mrow> <mi>f</mi> </mrow> <mi>e</mi> </msubsup> <mo>→</mo> <msubsup> <mi>J</mi> <mrow> <mi>r</mi> </mrow> <mi>o</mi> </msubsup> </mrow> </semantics></math> transitions with <math display="inline"><semantics> <mrow> <msubsup> <mi mathvariant="script">A</mi> <mrow> <mn>2</mn> </mrow> <mrow> <mi>U</mi> <mi>P</mi> </mrow> </msubsup> <mrow> <mo>(</mo> <msub> <mi>α</mi> <mi>b</mi> </msub> <msub> <mi>J</mi> <mi>b</mi> </msub> <mo>)</mo> </mrow> <mo>=</mo> <mn>0</mn> </mrow> </semantics></math> (<b>upper</b>) and <math display="inline"><semantics> <mrow> <msubsup> <mi mathvariant="script">A</mi> <mrow> <mn>2</mn> </mrow> <mrow> <mi>U</mi> <mi>P</mi> </mrow> </msubsup> <mrow> <mo>(</mo> <msub> <mi>α</mi> <mi>b</mi> </msub> <msub> <mi>J</mi> <mi>b</mi> </msub> <mo>)</mo> </mrow> <mo>=</mo> <mstyle scriptlevel="0" displaystyle="true"> <mfrac> <mn>1</mn> <msqrt> <mn>2</mn> </msqrt> </mfrac> </mstyle> </mrow> </semantics></math> (<b>lower</b>) intermediate state alignment, respectively. The black line represents the null polarization axis. The values for linear polarization at <math display="inline"><semantics> <mrow> <mi>π</mi> <mo>/</mo> <mn>2</mn> </mrow> </semantics></math> angle with respect to the pump and probe pulse directions are given by parameter <math display="inline"><semantics> <msubsup> <mi mathvariant="double-struck">P</mi> <mrow> <mn>1</mn> </mrow> <mrow> <mi>U</mi> <mi>P</mi> </mrow> </msubsup> </semantics></math> for all transition types.</p>
Full article ">
24 pages, 2494 KiB  
Article
The Impact of Oxford Nanopore Technologies Based Methodologies on the Genome Sequencing and Assembly of Romanian Strains of Drosophila suzukii
by Attila Cristian Ratiu, Adrian Ionascu and Nicoleta Denisa Constantin
Insects 2025, 16(1), 2; https://doi.org/10.3390/insects16010002 - 24 Dec 2024
Viewed by 41
Abstract
Background: Drosophila suzukii is a worldwide invasive species with serious economic impacts. Herein, we are presenting the first project of sequencing and assembling the whole genomes of two lines of D. suzukii derived from Romanian local populations using exclusively Oxford Nanopore Technologies data. [...] Read more.
Background: Drosophila suzukii is a worldwide invasive species with serious economic impacts. Herein, we are presenting the first project of sequencing and assembling the whole genomes of two lines of D. suzukii derived from Romanian local populations using exclusively Oxford Nanopore Technologies data. Methods: We implemented both MinION and Flongle flow-cells and tested the impact of various basecalling models and assembly strategies on the quality of the sought-after representative genome assemblies. Results: We demonstrate that the sup-basecalling model significantly improved the read quality and that adding a relatively small collection of reads had a significant positive impact over the assembly quality. The novel dScaff bioinformatics prototype tool allowed us to perform sequence-level quality tests, as well as to represent assembly selections and display both the contig redundancy and the repeats-enriched genomic sub-sequences. Moreover, we used dScaff to propose a minimal assembly variant corresponding to one of our lines, GB-ls-coga4, which assured a basic linear coverage of the genome and exhibited quality parameters comparable with those particular to the current reference genome assembly. Conclusions: The study presents the first sequencing and assembly of a D. suzukii line in Romania and argues the efficiency of long-read sequencing strategies. Full article
(This article belongs to the Section Insect Molecular Biology and Genomics)
Show Figures

Figure 1

Figure 1
<p>Trap design used for <span class="html-italic">D. suzukii</span> collection and the corresponding locations of trap placement. The two locations (upper, Research Development Institute for Plant Protection (ICDPP) at 44°30′07.0″ N 26°04′11.4″ E; lower, “Dimitrie Brândză” Botanical Garden at 44°26′19.6″ N 26°03′43.2″ E) are separated by various natural and artificial barriers, such as water flows and urban architecture. Created with <a href="http://BioRender.com" target="_blank">BioRender.com</a> (accessed on 23 December 2024).</p>
Full article ">Figure 2
<p>Boxplot of log<sub>2</sub> transformed number of reads corresponding to the GB-ls-coga4 sequencing experiment with a Phred Q score higher than the threshold of 7, 10, or 15 obtained from either fast or sup-basecalling models. Statistical significance is shown as *** for <span class="html-italic">p</span> ≤ 0.001 or **** for <span class="html-italic">p</span> &lt; 0.0001 based on paired two-sample Student’s <span class="html-italic">t</span> tests. Boxplots were created in R (version 4.3.0), and the collage was created with <a href="http://BioRender.com" target="_blank">BioRender.com</a> (accessed on 23 November 2024).</p>
Full article ">Figure 3
<p>The figure represents the selection of contigs that were mapped on the NW_023496808.1 scaffold from the 2R chromosome. (<b>A</b>) depicts the contigs pertaining to GB-ls-coga4_sup assembly, while (<b>B</b>) depicts the contigs particular to GB-ls-coga4_all. Some gene-queries contained repetitive genomic sequences that could be found within more than one contig (blue hits). Since the overall number of blue hits can be a measure of redundant genomic information, the comparative graphics show how the FLO-FLG114 positively influenced the redundancy of GB-ls-coga4_all. The collage was created with <a href="http://BioRender.com" target="_blank">BioRender.com</a> (accessed on 23 November 2024).</p>
Full article ">Figure 4
<p>Comparison of results obtained with dScaff when gene-queries (<b>A</b>) and ranked-queries (<b>B</b>) were employed in order to sort the contigs from GB-ls-coga4_all that match the NW_023496808.1 scaffold. In (<b>A</b>), the left or smaller genomic coordinate is 6,819,396, while in (<b>B</b>), the corresponding coordinate is 6,813,001. Starting approximately from the 7,353,001 genomic coordinates (vertical orange line), the scaffold seems to be particularly rich in sequence repeats, a feature that is highlighted especially when ranked-queries are used. The collage was created with <a href="http://BioRender.com" target="_blank">BioRender.com</a> (accessed on 23 November 2024).</p>
Full article ">Figure 5
<p>The automatic graphical output for the minimal scaffold corresponding to the 2R chromosome of the GB-ls-coga4 genotype. The contigs name and mapping relative to the reference chromosome are presented on the <span class="html-italic">Y-</span> and <span class="html-italic">X</span>-axis, respectively. In addition, an approximate estimation of the linear chromosomal coverage of 90.346% is provided on the upper line.</p>
Full article ">Figure 6
<p>Schematic representations of the pipeline implemented for obtaining optimal assembly quality. The red boxes mark the basecalling model and the assembly with the highest qualities. Starting from the best assembly, we generated a minimal complete assembly using dScaff (indicated by the red arrow). Created with <a href="http://BioRender.com" target="_blank">BioRender.com</a> (accessed on 19 December 2024).</p>
Full article ">
25 pages, 11825 KiB  
Article
Analytical Solutions and Computer Modeling of a Boundary Value Problem for a Nonstationary System of Nernst–Planck–Poisson Equations in a Diffusion Layer
by Savva Kovalenko, Evgenia Kirillova, Vladimir Chekanov, Aminat Uzdenova and Mahamet Urtenov
Mathematics 2024, 12(24), 4040; https://doi.org/10.3390/math12244040 - 23 Dec 2024
Viewed by 199
Abstract
This article proposes various new approximate analytical solutions of the boundary value problem for the non-stationary system of Nernst–Planck–Poisson (NPP) equations in the diffusion layer of an ideally selective ion-exchange membrane at overlimiting current densities. As is known, the diffusion layer in the [...] Read more.
This article proposes various new approximate analytical solutions of the boundary value problem for the non-stationary system of Nernst–Planck–Poisson (NPP) equations in the diffusion layer of an ideally selective ion-exchange membrane at overlimiting current densities. As is known, the diffusion layer in the general case consists of a space charge region and a region of local electroneutrality. The proposed analytical solutions of the boundary value problems for the non-stationary system of Nernst–Planck–Poisson equations are based on the derivation of a new singularly perturbed nonlinear partial differential equation for the potential in the space charge region (SCR). This equation can be reduced to a singularly perturbed inhomogeneous Burgers equation, which, by the Hopf–Cole transformation, is reduced to an inhomogeneous singularly perturbed linear equation of parabolic type. Inside the extended SCR, there is a sufficiently accurate analytical approximation to the solution of the original boundary value problem. The electroneutrality region has a curvilinear boundary with the SCR, and with an unknown boundary condition on it. The article proposes a solution to this problem. The new analytical solution methods developed in the article can be used to study non-stationary boundary value problems of salt ion transfer in membrane systems. The new analytical solution methods developed in the article can be used to study non-stationary boundary value problems of salt ion transport in membrane systems. Full article
(This article belongs to the Section Computational and Applied Mathematics)
Show Figures

Figure 1

Figure 1
<p>Distributions of cation (solid lines) and anion (dashed lines) concentrations at different times t = 0 s, 1 s, …, 20 s, calculated at a constant current density for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>b</b>).</p>
Full article ">Figure 2
<p>Distributions of the space charge density <math display="inline"><semantics> <mrow> <mi>ρ</mi> <mo>=</mo> <mi>F</mi> <mo stretchy="false">(</mo> <msub> <mi>C</mi> <mn>1</mn> </msub> <mo>−</mo> <msub> <mi>C</mi> <mn>2</mn> </msub> <mo stretchy="false">)</mo> </mrow> </semantics></math> at different times t = 0 s, 1 s, …, 20 s, calculated at a current density <math display="inline"><semantics> <mrow> <mi>I</mi> <mo>=</mo> <mn>1.5</mn> <msub> <mi>I</mi> <mrow> <mi>n</mi> <mi>p</mi> </mrow> </msub> </mrow> </semantics></math> of C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>b</b>).</p>
Full article ">Figure 3
<p>Distributions of potential (<b>a</b>,<b>c</b>) and electric field strength (<b>b</b>,<b>d</b>) at different times t = 0 s, 1 s, …, 20 s, calculated at current density for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>,<b>b</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>c</b>,<b>d</b>).</p>
Full article ">Figure 3 Cont.
<p>Distributions of potential (<b>a</b>,<b>c</b>) and electric field strength (<b>b</b>,<b>d</b>) at different times t = 0 s, 1 s, …, 20 s, calculated at current density for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>,<b>b</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>c</b>,<b>d</b>).</p>
Full article ">Figure 4
<p>Distributions of the space charge density <math display="inline"><semantics> <mrow> <mi>ρ</mi> <mo>=</mo> <mi>F</mi> <mo stretchy="false">(</mo> <msub> <mi>C</mi> <mn>1</mn> </msub> <mo>−</mo> <msub> <mi>C</mi> <mn>2</mn> </msub> <mo stretchy="false">)</mo> </mrow> </semantics></math> at different times t = 0 s, 1 s, …, 20 s, calculated at a current density for C<sub>0</sub> = 10 mol/m<sup>3</sup> (red lines), 1 mol/m<sup>3</sup> (green lines), 0.1 mol/m<sup>3</sup> (blue lines) (<b>a</b>), (<b>b</b>)—enlargement of a fragment of (<b>a</b>).</p>
Full article ">Figure 5
<p>Distributions of cation <math display="inline"><semantics> <mrow> <msub> <mi>C</mi> <mn>1</mn> </msub> </mrow> </semantics></math> (solid lines) and anion <math display="inline"><semantics> <mrow> <msub> <mi>C</mi> <mn>2</mn> </msub> </mrow> </semantics></math> (dashed lines) concentrations at different times t = 0 s, 200 s, …, 2000 s, calculated at a current density <math display="inline"><semantics> <mrow> <mi>I</mi> <mo>=</mo> <mn>0.001</mn> <msub> <mi>I</mi> <mrow> <mi>n</mi> <mi>p</mi> </mrow> </msub> <mtext> </mtext> <mi>t</mi> </mrow> </semantics></math> of C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>b</b>).</p>
Full article ">Figure 6
<p>Distributions of the space charge density at different times t = 0 s, 200 s, …, 2000 s, calculated at a current density of C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>b</b>).</p>
Full article ">Figure 7
<p>Distributions of potential <math display="inline"><semantics> <mi>φ</mi> </semantics></math> (<b>a</b>,<b>c</b>) and electric field strength <math display="inline"><semantics> <mrow> <mi>E</mi> <mo>=</mo> <mo>−</mo> <mrow> <mrow> <mo>∂</mo> <mi>φ</mi> </mrow> <mo>/</mo> <mrow> <mo>∂</mo> <mi>x</mi> </mrow> </mrow> </mrow> </semantics></math> (<b>b</b>,<b>d</b>) at different times t = 0 s, 200 s, …, 2000 s, calculated at current density <math display="inline"><semantics> <mrow> <mi>I</mi> <mo>=</mo> <mn>0.001</mn> <msub> <mi>I</mi> <mrow> <mi>n</mi> <mi>p</mi> </mrow> </msub> <mtext> </mtext> <mi>t</mi> <mtext> </mtext> </mrow> </semantics></math> for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>,<b>b</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>c</b>,<b>d</b>).</p>
Full article ">Figure 7 Cont.
<p>Distributions of potential <math display="inline"><semantics> <mi>φ</mi> </semantics></math> (<b>a</b>,<b>c</b>) and electric field strength <math display="inline"><semantics> <mrow> <mi>E</mi> <mo>=</mo> <mo>−</mo> <mrow> <mrow> <mo>∂</mo> <mi>φ</mi> </mrow> <mo>/</mo> <mrow> <mo>∂</mo> <mi>x</mi> </mrow> </mrow> </mrow> </semantics></math> (<b>b</b>,<b>d</b>) at different times t = 0 s, 200 s, …, 2000 s, calculated at current density <math display="inline"><semantics> <mrow> <mi>I</mi> <mo>=</mo> <mn>0.001</mn> <msub> <mi>I</mi> <mrow> <mi>n</mi> <mi>p</mi> </mrow> </msub> <mtext> </mtext> <mi>t</mi> <mtext> </mtext> </mrow> </semantics></math> for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>,<b>b</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>c</b>,<b>d</b>).</p>
Full article ">Figure 8
<p>Distributions of cation <math display="inline"><semantics> <mrow> <msub> <mi>C</mi> <mn>1</mn> </msub> </mrow> </semantics></math> (solid lines) and anion <math display="inline"><semantics> <mrow> <msub> <mi>C</mi> <mn>2</mn> </msub> </mrow> </semantics></math> (dashed lines) concentrations at different times t = 0.01 s, 0.02 s, 0.03 s, 0.05 s, 0.1 s, 0.15 s, 0.2 s, 0.3 s, 0.5 s, 1 s, 2 s, 5 s, 10 s, 15 s, 20 s, calculated at a potential drop of 0.5 V for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>b</b>), at a potential drop of 1 V for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>c</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>d</b>).</p>
Full article ">Figure 9
<p>Distributions of the space charge density at different times t = 0.01 s, 0.02 s, 0.03 s, 0.05 s, 0.1 s, 0.15 s, 0.2 s, 0.3 s, 0.5 s, 1 s, 2 s, 5 s, 10 s, 15 s, 20 s at a potential drop of 0.5 V for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>b</b>), at a potential drop of 1 V for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>c</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>d</b>).</p>
Full article ">Figure 9 Cont.
<p>Distributions of the space charge density at different times t = 0.01 s, 0.02 s, 0.03 s, 0.05 s, 0.1 s, 0.15 s, 0.2 s, 0.3 s, 0.5 s, 1 s, 2 s, 5 s, 10 s, 15 s, 20 s at a potential drop of 0.5 V for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>b</b>), at a potential drop of 1 V for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>c</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>d</b>).</p>
Full article ">Figure 10
<p>Distributions of cation <math display="inline"><semantics> <mrow> <msub> <mi>C</mi> <mn>1</mn> </msub> <mtext> </mtext> </mrow> </semantics></math> (solid lines) and anion <math display="inline"><semantics> <mrow> <msub> <mi>C</mi> <mn>2</mn> </msub> </mrow> </semantics></math> (dashed lines) concentrations at different times t = 0.01 s, 0.02 s, 0.03 s, 0.05 s, 0.1 s, 0.15 s, 0.1 s, 0.2 s, 0.3 s, 0.5 s, 1 s, 2 s, 3 s, 5 s, 10 s calculated at a potential scan rate of 0.1 V/s for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>b</b>).</p>
Full article ">Figure 11
<p>Distribution of space charge density at different times t = 0.1 s, 0.2 s, 0.3 s, 0.5 s, 1 … 10 s at a potential rate of 0.1 V/s for C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>b</b>).</p>
Full article ">Figure 12
<p>Schematic diagram of the diffusion layer (not to scale).</p>
Full article ">Figure 13
<p>Graph of local maxima in the intermediate region <math display="inline"><semantics> <mrow> <msub> <mi>U</mi> <mn>4</mn> </msub> <mo stretchy="false">(</mo> <mi>t</mi> <mo>,</mo> <mi>x</mi> <mo stretchy="false">)</mo> </mrow> </semantics></math> at <math display="inline"><semantics> <mrow> <mtext> </mtext> <mi>t</mi> <mo>≥</mo> <msub> <mi>t</mi> <mrow> <mi>n</mi> <mi>p</mi> </mrow> </msub> </mrow> </semantics></math>.</p>
Full article ">Figure 14
<p>Distributions of cation concentrations in the extended SCR calculated numerically (solid lines) and using the asymptotic solution (20) (dashed lines) at a current density <math display="inline"><semantics> <mrow> <mi>I</mi> <mo>=</mo> <mn>1.5</mn> <msub> <mi>I</mi> <mrow> <mi>n</mi> <mi>p</mi> </mrow> </msub> </mrow> </semantics></math> at time moments: 3 s, 4 s, 5 s, 6 s, 20 s for the initial concentration of the electrolyte solution C<sub>0</sub> = 1 mol/m<sup>3</sup> (<b>a</b>) and C<sub>0</sub> = 10 mol/m<sup>3</sup> (<b>b</b>).</p>
Full article ">
17 pages, 2243 KiB  
Article
In Situ Preparation of Silver Nanoparticles/Organophilic-Clay/Polyethylene Glycol Nanocomposites for the Reduction of Organic Pollutants
by Amina Sardi, Bouhadjar Boukoussa, Aouicha Benmaati, Kheira Chinoune, Adel Mokhtar, Mohammed Hachemaoui, Soumia Abdelkrim, Issam Ismail, Jibran Iqbal, Shashikant P. Patole, Gianluca Viscusi and Mohamed Abboud
Polymers 2024, 16(24), 3608; https://doi.org/10.3390/polym16243608 - 23 Dec 2024
Viewed by 259
Abstract
This work focuses on the preparation and application of silver nanoparticles/organophilic clay/polyethylene glycol for the catalytic reduction of the contaminants methylene blue (MB) and 4-nitrophenol (4-NP) in a simple and binary system. Algerian clay was subjected to a series of treatments including acid [...] Read more.
This work focuses on the preparation and application of silver nanoparticles/organophilic clay/polyethylene glycol for the catalytic reduction of the contaminants methylene blue (MB) and 4-nitrophenol (4-NP) in a simple and binary system. Algerian clay was subjected to a series of treatments including acid treatment, ion exchange with the surfactant hexadecyltrimethylammonium bromide (HTABr), immobilization of polyethylene glycol polymer, and finally dispersion of AgNPs. The molecular weight of polyethylene glycol was varied (100, 200, and 4000) to study its effect on the stabilization of silver nanoparticles (AgNPs) and the catalytic activity of the resulting samples. The results showed that the catalyst with the highest molecular weight of polyethylene glycol had the highest AgNP content. Catalyst mass, NaBH4 concentration, and type of catalyst were shown to have a significant influence on the conversion and rate constant. The material with the highest silver nanoparticle content was identified as the optimal catalyst for the reduction of both pollutants. The measured rate constants for the reduction of methylene blue (MB) and 4-nitrophenol (4-NP) were 164 × 10−4 s−1 and 25 × 10−4 s−1, respectively. The reduction of MB and 4-NP in the binary system showed high selectivity for MB dye, with rate constants of 64 × 10−4 s−1 and 9 × 10−4 s−1 for MB and 4-NP, respectively. The reuse of the best catalyst via MB dye reduction for four cycles showed good results without loss of performance. Full article
Show Figures

Figure 1

Figure 1
<p>XRD patterns of obtained Nano-1, Nano-2, and Nano-3 nanocomposites.</p>
Full article ">Figure 2
<p>FTIR spectra of obtained samples before and after modification.</p>
Full article ">Figure 3
<p>XPS spectra of different nanocomposites: (<b>a</b>) XPS survey spectra, (<b>b</b>) high-resolution Ag3d XPS, (<b>c</b>) high-resolution O1s XPS, and (<b>d</b>) high-resolution C1s XPS.</p>
Full article ">Figure 4
<p>Thermal analysis of different samples: (<b>a</b>) TGA curves; (<b>b</b>) DTG curves.</p>
Full article ">Figure 5
<p>TEM images of obtained Nano-1, Nano-2, and Nano-3 nanocomposites.</p>
Full article ">Figure 6
<p>(<b>a</b>–<b>c</b>) UV–vis of MB dye catalyzed by Nano-1 at different masses. (<b>d</b>) Conversion of MB dye as a function of time. (<b>e</b>) Correlation plot between Nano-1 catalyst mass and MB dye conversion. (<b>f</b>) Plot of ln(C<sub>t</sub>/C<sub>0</sub>) as a function of time.</p>
Full article ">Figure 7
<p>(<b>a</b>,<b>b</b>) UV–vis of MB dye catalyzed by Nano-1 catalyst at different concentrations of [NaBH<sub>4</sub>]. (<b>c</b>) Conversion of MB dye as a function of time. (<b>d</b>) Plot of Ln(C<sub>t</sub>/C<sub>0</sub>) as a function of time.</p>
Full article ">Figure 8
<p>(<b>a</b>–<b>c</b>) UV–vis of MB dye catalyzed by different catalysts. (<b>d</b>) Conversion of MB dye as a function of time. (<b>e</b>) Plot of Ln(C<sub>t</sub>/C<sub>0</sub>) as a function of time.</p>
Full article ">Figure 9
<p>(<b>a</b>) UV–vis of MB dye and 4-NP catalyzed by Nano-3 catalyst in binary system. (<b>b</b>) Zeta potential as a function of solution pH. (<b>c</b>) Conversion of MB dye and 4-NP as a function of time. (<b>d</b>) Plot of ln(C<sub>t</sub>/C<sub>0</sub>) as a function of time.</p>
Full article ">Figure 10
<p>Reuse of Nano-3 catalyst via MB dye reduction.</p>
Full article ">
22 pages, 3600 KiB  
Article
Crown Ether-Grafted Graphene Oxide-Based Materials—Synthesis, Characterization and Study of Lithium Adsorption from Complex Brine
by Ewa Knapik, Grzegorz Rotko, Marcin Piotrowski and Marta Marszałek
Materials 2024, 17(24), 6269; https://doi.org/10.3390/ma17246269 - 22 Dec 2024
Viewed by 277
Abstract
Direct lithium extraction from unconventional resources requires the development of effective adsorbents. Crown ether-containing materials have been reported as promising structures in terms of lithium selectivity, but data on adsorption in real, highly saline brines are scarce. Crown ether-grafted graphene oxides were synthesized [...] Read more.
Direct lithium extraction from unconventional resources requires the development of effective adsorbents. Crown ether-containing materials have been reported as promising structures in terms of lithium selectivity, but data on adsorption in real, highly saline brines are scarce. Crown ether-grafted graphene oxides were synthesized using 2-hydroxymethyl-12-crown-4, hydroxy-dibenzo-14-crown-4 and epichlorohydrin as a source of anchoring groups. The obtained carbonaceous materials were used to prepare chitosan–polyvinyl alcohol composites. The prepared materials (and intermediate products) were characterized using FTIR, XRD, Raman spectroscopy and SEM-EDS methods. Adsorption tests were performed in a pure diluted LiCl solution ([Li] = 200 mg/kg) as well as in a real, highly saline oilfield brine ([Li] ≈ 220 mg/kg), and the distribution coefficients (Kd) were determined. The obtained results show that Kd in pure LiCl solution was in the range of 0.9–75.6, while in brine it was in the range of 0.2–2.3. The study indicates that the high affinity for lithium in pure LiCl solution is mostly associated with the non-selective interaction of lithium ions with the graphene oxide matrix (COOH groups). It was also shown that the application of dibenzo-14-crown-4 moiety to graphene oxide modification groups increases the affinity of the composite material for lithium ions compared to an analogous material containing 12-crown-4-ether groups. Full article
Show Figures

Figure 1

Figure 1
<p>Reaction scheme for graphene oxide synthesis.</p>
Full article ">Figure 2
<p>Scheme of graphene oxide modification with epichlorohydrin: (<b>a</b>) the main reaction postulated in the literature, (<b>b</b>) a side reaction leading to the formation of a polyether polymer.</p>
Full article ">Figure 3
<p>Reaction scheme for hydroxy-DB14C4 synthesis.</p>
Full article ">Figure 4
<p>Reaction scheme for introduction of 12-crown-4 (<b>a</b>) and dibenzo-14-crown-4 (<b>b</b>) onto the modified GO.</p>
Full article ">Figure 5
<p>SEM images of (<b>a</b>) raw graphite; (<b>b</b>) graphene oxide; (<b>c</b>) GO modified with epichlorohydrin according to Procedure 1 (GO-Epi1); (<b>d</b>) GO modified with epichlorohydrin according to the Procedure 2 (GO-Epi2); (<b>e</b>) GO modified with epichlorohydrin and 2-hydroxymethyl-12-crown-4 according to Procedure 1 (GO-Epi1-E1); (<b>f</b>) GO modified with epichlorohydrin and 2-hydroxymethyl-12-crown-4 according to Procedure 2 (GO-Epi2-E1); (<b>g</b>) GO modified with epichlorohydrin and hydroxy-DB14C4 (GO-Epi2-E2).</p>
Full article ">Figure 6
<p>XRD patterns of raw graphite, graphene oxide (GO), GO modified with epichlorohydrin according to Procedure 1 (GO-Epi1), GO modified with epichlorohydrin according to Procedure 2 (GO-Epi2), GO modified with epichlorohydrin and 2-hydroxymethyl-12-crown-4 according to Procedure 1 (GO-Epi1-E1), GO modified with epichlorohydrin and 2-hydroxymethyl-12-crown-4 according to Procedure 2 (GO-Epi2-E1), GO modified with epichlorohydrin and hydroxy-DB14C4 (GO-Epi2-E2).</p>
Full article ">Figure 7
<p>Comparison of FTIR spectra of materials at different stages of modification: (<b>a</b>) graphene oxide modification with epichlorohydrin; (<b>b</b>) 2-Hydroxymethyl-12-crown-4 grafting on the modified graphene oxide; (<b>c</b>) hydroxy-DB14C4 grafting on the modified graphene oxide; (<b>d</b>) comparison of prepared composite materials.</p>
Full article ">Figure 8
<p>Comparison of Raman spectra of selected materials.</p>
Full article ">
25 pages, 9193 KiB  
Article
Capacity Prognostics of Marine Lithium-Ion Batteries Based on ICPO-Bi-LSTM Under Dynamic Operating Conditions
by Qijia Song, Xiangguo Yang, Telu Tang, Yifan Liu, Yuelin Chen and Lin Liu
J. Mar. Sci. Eng. 2024, 12(12), 2355; https://doi.org/10.3390/jmse12122355 - 21 Dec 2024
Viewed by 322
Abstract
An accurate prognosis of the marine lithium-ion battery capacity is significant in guiding electric ships’ optimal operation and maintenance. Under real-world operating conditions, lithium-ion batteries are exposed to various external factors, making accurate capacity prognostication a complex challenge. The paper develops a marine [...] Read more.
An accurate prognosis of the marine lithium-ion battery capacity is significant in guiding electric ships’ optimal operation and maintenance. Under real-world operating conditions, lithium-ion batteries are exposed to various external factors, making accurate capacity prognostication a complex challenge. The paper develops a marine lithium-ion battery capacity prognostic method based on ICPO-Bi-LSTM under dynamic operating conditions to address this. First, the battery is simulated according to the actual operating conditions of an all-electric ferry, and in each charge/discharge cycle, the sum, mean, and standard deviation of each parameter (current, voltage, energy, and power) during battery charging, as well as the voltage difference before and after the simulated operating conditions, are calculated to extract a series of features that capture the complex nonlinear degradation tendency of the battery, and then a correlation analysis is performed on the extracted features to select the optimal feature set. Next, to address the challenge of determining the neural network’s hyperparameters, an improved crested porcupine optimization algorithm is proposed to identify the optimal hyperparameters for the model. Finally, to prevent the interference of test data during model training, which could lead to evaluation errors, the training dataset is used for parameter fitting, the validation dataset for hyperparameter adjustment, and the test dataset for the model performance evaluation. The experimental results demonstrate that the proposed method achieves high accuracy and robustness in capacity prognostics of lithium-ion batteries across various operating conditions and types. Full article
(This article belongs to the Special Issue Advancements in Power Management Systems for Hybrid Electric Vessels)
Show Figures

Figure 1

Figure 1
<p>NEWARE CTE-4008D-5V30A tester.</p>
Full article ">Figure 2
<p>Network topology of the battery system.</p>
Full article ">Figure 3
<p>The current variation curves. (<b>a</b>) Actual condition; (<b>b</b>) simulated condition.</p>
Full article ">Figure 4
<p>Capacity degradation curves for B1, B2, and B3.</p>
Full article ">Figure 5
<p>Correlation analysis results. (<b>a</b>) Spearman’s correlation coefficients for B1; (<b>b</b>) Spearman’s correlation coefficients for B2; (<b>c</b>) gray relation coefficients for B1; and (<b>d</b>) gray relation coefficients for B2.</p>
Full article ">Figure 6
<p>Normalized optimal feature set. (<b>a</b>) Features of B1; (<b>b</b>) features of B2.</p>
Full article ">Figure 7
<p>The structure of LSTM.</p>
Full article ">Figure 8
<p>The structure of Bi-LSTM.</p>
Full article ">Figure 9
<p>The flowchart of the developed ICPO-Bi-LSTM.</p>
Full article ">Figure 10
<p>The framework of the capacity prognostic analysis based on ICPO-Bi-LSTM and feature extraction.</p>
Full article ">Figure 11
<p>Capacity prognostics for different batteries at various set ratios: (<b>a</b>) B1; (<b>b</b>) B2; and (<b>c</b>) B3.</p>
Full article ">Figure 12
<p>Capacity prognostics for different batteries using different methods. (<b>a</b>) B1; (<b>b</b>) B2; and (<b>c</b>) B3.</p>
Full article ">
14 pages, 1356 KiB  
Article
Innovative Nafion- and Lignin-Based Cation Exchange Materials Against Standard Resins for the Removal of Heavy Metals During Water Treatment
by Sara Bergamasco, Luis Alexander Hein, Laura Silvestri, Robert Hartmann, Giampiero Menegatti, Alfonso Pozio and Antonio Rinaldi
Separations 2024, 11(12), 357; https://doi.org/10.3390/separations11120357 - 21 Dec 2024
Viewed by 314
Abstract
The contamination of water by heavy metals poses an escalating risk to human health and the environment, underscoring the critical need for efficient removal methods to secure safe water resources. This study evaluated the performance of four cationic exchange materials (labeled “PS—DVB”, “PA—DVB”, [...] Read more.
The contamination of water by heavy metals poses an escalating risk to human health and the environment, underscoring the critical need for efficient removal methods to secure safe water resources. This study evaluated the performance of four cationic exchange materials (labeled “PS—DVB”, “PA—DVB”, “TFSA”, and “OGL”) in removing or harvesting metals such as copper, silver, lead, cobalt, and nickel from aqueous solutions, several of which are precious and/or classified as Critical Raw Materials (CRMs) due to their economic importance and supply risk. The objective was to screen and benchmark the four ion exchange materials for water treatment applications by investigating their metal sequestration capacities. Experiments were conducted using synthetic solutions with controlled metal concentrations, analyzed through ICP-OES, and supported by kinetic modeling. The adsorption capacities (qe) obtained experimentally were compared with those predicted by pseudo-first-order and pseudo-second-order models. This methodology enables high precision and reproducibility, validating its applicability for assessing ion exchange performance. The results indicated that PS—DVB and PA—DVB resins proved to be of “wide range”, exhibiting high efficacy for most of the metals tested, including CRM-designated ones, and suggesting their suitability for water purification. Additionally, the second-life Nafion-based “TFSA” material demonstrated commendable performance, highlighting its potential as a viable and technologically advanced alternative in water treatment. Lastly, the lignin-based material, “OGL”, representing the most innovative and sustainability apt option, offered relevant performance only in selected cases. The significant differences in performance among the resins underscore the impact of structural and compositional factors on adsorption efficiency. This study offers valuable insights for investigating and selecting new sustainable materials for treating contaminated water, opening new pathways for targeted and optimized solutions in environmental remediation. Full article
(This article belongs to the Special Issue Separation Technology for Metal Extraction and Removal)
Show Figures

Figure 1

Figure 1
<p>Photographic images of the ion exchange materials utilized: (<b>A</b>) polystyrene–divinylbenzfene resin (PS–DVB), (<b>B</b>) polyacrylic–divinylbenzene resin (PA–DVB), (<b>D</b>) regenerated Nafion granules (TFSA), and (<b>D</b>) lignin-based powder material (OGL).</p>
Full article ">Figure 2
<p>Time-dependent concentration of the available metal ions (Cu<sup>2+</sup>, Pb<sup>2+</sup>, Co<sup>2+</sup> and Ni<sup>2+</sup>) in bulk solution (ppm) examined by ICP-EOS. Each panel shows the remaining concentration of a specific metal ion over time (0, 5, 10, 20, and 40 min): (<b>A</b>) Cu<sup>2+</sup> concentration in bulk, (<b>B</b>) Pb<sup>2+</sup> concentration in bulk, (<b>C</b>) Co<sup>2+</sup> concentration in bulk, and (<b>D</b>) Ni<sup>2+</sup> concentration in bulk.</p>
Full article ">
Back to TopTop