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22 pages, 840 KiB  
Review
Advanced Optimization of Bioprocess Parameters for Exopolysaccharides Synthesis in Extremophiles
by Nadja Radchenkova and Songül Yaşar Yıldız
Processes 2025, 13(3), 822; https://doi.org/10.3390/pr13030822 - 11 Mar 2025
Abstract
Exopolysaccharides (EPSs) represent versatile biopolymers finding diverse applications in food, pharmaceuticals, and bioremediation industries. Extremophiles, thriving under extreme environmental conditions, have emerged as a promising source of novel EPSs with better stability and bioactivity. The present work reviews the complex influence of various [...] Read more.
Exopolysaccharides (EPSs) represent versatile biopolymers finding diverse applications in food, pharmaceuticals, and bioremediation industries. Extremophiles, thriving under extreme environmental conditions, have emerged as a promising source of novel EPSs with better stability and bioactivity. The present work reviews the complex influence of various abiotic factors and bioprocess parameters such as temperature, pH, carbon and nitrogen sources, C/N ratios, and oxygen transfer dynamics on the production of EPSs from extremophilic microorganisms. Results underline the important role of temperature for structural and functional properties of EPSs, from the synthesis of cryoprotective polymers in psychrophiles to the production of thermostable EPSs in thermophiles under cold stress. The pH has an extensive effect on enzymatic activities: optimal neutral to slightly acidic conditions exist for most strains. Carbon sources determine not only the yield of EPSs but also its structural features, while nitrogen sources and C/N ratios regulate the balance between biomass production and polymer biosynthesis. Besides that, oxygen transfer limitations—which may happen in particularly viscous or saline media—are overtaken by optimized bioreactor configuration and stirring strategies. These findings are highly relevant to the development of tailored cultivation conditions enabling the maximization of EPS yields and adaptation of its properties to comply with industrial requirements. This study provides a framework for enhancing EPS production by leveraging the adaptive traits of extremophiles. This approach supports the sustainable use of biopolymers, advances fermentation production processes, and helps uncover the underlying mechanisms involved. Full article
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Figure 1

Figure 1
<p>Factors affecting EPS production.</p>
Full article ">Figure 2
<p>Oxygen transfer from the gas bubbles to the cell–steps: (1) transfer from the interior of the bubble and gas film; (2) movement across the gas–liquid interface; (3) diffusion through the relatively stagnant liquid film surrounding the bubble; (4) transport through the bulk liquid; (5) diffusion through the relatively stagnant liquid film surrounding the cells; (6) movement across the liquid–cell interface; and (7) transport through the cytoplasm to the site of the biochemical reaction.</p>
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16 pages, 3113 KiB  
Article
Reactions of Plasmodium falciparum Type II NADH: Ubiquinone Oxidoreductase with Nonphysiological Quinoidal and Nitroaromatic Oxidants
by Lina Misevičienė, Marie-Pierre Golinelli-Cohen, Visvaldas Kairys, Audronė Marozienė, Mindaugas Lesanavičius and Narimantas Čėnas
Int. J. Mol. Sci. 2025, 26(6), 2509; https://doi.org/10.3390/ijms26062509 (registering DOI) - 11 Mar 2025
Abstract
In order to detail the antiplasmodial effects of quinones (Q) and nitroaromatic compounds (ArNO2), we investigated their reduction mechanism by Plasmodium falciparum flavoenzyme type II NADH:ubiquinone oxidoreductase (PfNDH2). The reactivity of Q and ArNO2 (n = 29) [...] Read more.
In order to detail the antiplasmodial effects of quinones (Q) and nitroaromatic compounds (ArNO2), we investigated their reduction mechanism by Plasmodium falciparum flavoenzyme type II NADH:ubiquinone oxidoreductase (PfNDH2). The reactivity of Q and ArNO2 (n = 29) follows a common trend and exhibits a parabolic dependence on their single-electron reduction potential (E71), albeit with significantly scattered data. The reactivity of quinones with similar E71 values increases with their lipophilicity. Quinones are reduced by PfNDH2 in a two-electron way, but ArNO2 are reduced in a single-electron way. The inhibition studies using NAD+ and ADP-ribose showed that quinones oxidize the complexes of reduced enzyme with NADH and NAD+. This suggests that, as in the case of other NDH2s, quinones and the nicotinamide ring of NAD(H) bind at separate sites. A scheme of PfNDH2 catalysis is proposed, consistent with both the observed ‘ping-pong’ mechanism and the presence of two substrate binding sites. Molecular docking showed that Q and ArNO2 bind in a similar manner and that lipophilic quinones have a higher affinity for the binding site. One may expect that PfNDH2 can be partially responsible for the previously observed enhanced antiplasmodial activity of aziridinylbenzoquinones caused by their two-electron reduction, as well as for the redox cycling and oxidative stress-type action of ArNO2. Full article
(This article belongs to the Section Biochemistry)
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Figure 1

Figure 1
<p>The structures of nontrivial oxidants used in this study. The numbers of compounds correspond to those given in <a href="#ijms-26-02509-t001" class="html-table">Table 1</a>: DZQ (<b>3</b>), MeDZQ (<b>11</b>), decylubiquinone (<b>13</b>), idebenone (<b>14</b>), and tetryl (<b>19</b>).</p>
Full article ">Figure 2
<p>(<b>A</b>) Relationship between the log <span class="html-italic">k</span><sub>cat</sub>/<span class="html-italic">K</span><sub>m</sub> of quinones (solid circles) and nitroaromatics (blank circles) and their single-electron reduction midpoint potentials at pH 7.0 (<math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>E</mi> </mrow> <mrow> <mn>7</mn> </mrow> <mrow> <mn>1</mn> </mrow> </msubsup> </mrow> </semantics></math>). Numbers and reduction potentials of compounds are given in <a href="#ijms-26-02509-t001" class="html-table">Table 1</a>. The log <span class="html-italic">k</span><sub>cat</sub>/<span class="html-italic">K</span><sub>m</sub> of the single-electron oxidant benzylviologen (31) is shown as an inverted triangle. (<b>B</b>) Relationship between the log <span class="html-italic">k</span><sub>cat</sub>/<span class="html-italic">K</span><sub>m</sub> of quinones with <math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>E</mi> </mrow> <mrow> <mn>7</mn> </mrow> <mrow> <mn>1</mn> </mrow> </msubsup> </mrow> </semantics></math> = −0.23–−0.26 V and their octanol/water distribution coefficient at pH 7.0 (log <span class="html-italic">D</span>).</p>
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<p>Steady-state kinetics of a reduction of naphthazarin by NADH catalyzed by <span class="html-italic">Pf</span>NDH2 at varied NADH concentrations. NADH concentrations: 100 μM (1), 50 μM (2), 25 μM (3), 16.7 μM (4), 12.5 μM (5), and 8.5 µM (6).</p>
Full article ">Figure 4
<p>(<b>A</b>) Kinetics of oxidation of 250 µM NADH by 50 nM <span class="html-italic">Pf</span>NDH2 in the absence of oxidant (1) and in the presence of 50 µM 2,6-dimethyl-1,4-benzoquinone at pH 7.0 (2), 50 µM 1,4-naphthoquinone at pH 5.5 (3) or pH 7.0 (4), and 50 µM naphthazarin at pH 5.5 (5) or pH 7.0 (6). (<b>B</b>) Formation of <span class="html-italic">N</span>-methylpicramide during the oxidation of 250 µM NADH by 50 µM tetryl in the presence of 50 nM <span class="html-italic">Pf</span>NDH2. The arrows show the decrease in absorbance at 340 nm due to NADH oxidation and absorbance increase at 420 nm. The spectra are recorded every 3 min. Inset shows absorbance spectrum of 50 µM <span class="html-italic">N</span>-methylpicramide.</p>
Full article ">Figure 5
<p>NAD<sup>+</sup> as a competitive to NADH inhibitor in <span class="html-italic">Pf</span>NDH2-catalyzed reactions in the presence of 50 µM naphthazarin: 1—no NAD<sup>+</sup>, 2—1.25 mM NAD<sup>+</sup>, 3—2.5 mM NAD<sup>+</sup>, 4—3.75 mM NAD<sup>+</sup>, 5—5.0 mM NAD<sup>+</sup>, 6—7.5 mM NAD<sup>+</sup>.</p>
Full article ">Figure 6
<p>NAD<sup>+</sup> as an inhibitor towards naphthazarin in the PfNDH2-catalyzed reaction. (<b>A</b>) Competitive inhibition of NAD<sup>+</sup> towards naphthazarin in the presence of 200 µM NADH: 1—no NAD<sup>+</sup>, 2—0.6 mM NAD<sup>+</sup>, 3—1.0 mM NAD<sup>+</sup>, 4—2.0 mM NAD<sup>+</sup>, 5—6.0 mM NAD<sup>+</sup>. (<b>B</b>) Dependence of inhibition efficiency on NAD<sup>+</sup> concentration at 200 μM (1), 50 μM (2), and 25 μM (3) NADH. (<b>C</b>) Dependence of the calculated NAD<sup>+</sup> binding constants (<span class="html-italic">K</span><sub>d(app)</sub>(NAD<sup>+</sup>)) on NADH concentration.</p>
Full article ">Figure 7
<p>Docked conformations of quinones in the active site of <span class="html-italic">Pf</span>NDH2: (<b>A</b>) duroquinone; (<b>B</b>) menadione; (<b>C</b>) ubiquinone-1; (<b>D</b>) decylubiquinone; (<b>E</b>) idebenone. FAD is colored magenta, NAD(H) is colored green, quinone is colored light blue. Hydrogen bonds are shown as dotted lines.</p>
Full article ">Figure 8
<p>Docked conformations of nitroaromatic compounds in the active site of <span class="html-italic">Pf</span>NDH2: (<b>A</b>) TNT; (<b>B</b>) tetryl. FAD is colored magenta, NAD(H) is colored green, nitroaromatic compound is colored light blue. Hydrogen bonds are shown as dotted lines.</p>
Full article ">Scheme 1
<p>The proposed mechanism of quinone reductase reaction of <span class="html-italic">Pf</span>NDH2.</p>
Full article ">
15 pages, 1726 KiB  
Article
Influence on the Result by Abrasion on Filter Casings, Tested in the Environment in Finnmark, Norway
by Fabio Manna, Michel Mues, Clara Wiebensohn, Maja Dukat and Andreas Fath
Microplastics 2025, 4(1), 14; https://doi.org/10.3390/microplastics4010014 - 11 Mar 2025
Abstract
The purpose of this study is to determine the plastic wear of the cartridge filter casing 01WTKF (Wolftechnik Filtersysteme GmbH & Co. KG, Weil der Stadt, Germany) when exposed to sand, sediment, and ice at temperatures below 0 °C, both in laboratory and [...] Read more.
The purpose of this study is to determine the plastic wear of the cartridge filter casing 01WTKF (Wolftechnik Filtersysteme GmbH & Co. KG, Weil der Stadt, Germany) when exposed to sand, sediment, and ice at temperatures below 0 °C, both in laboratory and field conditions. Furthermore, this study aims to discuss whether previous studies conducted with the model 01WTKF may suffer significant errors due to abrasion. The freshwater samples were collected in Finnmark, Norway. These samples were filtered using a cartridge filtration method and the 01WTKF filter casing, which features lids made of polypropylene (PP) and bottom parts made of styrene–acrylonitrile copolymer (SAN) or PP. The samples were analyzed for microplastic (MP) cross-contamination by comparing the results of the model 01WTKF to those of the stainless-steel-based model 01WTGD. Laboratory and environmental samples were examined using FT-IR spectroscopy. The results indicate that wear occurs for ice, sand, and sediment. Abrasion significantly increased the overall PP concentration in the environmental samples, introducing an error of 858 ± 516 N m−3 MPs to 2453 ± 92 N m−3 MPs. By contrast, no wear was detected for the SAN-based bottom part. For the PP-based lids, only 92 ± 83 N m−3 MPs were identified. Therefore, the use of PP-based bottom parts and lids is not recommended at temperatures below 0 °C. Additionally, studies utilizing the model 01WTKF should be reviewed and re-evaluated to ensure the accuracy of the obtained data. Full article
(This article belongs to the Collection Current Opinion in Microplastics)
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Figure 1
<p>There are different ways for microplastics to enter the environment, especially the sub-Arctic and Arctic, by atmospheric input. Therefore, different kinds of measured pollution are depicted in the illustration. The figure is adapted from AWI-Infographic, CC BY 4.0, without any changes to the graphic (<a href="https://creativecommons.org/licenses/by/4.0/" target="_blank">https://creativecommons.org/licenses/by/4.0/</a>) accessed on 12 February 2025.</p>
Full article ">Figure 2
<p>▲: mean. Comparison of sampling in the presence of ice and sand with the model 01WTKF and in the environment with the bottom part made of PP. The means amount to 2255 ± 142 N m<sup>−3</sup> for ice, 1425 ± 107 N m<sup>−3</sup> for sand, and 1690 ± 290 N m<sup>−3</sup> for environment. A significant difference (<span class="html-italic">p</span> &lt; 0.05) was found by the Kruskal–Wallis Test, and the Dunn Test confirmed a significant difference (<span class="html-italic">p</span> &lt; 0.05) for the mean of the sand samples compared to the mean of the ice samples. For the mean of the environment samples, no significant difference was confirmed.</p>
Full article ">Figure 3
<p>▲: mean. For the locations Tanaelva 1 and Bergebyelva, where the PP casings were used. The difference in PP levels without and with added cross-contamination through abrasion on the PP casings and lids is displayed. The means amount to 858 ± 516 N m<sup>−3</sup> (Figure 5A,C) for the environmental samples and 2453 ± 92 N m<sup>−3</sup> for the environmental samples with abrasion. The added cross-contaminations led to a significant difference (<span class="html-italic">p</span> &lt; 0.05) in the measurement of PP particles.</p>
Full article ">Figure 4
<p>Size comparison for MP abrasion in percentage for the categories: &lt;5 mm–1 mm, &lt;1 mm–50 µm, and &lt;50 µm–10 µm. The results show abrasion levels for the means as high as 91% for particles with a size of &lt;50 µm to 10 µm, 9% for particles with a size of &lt;1 mm–50 µm, and 0% for particles with a size of &lt;5 mm to 1 mm. There are no significant differences within the distribution groups.</p>
Full article ">Figure 5
<p>(<b>A</b>) The polymer composition for the samples taken at the locations: Báíšjohka, Tanaelva 1, and Bergebyelva. All samples rank PE as the most abundant polymer, followed by PP, PA, and PS. PET was detected only for Báíšjohka and Tanaelva 1, the latter being the only one containing EVOH. (<b>B</b>) Particle size comparison for MP abrasion in percentage. The results display the means for all locations with 91% for &lt;25 µm, 5% for &lt;1 mm–25 µm, and 4% for &lt;5 mm–1 mm. There are no significant differences within the distribution groups. (<b>C</b>) <b>▲</b>: mean. The overall particle amount for Tanaelva 1 was the highest with 2873 ± 265 N m<sup>−3</sup>, followed by Báíšjohka with 1622 ± 329 N m<sup>−3</sup> and Bergebyelva with 1297 ± 523 N m<sup>−3</sup>. The total mean for all three locations amounts to 1900 ± 779 N m<sup>−3</sup>. There are no significant differences among the three locations.</p>
Full article ">Figure 6
<p>Traced particle shapes for all three locations. The total mean for each group amounts to 81% fragments, 11% fibers, 5% foam, and 3% films. No significant differences within the groups are confirmed.</p>
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5 pages, 1473 KiB  
Short Note
(Z)-1-(3,5-Dichloro-2H-pyrrol-2-ylidene)-N,N-dimethylmethanamine
by Daniil Rykunov, Alina Sonina and Aleksey Vorob’ev
Molbank 2025, 2025(1), M1979; https://doi.org/10.3390/M1979 (registering DOI) - 11 Mar 2025
Abstract
The Vilsmeier–Haack reaction is a convenient method for the formylation of electron-rich aromatic compounds. However, this interaction sometimes gives specific side products. We report the isolation and structural characterization of a novel compound (Z)-1-(3,5-dichloro-2-pyrrolylidene)-N,N-dimethylmethanamine obtained as a [...] Read more.
The Vilsmeier–Haack reaction is a convenient method for the formylation of electron-rich aromatic compounds. However, this interaction sometimes gives specific side products. We report the isolation and structural characterization of a novel compound (Z)-1-(3,5-dichloro-2-pyrrolylidene)-N,N-dimethylmethanamine obtained as a side product during the formylation of 2-chloropyrrole. The product was characterized using NMR spectroscopy and X-ray crystallography. Full article
(This article belongs to the Collection Molecules from Side Reactions)
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Figure 1

Figure 1
<p>Molecular structure, atom and cycle numbering of product <b>1</b> with anisotropic displacement ellipsoids drawn at 50% probability level.</p>
Full article ">Figure 2
<p>Fragments of product <b>1</b> crystal structure forming (<b>a</b>) dimer between M1 molecules connected by C<sup>6</sup>-H···Cl<sup>1</sup> and C<sup>7</sup>-H···π<sup>1</sup> interactions; (<b>b</b>) chain of M1 molecules along <span class="html-italic">a</span>-axis; and (<b>c</b>) intermolecular interactions between M1 and M2 along <span class="html-italic">a</span>-axis. Dashed blue lines represent noncovalent interactions. The arrows indicate the orientation of the crystallographic axes.</p>
Full article ">Scheme 1
<p>Reaction of 2-chloropyrrole with Vilsmeier–Haack reagent.</p>
Full article ">Scheme 2
<p>Proposed mechanism of formation of product <b>1</b>.</p>
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15 pages, 1717 KiB  
Article
Enhanced Biosorption and Recovery of Copper and Zinc from Acetic Acid-Extracted Livestock Wastewater Sludge Using Baker’s Yeast
by Jung-Jeng Su, Kuang-Wei Yen and Wei-Chen Chen
Animals 2025, 15(6), 794; https://doi.org/10.3390/ani15060794 - 11 Mar 2025
Viewed by 9
Abstract
This study aims to develop a novel use of baker’s yeast in biosorption as a sustainable metal recovery process for cost-effective and practical applications in recovering copper and zinc from waste gravity-thickened sludge generated at livestock wastewater treatment facilities. The supernatant of the [...] Read more.
This study aims to develop a novel use of baker’s yeast in biosorption as a sustainable metal recovery process for cost-effective and practical applications in recovering copper and zinc from waste gravity-thickened sludge generated at livestock wastewater treatment facilities. The supernatant of the acid-extracted product was separated from the residues through centrifugation. To ensure cost efficiency, the supernatant was treated with 2N acetic acid for 24 h, with the addition of hydrogen peroxide, and used for the biosorption experiments. The filtrated supernatant was adjusted to various pH values (4.5, 5.0, and 5.5) to explore the effects of acidity on the subsequent biosorption of extracted zinc and copper by baker’s yeast. A diluted molasses solution was added to the filtrate as a carbon source to support yeast growth during the 4 h biosorption experiments. The results revealed that the removal efficiency of zinc from the filtrate by baker’s yeast was 97.3%, while the removal efficiency for copper was about 48.8% at pH 5.5 with a reaction time of 4 h. In summary, this combined approach is expected to reduce and recycle heavy metals in livestock sludge. Acetic acid with hydrogen peroxide can extract copper and zinc from the sludge, and baker’s yeast can absorb both metals from the filtrate at pH 5.5 in a 4 h reaction time. This technological innovation has the potential to transform waste management practices in the livestock industry, contributing to resource recovery and environmental sustainability. Full article
(This article belongs to the Section Animal System and Management)
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Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Schematic representation of acidic extraction and yeast biosorption for copper and zinc recovery from livestock sludge.</p>
Full article ">Figure 2
<p>Effect of varying pH levels on the removal efficiency of copper (Cu) and zinc (Zn) by yeast biosorption from the filtrated supernatant. Error bars indicate standard deviations.</p>
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<p>The remaining concentrations of phosphorus (P) and potassium (K) in the filtrated supernatant were evaluated at different pH values (4.5, 5, and 5.5) following yeast biosorption. The concentrations are expressed in mg/kg, with phosphorus represented by grey bars and potassium by white bars. Error bars indicate the standard deviation of the measurements.</p>
Full article ">Figure 4
<p>The removal efficiency of copper (Cu) and zinc (Zn) from the filtrated supernatant at pH 5.5, was evaluated at different inoculation ratios using yeast biosorption. Error bars indicate standard deviations.</p>
Full article ">Figure 5
<p>The remaining concentrations of phosphorus (P) and potassium (K) in the filtrated supernatant at pH 5.5 were measured after yeast biosorption at different inoculum ratios. The concentrations are expressed in mg/kg, with phosphorus represented by grey bars and potassium by white bars. Error bars indicate the standard deviation of the measurements.</p>
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18 pages, 4615 KiB  
Review
The Effect of Transversus Abdominis Plane Block on Pain-Related Outcomes in Kidney Transplantation: A Systematic Review with Meta-Analysis and Trial Sequential Analysis
by Dmitriy Viderman, Mina Aubakirova, Fatima Nabidollayeva, Anuar Aryngazin, Nekane Romero-Garcia, Rafael Badenes and Yerkin G. Abdildin
J. Clin. Med. 2025, 14(6), 1879; https://doi.org/10.3390/jcm14061879 - 11 Mar 2025
Viewed by 39
Abstract
Background/Objectives: Due to post-surgical discomfort in kidney transplant recipients and donors as well as opioids’ multiple side effects, alternative analgesic methods are required in renal transplant surgeries. This study aimed to evaluate the analgesic effect of the transversus abdominis plane (TAP) block [...] Read more.
Background/Objectives: Due to post-surgical discomfort in kidney transplant recipients and donors as well as opioids’ multiple side effects, alternative analgesic methods are required in renal transplant surgeries. This study aimed to evaluate the analgesic effect of the transversus abdominis plane (TAP) block versus no-block controls in kidney transplantation patients. Methods: We conducted a meta-analysis with a trial sequential analysis (TSA) of randomized controlled trials (RCTs). We searched for relevant articles in PubMed, Scopus, and the Cochrane Library published before December 2023. Protocol registration: doi.org/10.17605/OSF.IO/PMZJ4. Results: A total of 11 RCTs were included in the meta-analysis. The TAP block group had lower pain intensity on postoperative day 1 (mean difference, MD = −0.65 [−0.88, −0.42]; p < 0.00001) than the control group. However, the heterogeneity among the included studies was considerable (I2 = 93%). Subgroup meta-analysis and TSA revealed a significant pain reduction at 24 h postoperatively in donors (MD = −0.70 [−1.16, −0.24]; p = 0.003); heterogeneity was substantial (I2 = 67%). The TAP block group also had lower overall morphine consumption within 24 h (MD = −4.82 [−7.87, −1.77]; p = 0.002) and cumulative 24 h morphine use (MD = −14.13 [−23.64, −4.63]; p = 0.004); however, heterogeneity was considerable (I2 = 98% in both cases). The time to first analgesia (hours) was significantly longer in the TAP block group (MD = 5.92 h [3.63, 8.22]; p < 0.00001, n = 3). There was no significant difference between the groups in postoperative nausea and vomiting (risk ratio, RR = 0.91 [0.49, 1.71]; p = 0.78). Conclusions: TAP block can lower pain intensity and reduce morphine consumption on the first postoperative day in patients undergoing renal transplantation. Pain reduction is especially notable in the subgroup of donors, but the benefits reported are minimum and certainly not clinically relevant. Larger, well-powered RCTs are warranted to confirm these results and evaluate the effect of TAP block in the subgroup of recipients. Full article
(This article belongs to the Special Issue Clinical Updates on Perioperative Pain Management: 2nd Edition)
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Figure 1

Figure 1
<p>PRISMA flowchart: the study selection process.</p>
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<p>Postoperative day 1 pain intensity score. The forest plot shows pain intensity during the first 24 h post-surgery [<a href="#B1-jcm-14-01879" class="html-bibr">1</a>,<a href="#B2-jcm-14-01879" class="html-bibr">2</a>,<a href="#B3-jcm-14-01879" class="html-bibr">3</a>,<a href="#B4-jcm-14-01879" class="html-bibr">4</a>,<a href="#B5-jcm-14-01879" class="html-bibr">5</a>,<a href="#B6-jcm-14-01879" class="html-bibr">6</a>,<a href="#B13-jcm-14-01879" class="html-bibr">13</a>,<a href="#B14-jcm-14-01879" class="html-bibr">14</a>,<a href="#B15-jcm-14-01879" class="html-bibr">15</a>,<a href="#B16-jcm-14-01879" class="html-bibr">16</a>,<a href="#B17-jcm-14-01879" class="html-bibr">17</a>].</p>
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<p>Morphine requirements. The forest plot shows morphine requirements within the first 24 h post-surgery [<a href="#B1-jcm-14-01879" class="html-bibr">1</a>,<a href="#B5-jcm-14-01879" class="html-bibr">5</a>,<a href="#B6-jcm-14-01879" class="html-bibr">6</a>,<a href="#B14-jcm-14-01879" class="html-bibr">14</a>].</p>
Full article ">Figure 4
<p>Cumulative morphine requirements in 24 h. The forest plot shows cumulative morphine requirements at 24 h post-surgery [<a href="#B1-jcm-14-01879" class="html-bibr">1</a>,<a href="#B2-jcm-14-01879" class="html-bibr">2</a>,<a href="#B3-jcm-14-01879" class="html-bibr">3</a>,<a href="#B4-jcm-14-01879" class="html-bibr">4</a>,<a href="#B13-jcm-14-01879" class="html-bibr">13</a>,<a href="#B15-jcm-14-01879" class="html-bibr">15</a>,<a href="#B16-jcm-14-01879" class="html-bibr">16</a>].</p>
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<p>Time to first analgesia. The forest plot shows the time (hours) until the first request for analgesia [<a href="#B2-jcm-14-01879" class="html-bibr">2</a>,<a href="#B16-jcm-14-01879" class="html-bibr">16</a>,<a href="#B17-jcm-14-01879" class="html-bibr">17</a>].</p>
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<p>Postoperative nausea and vomiting. The forest plot shows the risk ratio of nausea and vomiting 24 h post-surgery [<a href="#B2-jcm-14-01879" class="html-bibr">2</a>,<a href="#B3-jcm-14-01879" class="html-bibr">3</a>,<a href="#B4-jcm-14-01879" class="html-bibr">4</a>,<a href="#B6-jcm-14-01879" class="html-bibr">6</a>,<a href="#B13-jcm-14-01879" class="html-bibr">13</a>,<a href="#B15-jcm-14-01879" class="html-bibr">15</a>].</p>
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<p>Subgroup analysis on pain intensity at 24 h PO. The forest plot shows the mean difference in pain scores at 24 h post-surgery for the subgroups of donors and recipients [<a href="#B1-jcm-14-01879" class="html-bibr">1</a>,<a href="#B2-jcm-14-01879" class="html-bibr">2</a>,<a href="#B3-jcm-14-01879" class="html-bibr">3</a>,<a href="#B4-jcm-14-01879" class="html-bibr">4</a>,<a href="#B5-jcm-14-01879" class="html-bibr">5</a>,<a href="#B6-jcm-14-01879" class="html-bibr">6</a>,<a href="#B13-jcm-14-01879" class="html-bibr">13</a>,<a href="#B14-jcm-14-01879" class="html-bibr">14</a>,<a href="#B15-jcm-14-01879" class="html-bibr">15</a>,<a href="#B16-jcm-14-01879" class="html-bibr">16</a>,<a href="#B17-jcm-14-01879" class="html-bibr">17</a>].</p>
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<p>TSA of pain intensity at PO hour 24: (<b>A</b>) recipients; (<b>B</b>) donors; (<b>C</b>) recipients and donors together. <a href="#jcm-14-01879-f008" class="html-fig">Figure 8</a> shows the results of a trial sequential analysis of pain 24 h after surgery for the recipient and donor groups, both separately and together [<a href="#B1-jcm-14-01879" class="html-bibr">1</a>,<a href="#B2-jcm-14-01879" class="html-bibr">2</a>,<a href="#B3-jcm-14-01879" class="html-bibr">3</a>,<a href="#B4-jcm-14-01879" class="html-bibr">4</a>,<a href="#B5-jcm-14-01879" class="html-bibr">5</a>,<a href="#B6-jcm-14-01879" class="html-bibr">6</a>,<a href="#B13-jcm-14-01879" class="html-bibr">13</a>,<a href="#B14-jcm-14-01879" class="html-bibr">14</a>,<a href="#B15-jcm-14-01879" class="html-bibr">15</a>,<a href="#B16-jcm-14-01879" class="html-bibr">16</a>,<a href="#B17-jcm-14-01879" class="html-bibr">17</a>].</p>
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<p>TSA of pain intensity at PO hour 24: (<b>A</b>) recipients; (<b>B</b>) donors; (<b>C</b>) recipients and donors together. <a href="#jcm-14-01879-f008" class="html-fig">Figure 8</a> shows the results of a trial sequential analysis of pain 24 h after surgery for the recipient and donor groups, both separately and together [<a href="#B1-jcm-14-01879" class="html-bibr">1</a>,<a href="#B2-jcm-14-01879" class="html-bibr">2</a>,<a href="#B3-jcm-14-01879" class="html-bibr">3</a>,<a href="#B4-jcm-14-01879" class="html-bibr">4</a>,<a href="#B5-jcm-14-01879" class="html-bibr">5</a>,<a href="#B6-jcm-14-01879" class="html-bibr">6</a>,<a href="#B13-jcm-14-01879" class="html-bibr">13</a>,<a href="#B14-jcm-14-01879" class="html-bibr">14</a>,<a href="#B15-jcm-14-01879" class="html-bibr">15</a>,<a href="#B16-jcm-14-01879" class="html-bibr">16</a>,<a href="#B17-jcm-14-01879" class="html-bibr">17</a>].</p>
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<p>TSA of cumulative morphine requirements on POD1 (only recipients). <a href="#jcm-14-01879-f009" class="html-fig">Figure 9</a> shows the results of a trial sequential analysis of cumulative morphine requirements 24 h after surgery [<a href="#B1-jcm-14-01879" class="html-bibr">1</a>,<a href="#B2-jcm-14-01879" class="html-bibr">2</a>,<a href="#B3-jcm-14-01879" class="html-bibr">3</a>,<a href="#B4-jcm-14-01879" class="html-bibr">4</a>,<a href="#B13-jcm-14-01879" class="html-bibr">13</a>,<a href="#B15-jcm-14-01879" class="html-bibr">15</a>].</p>
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14 pages, 3237 KiB  
Article
Development of Fluorescence-Based Method for Dopamine Determination Using o-Phthaldialdehyde and 3-Mercaptopropyltriethoxysilane
by Valeriia Sliesarenko, Marijana Krstić, Urban Bren and Aleksandra Lobnik
Sensors 2025, 25(6), 1729; https://doi.org/10.3390/s25061729 - 11 Mar 2025
Viewed by 23
Abstract
Nanomaterials and sensors play an important role in modern technologies, including medical diagnostics and biochemical research. This work presents the possibility of using o-Phthaldialdehyde (OPA) in combination with 3-mercaptopropyltriethoxysilane (MPTES) to develop a dopamine-responsive sensor. During the experiment, these materials were used at [...] Read more.
Nanomaterials and sensors play an important role in modern technologies, including medical diagnostics and biochemical research. This work presents the possibility of using o-Phthaldialdehyde (OPA) in combination with 3-mercaptopropyltriethoxysilane (MPTES) to develop a dopamine-responsive sensor. During the experiment, these materials were used at different pH and ratios to determine the optimal parameters for obtaining high fluorescence intensity of the reaction product. The data obtained demonstrate a linear relationship between the fluorescence response (λexem = 340/460 nm) of OPA/MPTES and dopamine concentration in the range of 0.1–3.0 µM at a pH of 8, and the detection limit was 8.7 nM. The obtained results confirm the potential of OPA/MPTES as a sensing component for the detection of dopamine. Full article
(This article belongs to the Section Physical Sensors)
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Graphical abstract

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<p>Influence of pH on the fluorescence intensity over time (λ<sub>ex</sub>/λ<sub>em</sub> = 340/460 nm) during the reaction between 5 µM of dopamine and 500 µM of OPA with 2000 µM of MPTES, recorded at M 5/5.</p>
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<p>Influence of the dopamine-to-OPA ratio on the fluorescence intensity over time (λ<sub>ex</sub>/λ<sub>em</sub> = 340/460 nm) during the reaction between 5 µM of dopamine and OPA (0–500 µM) with MPTES (OPA:MPTES = 1:4) at a pH of 8, recorded at M 5/5. The legend indicates the ratio of dopamine to OPA as follows: 1:0 (5 µM:0 µM), 1:10 (5 µM:50 µM), 1:20 (5 µM:100 µM), 1:50 (5 µM:250 µM), and 1:100 (5 µM:500 µM).</p>
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<p>Influence of the OPA-to-MPTES ratio on the fluorescence intensity over time (λ<sub>ex</sub>/λ<sub>em</sub> = 340/460 nm) during the reaction between 5 µM of dopamine and 100 µM of OPA with MPTES (0–1000 µM) at a pH of 8, recorded at M 3/3. The legend indicates the ratio of OPA to MPTES as follows: 1:0 (100 µM:0 µM), 1:1 (100 µM:100 µM), 1:2 (100 µM:200 µM), 1:4 (100 µM:400 µM), and 1:10 (100 µM:1000 µM).</p>
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<p>Fluorescence spectra (λ<sub>ex</sub> = 340 nm) of the reaction between 5 µM of dopamine and 100 µM of OPA with 200 µM of MPTES at different pHs, recorded at M 3/3 after 10 min.</p>
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<p>Influence of pH on the fluorescence intensity over time (λ<sub>ex</sub>/λ<sub>em</sub> = 340/460 nm) during the reaction between 5 µM of dopamine and 100 µM of OPA with 200 µM of MPTES, recorded at M 3/3.</p>
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<p>Fluorescence spectra (λ<sub>ex</sub>/λ<sub>em</sub> = 340/460 nm) of the reaction between 5 µM of dopamine and 100 µM of OPA with 200 µM of MPTES at a pH of 8, recorded at M 3/3 after 10 min.</p>
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<p>Fluorescence spectra and linear calibration plot (λ<sub>ex</sub>/λ<sub>em</sub> = 340/460 nm) of the reaction between dopamine (0.5, 1.0, 2.0, 3.0, and 5.0 µM) and 100 µM of OPA with 200 µM of MPTES at a pH of 8, recorded at M 3/3 after 10 min.</p>
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<p>Calibration plots (λ<sub>ex</sub>/λ<sub>em</sub> = 340/460 nm) of the reaction between dopamine and 100 µM of OPA with 200 µM of MPTES at a pH of 8, recorded after 10 min.</p>
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<p>Fluorescence intensity (λ<sub>ex</sub>/λ<sub>em</sub> = 340/460 nm) of the reaction between 5 µM of dopamine and 100 µM of OPA with 200 µM of MPTES at a pH of 8 in the presence of various solutes, recorded at M 3/3 after 10 min. The horizontal yellow band indicates the intensity range for the solution without added solutes.</p>
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<p>Fluorescence spectra (λ<sub>ex</sub> = 340 nm) of the reaction between various biogenic amines (5 µM each) and 100 µM of OPA with 200 µM of MPTES, recorded at M 3/3 after 10 min.</p>
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<p>Fluorescence spectra (λ<sub>ex</sub> = 340 nm) of the reaction between various biogenic amines (5 µM each) and 100 µM of OPA with 200 µM of MPTES, recorded at M 3/3 after 10 min.</p>
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<p>Fluorescence intensity (λ<sub>ex</sub>/λ<sub>em</sub> = 340/460 nm, exept for glutation λ<sub>em</sub> = 426 nm) of the reaction between various biogenic amines (5 µM each) and 100 µM of OPA with 200 µM of MPTES, recorded at M 3/3 after 10 min.</p>
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<p>Starting components and presumed product.</p>
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13 pages, 1966 KiB  
Article
Long-Term Effects of Biochar Application on Soil Heterotrophic Respiration in a Warm–Temperate Oak Forest
by Shinpei Yoshitake, Kakuya Enichi, Yuki Tsukimori, Toshiyuki Ohtsuka, Hiroshi Koizumi and Mitsutoshi Tomotsune
Forests 2025, 16(3), 489; https://doi.org/10.3390/f16030489 (registering DOI) - 11 Mar 2025
Viewed by 11
Abstract
Biochar application as a soil amendment is gaining attention as a stable, long-term carbon sequestration strategy for the mitigation of climate change. However, biochar applied to the soil may increase soil carbon efflux. This study aimed to determine the long-term (8 years) effects [...] Read more.
Biochar application as a soil amendment is gaining attention as a stable, long-term carbon sequestration strategy for the mitigation of climate change. However, biochar applied to the soil may increase soil carbon efflux. This study aimed to determine the long-term (8 years) effects of biochar application to the forest floor on soil carbon effluxes (soil respiration [SR] and heterotrophic respiration [HR]) in a warm–temperate oak forest. Biochar was applied at the rate of 0, 5, or 10 Mg ha−1 to 20 m × 20 m plots (n = 4). The SR and HR rates were determined using the closed chamber method and the trenching method. The annual SR tended to increase over 8 years following biochar application, whereas a significant increase in the annual HR (+31%–37%) was observed in the short term (<3 years). The increased HR likely included CO2 emissions from the decomposition of the labile fraction of biochar carbon and from the microbial decomposition of the original soil organic matter stimulated through changes in the soil physicochemical environment, such as soil moisture and pH. The results suggest that a short-term increase in HR should be considered in the evaluation of carbon sequestration in response to biochar addition to forest ecosystems. Full article
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<p>Temporal changes in (<b>a</b>) soil respiration rate (<span class="html-italic">R</span><sub>S</sub>) and (<b>b</b>) heterotrophic respiration rate (<span class="html-italic">R</span><sub>H</sub>) in the plots with or without biochar. C0, C5, and C10 represent the experimental plots with 0, 5, and 10 Mg ha<sup>−1</sup> biochar application, respectively. Values are means (<span class="html-italic">n</span> = 3–4).</p>
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<p>Temporal changes in (<b>a</b>) soil temperature and (<b>b</b>) soil moisture (volumetric soil water content) recorded during the respiration measurements in plots with or without biochar. C0, C5, and C10 represent experimental plots with 0, 5, and 10 Mg ha<sup>−1</sup> biochar application, respectively. Values are means (<span class="html-italic">n</span> = 3–4).</p>
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<p>Soil pH in plots with or without biochar. C0, C5, and C10 represent experimental plots with 0, 5, and 10 Mg ha<sup>−1</sup> biochar application, respectively. Bars and error bars indicate the mean ± SD (<span class="html-italic">n</span> = 4). Bars labeled with different lowercase letters differ significantly (Tukey’s test, <span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Soil microbial biomass carbon determined with the adenosine triphosphate method in plots with or without biochar. C0, C5, and C10 represent experimental plots with 0, 5, and 10 Mg ha<sup>−1</sup> biochar application, respectively. Bars and error bars represent the mean ± SD (<span class="html-italic">n</span> = 4). Bars labeled with different lowercase letters differ significantly (Tukey’s test, <span class="html-italic">p</span> &lt; 0.05). n.d., not determined.</p>
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<p>(<b>a</b>) Annual soil respiration (SR) and (<b>b</b>) annual heterotrophic respiration (HR) in the plots with or without biochar from the second to the eighth year. C0, C5, and C10 represent the experimental plots with 0, 5, and 10 Mg ha<sup>−1</sup> biochar application, respectively. Bars and error bars represent the mean ± SD (<span class="html-italic">n</span> = 4). Bars labeled with different lowercase letters differ significantly (Tukey’s test, <span class="html-italic">p</span> &lt; 0.05). n.d., not determined.</p>
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8 pages, 350 KiB  
Article
Effects of Exogenous Supplementation of Progesterone on Conception Rates in Lactating Murrah Buffaloes
by Rajesh Kumar, Jagat Bir Phogat, Rakesh Kumar Sharma, Sushil Kumar Phulia and Jerome Andonissamy
Vet. Sci. 2025, 12(3), 261; https://doi.org/10.3390/vetsci12030261 - 11 Mar 2025
Viewed by 133
Abstract
The objective of this study was to deduce the effect of exogenous supplementation of progesterone as an intramuscular injection at the time of artificial insemination (AI) on time of ovulation and conception rate in lactating Murrah buffaloes. A total of 30 buffaloes were [...] Read more.
The objective of this study was to deduce the effect of exogenous supplementation of progesterone as an intramuscular injection at the time of artificial insemination (AI) on time of ovulation and conception rate in lactating Murrah buffaloes. A total of 30 buffaloes were included in the experiment and randomly divided into two groups (Treatment, n = 13 and Control, n = 17). Only those buffaloes which were in heat according to visual observation and had clear vaginal discharge, good uterine tone and a large follicle (>12 mm on ultrasound scanning) were reported. Ultrasound scanning was carried out at 6 h intervals after insemination until ovulation. The results revealed that significantly higher numbers of buffaloes ovulated within 24 h post AI in the control group (82.4%) as compared to only 15.4% in the treatment group. In the treatment group, 53.8% of ovulations occurred after 24 h post AI, whereas in the control group only 11.8% of ovulations occurred after 24 h post AI. Up to 96 h post AI, 30.8% of buffaloes in the treatment group and only 5.9% of buffaloes in the control group remained anovulatory. No significant difference was found in CL size between the treatment (226.5 ± 17.4 mm2) and control (238.9 ± 7.9 mm2) groups. Following insemination, 52.9% of buffaloes in the control group conceived, whereas in the treatment group, only 38.5% of buffaloes conceived. Full article
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<p>Size of corpus luteum (CL area in mm<sup>2</sup>) on days 5 and 12 of the estrous cycle in treatment and control groups. a, b—different superscripts indicate significant differences (<span class="html-italic">p</span> &lt; 0.05).</p>
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14 pages, 249 KiB  
Review
Key Gaps in the Prevention and Treatment of Obesity in Children and Adolescents: A Critical Appraisal of Clinical Guidelines
by Francesca Filippi-Arriaga, Michael Georgoulis, Eirini Bathrellou, Meropi D. Kontogianni, Eduard Mogas, Graciela Gastelum and Andreea Ciudin
Children 2025, 12(3), 347; https://doi.org/10.3390/children12030347 (registering DOI) - 10 Mar 2025
Viewed by 77
Abstract
Background: The worldwide increase in the prevalence of childhood obesity necessitates effective prevention and treatment strategies. Clinical practice guidelines (CPGs) offer guidance, but significant heterogeneity or lack of practical application exists in their recommendations. The purpose of the present study is to provide [...] Read more.
Background: The worldwide increase in the prevalence of childhood obesity necessitates effective prevention and treatment strategies. Clinical practice guidelines (CPGs) offer guidance, but significant heterogeneity or lack of practical application exists in their recommendations. The purpose of the present study is to provide an expert, comprehensive, and comparative analysis of gaps in current CPGs for the prevention and treatment of obesity in children and adolescents. Results: A total of 14 CPGs were identified, focusing on childhood obesity prevention (n = 11), treatment (n = 9), or both (n = 6). Prevention CPGs generally recommend body mass index (BMI) assessment, but specific measurement frequency is often absent. While some provide age-specific dietary recommendations, graphical tools are lacking. Recommendations for increased physical activity and reduced screen time are common, but age-stratified guidance is deficient. Furthermore, recommendations regarding mental health and sleep are notably absent. Treatment CPGs utilize BMI for obesity diagnosis, but inconsistencies in cut-off points persist. Comorbidity assessment is generally recommended, yet age-specific guidance remains lacking. Dietary recommendations are present in most CPGs, but many lack detailed specifications (e.g., meal frequency, portion sizes, macronutrient distribution, age-appropriate examples). Most CPGs advocate for 60 min of daily physical activity and limit screen time to 2 h per day. Recommendations concerning sleep are consistently absent. While parental involvement is acknowledged, specific guidance for active participation in prevention and treatment is deficient. Pharmacological treatment options are frequently outdated, and surgical intervention is reserved for exceptional cases of severe obesity. Conclusions: Standardizing BMI cut-off points and defining age groups across CPGs would improve consistency and comparability in the diagnosis, prevention, and treatment of childhood obesity. Tailoring recommendations for diet, physical activity, sedentary behavior, and sleep to specific age groups would ensure developmentally appropriate interventions. A stronger emphasis on early prevention strategies is needed to address the root causes of obesity. Clear guidance for parents and families would facilitate their active engagement in prevention and treatment. Up-to-date information regarding pharmacological and surgical treatments is imperative. Full article
(This article belongs to the Section Global Pediatric Health)
20 pages, 6685 KiB  
Article
Changes in the Properties of Different Zones in Multilayered Translucent Zirconia Used in Monolithic Restorations During Aging Process
by Phil-Joon Koo, Jong-Hyuk Lee, Seung-Ryong Ha, Deog-Gyu Seo, Jin-Soo Ahn and Yu-Sung Choi
J. Funct. Biomater. 2025, 16(3), 96; https://doi.org/10.3390/jfb16030096 - 10 Mar 2025
Viewed by 107
Abstract
This study assessed the changes in the mechanical and surface properties of the transition zone in multilayered translucent monolithic zirconia subjected to long-term hydrothermal aging. A total of 360 disk-shaped specimens (diameter: 15.0 mm; thickness: 1.2 mm) were prepared using conventional (3Y-TZP in [...] Read more.
This study assessed the changes in the mechanical and surface properties of the transition zone in multilayered translucent monolithic zirconia subjected to long-term hydrothermal aging. A total of 360 disk-shaped specimens (diameter: 15.0 mm; thickness: 1.2 mm) were prepared using conventional (3Y-TZP in LT; ZL, 4Y-TZP in MT; ZM) and multilayered translucent zirconia (5Y-TZP in MT Multi; ZT, 3Y/5Y-TZP in Prime; ZP) among IPS e.max ZirCAD blocks. Specimens were divided into three groups (n = 30) and aged in the autoclave at 134 °C under 0.2 MPa for 0 h (control group), 5 h (first aged group), and 10 h (second aged group). The mechanical and surface properties of the transition zone in the multilayered translucent zirconia were investigated, followed by statistical analysis (α = 0.05). Before and after aging, ZL (1102.64 ± 41.37 MPa) and ZP (1014.71 ± 139.86 MPa) showed the highest biaxial flexural strength (BFS); ZL showed the highest Weibull modulus (31.46) and characteristic strength (1121.63 MPa); and ZT exhibited the highest nanoindentation hardness (20.40 ± 1.80 GPa) and Young’s modulus (284.90 ± 20.07 GPa). After aging, ZL (116.75 ± 9.80 nm) exhibited the highest surface roughness (Ra); the monoclinic phase contents in ZL and ZP increased; and surface uplifts, microcracks, and irregular defects caused by phase transformation appeared on ZL and ZP surfaces. The 3Y/5Y-TZP transition zone exhibited flexural strength, Vickers hardness, phase distribution changes, and surface microstructure changes similar to those of 3Y-TZP before and after aging; however, the surface roughness was lower than that of 3Y-TZP and higher than those of 4Y-TZP and 5Y-TZP after aging. The mechanical and surface characteristics, excluding BFS and Vickers hardness, were influenced by the yttrium oxide content in each zone and the aging process. Full article
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<p>Mean ± standard deviation values and statistical analysis of biaxial flexural strength. * denotes a significant difference at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Probability plot for Weibull analysis for all the groups.</p>
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<p>Mean ± standard deviation values and statistical analysis of nanoindentation hardness. * denotes a significant difference at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Mean ± standard deviation values and statistical analysis of Young’s modulus. * denotes a significant difference at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Mean ± standard deviation values and statistical analysis of Vickers hardness. * denotes a significant difference at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Representative CLSM images of all the groups.</p>
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<p>Mean ± standard deviation values and statistical analysis of surface roughness of all specimens in the groups. (<b>A</b>) <span class="html-italic">Ra</span>; (<b>B</b>) <span class="html-italic">Rq</span>. *denotes a significant difference at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Phase transformation analyses in accordance with aging time. (<b>A</b>) Representative XRD patterns; (<b>B</b>) monoclinic volume fraction (<span class="html-italic">F<sub>m</sub></span>).</p>
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<p>FE-SEM images showing the surface topography of all the specimens in the groups. The white arrows indicate irregular defects, microcracks, and surface uplifts after aging.</p>
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<p>Elemental analysis. (<b>A</b>) Zirconium; (<b>B</b>) oxygen; (<b>C</b>) yttrium; (<b>D</b>) hafnium; and (<b>E</b>) aluminum. * denotes a significant difference at <span class="html-italic">p</span> &lt; 0.05.</p>
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12 pages, 2310 KiB  
Article
[3+2] Cycloaddition to a Chiral 5-Methylene-1,3-dioxolan-4-one and Pyrolysis of the Spiro Adducts
by R. Alan Aitken, Lynn A. Power and Alexandra M. Z. Slawin
Molecules 2025, 30(6), 1246; https://doi.org/10.3390/molecules30061246 - 10 Mar 2025
Viewed by 79
Abstract
The [3+2] cycloaddition chemistry of (2S)-5-methylene-2-t-butyl-1,3-dioxolan-4-one, derived from lactic acid, has been examined, and spiro adducts have been obtained with benzonitrile oxide, acetonitrile oxide, diazomethane and diphenyldiazomethane. The structure and absolute stereochemistry of the benzonitrile oxide adduct has been [...] Read more.
The [3+2] cycloaddition chemistry of (2S)-5-methylene-2-t-butyl-1,3-dioxolan-4-one, derived from lactic acid, has been examined, and spiro adducts have been obtained with benzonitrile oxide, acetonitrile oxide, diazomethane and diphenyldiazomethane. The structure and absolute stereochemistry of the benzonitrile oxide adduct has been confirmed by X-ray diffraction, and all the adducts have been fully characterised by 1H and 13C NMR. Attempted cycloaddition with a nitrile sulfide, a nitrile imine and azides failed. Pyrolysis results in a range of novel gas-phase reactions, with the nitrile oxide adducts giving pivalaldehyde, CO2, the nitrile and ketene, the diazomethane adduct losing only N2 to give a cyclopropane-fused dioxolanone, and the diphenylcyclopropane derived from diphenyldiazomethane giving mainly benzophenone in a sequence involving the loss of pivalaldehyde and methyleneketene. Full article
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<p>X-ray structure of <b>7</b> with thermal ellipsoids (50%) and crystallographic numbering system used.</p>
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<p>Compilation of NMR data for new spiro dioxolanones (blue: δ<sub>C</sub>; red: δ<sub>H</sub>).</p>
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<p>NMR data for similar spiro heterocyclic compounds (blue: δ<sub>C</sub>; red: δ<sub>H</sub>; * indicates assignments may be interchanged).</p>
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<p>Opportunities for cycloaddition chemistry to the double bond of <b>2</b>, and the only previous methylenedioxolanone [3+2] cycloadduct.</p>
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<p>Formation of [3+2] cycloadducts from <b>2</b>.</p>
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<p>Pyrolysis products from the nitrile oxide adducts.</p>
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<p>Proposed mechanism for the pyrolysis of <b>7</b> and <b>8</b>.</p>
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<p>FVP behaviour of spiro pyrazoline–dioxolanone <b>9</b> and comparison with <b>5</b> [<a href="#B14-molecules-30-01246" class="html-bibr">14</a>].</p>
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<p>FVP of the spiro cyclopropane–dioxolanone <b>10</b>.</p>
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<p>Proposed mechanism for the formation of benzophenone from FVP of <b>10</b>.</p>
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<p>Similar FVP reaction previously used to generate <b>22</b> [<a href="#B22-molecules-30-01246" class="html-bibr">22</a>].</p>
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20 pages, 3513 KiB  
Article
Coupled Effects of Water Depth, Vegetation, and Soil Properties on Soil Organic Carbon Components in the Huixian Wetland of the Li River Basin
by Yongkang Wang, Junfeng Dai, Fan Jiang, Zupeng Wan and Shuaipu Zhang
Land 2025, 14(3), 584; https://doi.org/10.3390/land14030584 - 10 Mar 2025
Viewed by 47
Abstract
Wetland ecosystems are essential to the global carbon cycle, and they contribute significantly to carbon storage and regulation. While existing studies have explored the individual effects of the water depth, vegetation, and soil properties on the soil organic carbon (SOC) components, a comprehensive [...] Read more.
Wetland ecosystems are essential to the global carbon cycle, and they contribute significantly to carbon storage and regulation. While existing studies have explored the individual effects of the water depth, vegetation, and soil properties on the soil organic carbon (SOC) components, a comprehensive study of the interactions between these factors is still lacking, particularly regarding their collective impact on the composition of the SOC in wetland soils. This paper focused on the Huixian Wetland in the Li River Basin. The variations in the SOC and its fractions, namely dissolved organic carbon, microbial biomass carbon, light fraction organic carbon, and mineral-associated organic carbon, under different water depths and vegetation conditions were examined. Additionally, the effects of the water depth, vegetation, and soil properties (pH and bulk density, total phosphorus (TP), total nitrogen (TN), ammonium nitrogen (NH4-N), and nitrate nitrogen (NO3-N)) on the changes in the SOC and its components were quantified. Specific water depth–vegetation combinations favor SOC accumulation, with Cladium chinense at a water depth of 20 cm and Phragmites communis at 40 cm exhibiting a higher biomass and higher SOC content. The SOC components were significantly and positively correlated with plant biomass, TP, TN, and NH4-N. The coupling of water depth, vegetation, and soil properties had a significant effect on the SOC components, with the coupling of water depth, vegetation, and soil properties contributing 74.4% of the variation in the SOC fractions. Among them, water depth, plant biomass, and soil properties explained 7.8%, 7.3%, and 6.4% of the changes, respectively, and their interactions explained 25.6% of the changes. The coupling of the three significantly influenced the changes in the SOC components. Optimal water level management and the strategic planting of wetland vegetation can enhance the carbon storage capacity and increase the SOC content. This research offers valuable insights for effectively managing wetland carbon sinks and soil carbon reserves. Full article
(This article belongs to the Section Land, Soil and Water)
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Figure 1
<p>Maps showing the location of the study area.</p>
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<p>Soil organic carbon content at three water depths (20, 40, and 60 cm) with <span class="html-italic">Cladium chinense</span>, <span class="html-italic">Phragmites communis</span>, and no plants. (<b>a</b>) 0–20 cm soil depth; (<b>b</b>) 20–40 cm soil depth; (<b>c</b>) 40–60 cm soil depth; (<b>d</b>) 60–100 cm soil depth.</p>
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<p>Soil organic carbon stocks and soil bulk density at three water depths (20, 40, and 60 cm) with <span class="html-italic">Cladium chinense</span>, <span class="html-italic">Phragmites communis</span>, and no plants. (<b>a</b>) SOC stocks; (<b>b</b>) soil bulk density.</p>
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<p>Soil properties at three water depths (20, 40, and 60 cm) with <span class="html-italic">Cladium chinense</span>, <span class="html-italic">Phragmites communis</span>, and no plants. (<b>a</b>) pH; (<b>b</b>) WC; (<b>c</b>) TP; (<b>d</b>) TN; (<b>e</b>) NO<sub>3</sub>-N; and (<b>f</b>) NH<sub>4</sub>-N.</p>
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<p>Soil properties at three water depths (20, 40, and 60 cm) with <span class="html-italic">Cladium chinense</span>, <span class="html-italic">Phragmites communis</span>, and no plants. (<b>a</b>) pH; (<b>b</b>) WC; (<b>c</b>) TP; (<b>d</b>) TN; (<b>e</b>) NO<sub>3</sub>-N; and (<b>f</b>) NH<sub>4</sub>-N.</p>
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<p>Soil organic carbon components at three water depths (20, 40, and 60 cm) with <span class="html-italic">Cladium chinense</span>, <span class="html-italic">Phragmites communis</span>, and no plants. (<b>a</b>) DOC; (<b>b</b>) MBC; (<b>c</b>) LFOC; and (<b>d</b>) ROC.</p>
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<p>Plant biomass at different water depths. (<b>a</b>) AGB; (<b>b</b>) RB.</p>
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<p>Pearson’s correlation analysis between the plant biomass, soil properties, and SOC component. The symbols * and ** indicate significant correlations at the 0.05 and 0.01 levels, respectively.</p>
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<p>Venn diagram showing variation partitioning in the plant biomass, soil properties, and water depth activities on the SOC component changes.</p>
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16 pages, 3238 KiB  
Article
Primary Pyrrolimines and Pyridinimines
by Amavi Kpoezoun, Gnon Baba and Jean-Claude Guillemin
Molecules 2025, 30(6), 1239; https://doi.org/10.3390/molecules30061239 - 10 Mar 2025
Viewed by 109
Abstract
The association of an aromatic ring with an N-H-unsubstituted imine generates families of compounds that have been little studied until now except when the ring is a phenyl group. Recently, such imines substituted by a furan or thiophene group have been synthesized. This [...] Read more.
The association of an aromatic ring with an N-H-unsubstituted imine generates families of compounds that have been little studied until now except when the ring is a phenyl group. Recently, such imines substituted by a furan or thiophene group have been synthesized. This work reports a similar study where a pyrrole or pyridine ring is directly linked to an N-unsubstituted aldimine or ketimine group in order to isolate such compounds and to open the way to the knowledge of their physicochemical properties. The lower volatility of pyrrole and pyridine derivatives compared to aryl, furan, or thiophene derivatives greatly increases the difficulty of the synthesis and isolation of these kinetically unstable compounds. Full article
(This article belongs to the Section Organic Chemistry)
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Graphical abstract

Graphical abstract
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<p>Drugs with a pyrrolimine motif.</p>
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<p>Drugs with a pyridinimine motif.</p>
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<p>Target imines <b>1a</b>–<b>1d</b> and <b>2a</b>–<b>2f</b>.</p>
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<p>α-aminonitriles <b>3a</b>–<b>3d</b> and <b>4a</b>–<b>4f</b>, potential precursors of imines <b>1a</b>–<b>1d</b> and <b>2a</b>–<b>2f</b>.</p>
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<p>Synthesis of α-aminonitriles <b>3a</b>, <b>3b</b>, and <b>4a</b>–<b>4f</b>.</p>
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<p>N-allylamines <b>5a</b>–<b>5d</b> and <b>6a</b>–<b>6f</b>.</p>
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<p>Synthesis of Allylamines <b>5a</b>–<b>5d</b> and <b>6a</b>–<b>6f</b>.</p>
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<p>Dehydrocyanation of α-aminonitriles <b>4b</b>, <b>4d</b>, and <b>4f</b>.</p>
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<p>Synthesis imines <b>1d</b> and <b>2a</b>–<b>2f</b> by a retro-ene reaction.</p>
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<p>(<span class="html-italic">E</span>)- and (<span class="html-italic">Z</span>)-N-methyl α-methyl-2-pyrrolemethanimines <b>1d</b> and <sup>1</sup>H NMR data of <b>(<span class="html-italic">E</span>)-1d</b>.</p>
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<p><sup>1</sup>H NMR data of pyridinaldimines <b>(<span class="html-italic">Z</span>)-</b> and <b>(<span class="html-italic">E</span>)-2a</b>, <b>(<span class="html-italic">E</span>)-2c</b>, and <b>(<span class="html-italic">E</span>)-2e</b>.</p>
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<p>Transimination reaction with imines <b>1d</b> and <b>2a</b>–<b>2f</b>.</p>
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<p>Transimination products with the yield of the two-step reaction.</p>
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<p>Synthesis of 2-pyridinimine-triethylborane complex <b>9a</b>.</p>
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<p>Proposed H-bond in compounds <b>2a</b> and <b>9a</b>.</p>
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15 pages, 3422 KiB  
Article
Rapid Synthesis of Honeycomb-Structured FeP2@NHC for High-Rate and Durable Lithium Storage
by Junjie Shao, Xiaodong Wang, Houhua Ceng, Lan Hu and Zhean Su
Energies 2025, 18(6), 1358; https://doi.org/10.3390/en18061358 - 10 Mar 2025
Viewed by 211
Abstract
The concurrent preservation of structural integrity and improvement of electrical conductivity in FeP2 anodes presents a persistent challenge. Herein, FeP2 nanoparticles embedded within a 3D N-doped honeycomb-like carbon framework composite (FeP2@NHC) are synthesized through a phosphorization process with a [...] Read more.
The concurrent preservation of structural integrity and improvement of electrical conductivity in FeP2 anodes presents a persistent challenge. Herein, FeP2 nanoparticles embedded within a 3D N-doped honeycomb-like carbon framework composite (FeP2@NHC) are synthesized through a phosphorization process with a honeycomb-like Fe3C@NHC as a precursor. The in situ incorporation of FeP2 nanoparticles into the 3D carbon matrix effectively restrains the aggregation, pulverization, and stripping of material during cycling, and significantly enhances reaction kinetics and structural stability, achieving a superior electrochemical performance. Specifically, FeP2@NHC electrodes demonstrate remarkable reversible capacity (1433.9 mA h g−1 at 0.1 A g−1), excellent rate-capability (399.9 mA h g−1 at 10 A g−1), and ultra-long cycle life (631.5 mA h g−1 after 1000 cycles at 2 A g−1). Moreover, XRD analysis reveals that iron-rich Fe3C and Fe3O4 precursors can react with NaH2PO2 to form FeP2 and FeP, respectively. This study offers a rational and practical strategy for designing other phosphorus-rich metal phosphide anode materials. Full article
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Figure 1
<p>Schematic illustration of the process for preparing FeP<sub>2</sub>@NHC nanocomposite.</p>
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<p>(<b>a</b>) SEM image of Fe<sub>3</sub>C@NHC; (<b>b</b>) SEM image of FeP<sub>2</sub>@NHC; (<b>c</b>) the low-magnification TEM image, (<b>d</b>) HRTEM image, (<b>e</b>) SAED pattern, (<b>f</b>) EDX spectrum of FeP<sub>2</sub>@NHC; (<b>g</b>–<b>k</b>) STEM image and elemental mapping images of FeP<sub>2</sub>@NHC.</p>
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<p>XRD spectra of (<b>a</b>) FeP<sub>2</sub>@NHC, (<b>b</b>) FeP−FeP<sub>2</sub>@C, (<b>c</b>) FeP; (<b>d</b>) Raman spectra, (<b>e</b>) N<sub>2</sub> adsorption–desorption isotherms and pore size distribution (inset), (<b>f</b>) TGA analysis, (<b>g</b>) XPS survey spectrum, (<b>h</b>) Fe 2p, and (<b>i</b>) P 2p XPS high solution of FeP<sub>2</sub>@NHC.</p>
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<p>The electrochemical performance of electrodes in LIBs: (<b>a</b>) CV curves at 0.2 mV s<sup>−1</sup>, (<b>b</b>) charge–discharge profiles at 0.1 A g<sup>−1</sup> of FeP<sub>2</sub>@NHC; (<b>c</b>) cycling stability at 0.1 A g<sup>−1</sup>, (<b>d</b>) rate capability, (<b>e</b>) long–cycling performance at 2 A g<sup>−1</sup> of FeP<sub>2</sub>@NHC, FeP–FeP<sub>2</sub>@C, FeP.</p>
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<p>(<b>a</b>,<b>d</b>,<b>g</b>) CV curves of (a) FeP<sub>2</sub>@NHC, (<b>d</b>) FeP−FeP<sub>2</sub>@C, (<b>g</b>) FeP electrodes at various scan rates; (<b>b</b>,<b>e</b>,<b>h</b>) diffusion contributions and capacitive contributions to charge storage of (<b>b</b>) FeP<sub>2</sub>@NHC, (<b>e</b>) FeP−FeP<sub>2</sub>@C, (<b>h</b>) FeP electrode at 0.8 mV s<sup>−1</sup>; (<b>c</b>,<b>f</b>,<b>i</b>) normalized contribution proportion of two storage mechanisms at different scan rates.</p>
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<p>(<b>a</b>) GITT curve of FeP<sub>2</sub>@NHC electrode; (<b>b</b>,<b>c</b>) calculation results of Li<sup>+</sup> diffusion coefficients of FeP<sub>2</sub>@NHC, FeP−FeP<sub>2</sub>@C, FeP.</p>
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<p>Structural evolutions during cycling process of anode materials.</p>
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