[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
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

Search Results (1,631)

Search Parameters:
Keywords = in situ reduction

Order results
Result details
Results per page
Select all
Export citation of selected articles as:
12 pages, 3498 KiB  
Article
An Integrated Na2S−Electrocatalyst Nanostructured Cathode for Sodium–Sulfur Batteries at Room Temperature
by Sichang Ma, Yueming Zhu, Yadong Yang, Dongyang Li, Wendong Tan, Ling Gao, Wanwei Zhao, Wenbo Liu, Wenyu Liang and Rui Xu
Batteries 2025, 11(1), 9; https://doi.org/10.3390/batteries11010009 - 27 Dec 2024
Viewed by 261
Abstract
Room-temperature sodium–sulfur (RT Na–S) batteries offer a superior, high-energy-density solution for rechargeable batteries using earth-abundant materials. However, conventional RT Na–S batteries typically use sulfur as the cathode, which suffers from severe volume expansion and requires pairing with a sodium metal anode, raising significant [...] Read more.
Room-temperature sodium–sulfur (RT Na–S) batteries offer a superior, high-energy-density solution for rechargeable batteries using earth-abundant materials. However, conventional RT Na–S batteries typically use sulfur as the cathode, which suffers from severe volume expansion and requires pairing with a sodium metal anode, raising significant safety concerns. Utilizing Na2S as the cathode material addresses these issues, yet challenges such as Na2S’s low conductivity as well as the shuttle effect of polysulfide still hinder RT Na–S battery development. Herein, we present a simple and cost-effective method to fabricate a Na2S–Na6CoS4/Co@C cathode, wherein Na2S nanoparticles are embedded in a conductive carbon matrix and coupled with dual catalysts, Na6CoS4 and Co, generated via the in situ carbothermal reduction of Na2SO4 and CoSO4. This approach creates a three-dimensional porous composite cathode structure that facilitates electrolyte infiltration and forms a continuous conductive network for efficient electron transport. The in situ formed Na6CoS4/Co electrocatalysts, tightly integrated with Na2S, exhibit strong catalytic activity and robust physicochemical stabilization, thereby accelerating redox kinetics and mitigating the polysulfide shuttle effect. As a result, the Na2S–Na6CoS4/Co@C cathode achieves superior capacity retention, demonstrating a discharge capacity of 346 mAh g−1 after 100 cycles. This work highlights an effective strategy for enhancing Na2S cathodes with embedded catalysts, leading to enhanced reaction kinetics and superior cycling stability. Full article
(This article belongs to the Special Issue Energy-Dense Metal–Sulfur Batteries)
Show Figures

Figure 1

Figure 1
<p>Scheme of the synthetic strategy for Na<sub>2</sub>S−Na<sub>6</sub>CoS<sub>4</sub>/Co@C.</p>
Full article ">Figure 2
<p>SEM of (<b>a</b>–<b>c</b>) Na<sub>2</sub>S@C and (<b>d</b>–<b>f</b>) Na<sub>2</sub>S−Na<sub>6</sub>CoS<sub>4</sub>/Co@C at various magnifications. HRTEM of (<b>g</b>) Na<sub>2</sub>S@C and (<b>h</b>,<b>i</b>) Na<sub>2</sub>S−Na<sub>6</sub>CoS<sub>4</sub>/Co@C.</p>
Full article ">Figure 3
<p>XRD of (<b>a</b>) Na<sub>2</sub>S@C and (<b>b</b>) Na<sub>2</sub>S−Na<sub>6</sub>CoS<sub>4</sub>/Co@C. (<b>c</b>) Raman spectra of Na<sub>2</sub>S@C. (<b>d</b>) N<sub>2</sub> adsorption−desorption isotherm of Na<sub>2</sub>S−Na<sub>6</sub>CoS<sub>4</sub>/Co@C. (<b>e</b>) Pore size distribution of Na<sub>2</sub>S−Na<sub>6</sub>CoS<sub>4</sub>/Co@C. (<b>f</b>) TGA curve of Na<sub>2</sub>S@C, which is measured in dry air at a ramp rate of 10 °C min<sup>−1</sup>. XPS plots of the (<b>g</b>) Na 1s, (<b>h</b>) Co 2p, and (<b>i</b>) S 2p regions in Na<sub>2</sub>S−Na<sub>6</sub>CoS<sub>4</sub>/Co@C.</p>
Full article ">Figure 4
<p>(<b>a</b>) Typical charge/discharge curves of the cells with Na<sub>2</sub>S@C and Na<sub>2</sub>S–Na<sub>6</sub>CoS<sub>4</sub>/Co@C cathodes at 0.1C. (<b>b</b>) Cyclic voltammograms of Na<sub>2</sub>S–Na<sub>6</sub>CoS<sub>4</sub>/Co@C electrode at 0.1 mV s<sup>−1</sup>. GCD profiles after different cycling stages at 0.1C of (<b>c</b>) Na<sub>2</sub>S@C and (<b>d</b>) Na<sub>2</sub>S–Na<sub>6</sub>CoS<sub>4</sub>/Co@C. (<b>e</b>) Cycling stability of Na<sub>2</sub>S@C and Na<sub>2</sub>S–Na<sub>6</sub>CoS<sub>4</sub>/Co@C at 0.1C rate.</p>
Full article ">Figure 5
<p>(<b>a</b>) Digital photos and (<b>b</b>) UV−vis adsorption spectra of Na<sub>2</sub>S<sub>6</sub> solutions trapped by Na<sub>6</sub>CoS<sub>4</sub>/Co@C and C.</p>
Full article ">
21 pages, 3805 KiB  
Article
Embedment of Biosynthesised Silver Nanoparticles in PolyNIPAAm/Chitosan Hydrogel for Development of Proactive Smart Textiles
by Dominika Glažar, Danaja Štular, Ivan Jerman, Barbara Simončič and Brigita Tomšič
Nanomaterials 2025, 15(1), 10; https://doi.org/10.3390/nano15010010 - 25 Dec 2024
Viewed by 52
Abstract
A smart viscose fabric with temperature and pH responsiveness and proactive antibacterial and UV protection was developed. PNCS (poly-(N-isopropylakrylamide)/chitosan) hydrogel was used as the carrier of silver nanoparticles (Ag NPs), synthesised in an environmentally friendly manner using AgNO3 and a sumac leaf [...] Read more.
A smart viscose fabric with temperature and pH responsiveness and proactive antibacterial and UV protection was developed. PNCS (poly-(N-isopropylakrylamide)/chitosan) hydrogel was used as the carrier of silver nanoparticles (Ag NPs), synthesised in an environmentally friendly manner using AgNO3 and a sumac leaf extract. PNCS hydrogel and Ag NPs were applied to the viscose fabric by either in situ synthesis of Ag NPs on the surface of viscose fibres previously modified with PNCS hydrogel, or by the direct immobilisation of Ag NPs by the dehydration/hydration of the PNCS hydrogel with the nanodispersion of Ag NPs in the sumac leaf extract and subsequent application to the viscose fibres. Compared to the pre-functionalised PNCS application method, the in situ functionalisation imparted much higher concentration of Ag NPs on the fibres, colouring the samples brown to brown-green. These samples showed more than 90% reduction in the test bacteria E. coli and S. aureus and provided excellent UV protection. In this case, the PNCS hydrogel acted as a reservoir for Ag NPs, whose release was based on a diffusion-controlled mechanism. Despite the Ag NPs decreasing the responsiveness of the PNCS hydrogel, the moisture management was still preserved in the modified samples. Accordingly, the PNCS hydrogel is a suitable carrier for biosynthesized Ag NPs to tailor the protective smart surface of viscose fibres. Full article
(This article belongs to the Special Issue Antimicrobial and Antioxidant Activity of Nanoparticles)
Show Figures

Figure 1

Figure 1
<p>A schematic presentation of viscose fabric modification with PNCS hydrogel functionalised via in situ synthesis of Ag NPs (<b>a</b>) and via the direct application of a functionalised PNCS hydrogel with previously embedded Ag NPs (<b>b</b>).</p>
Full article ">Figure 2
<p>(<b>a</b>) SEM images of untreated and modified samples at 3 K magnification; (<b>b</b>) EDS spectra of modified CV_5Ag, CV_PNCS/5Ag, and CV_PNCS + 5Ag samples, with corresponding SEM/BSE images as insets; (<b>c</b>) Ag concentration in the analysed samples; (<b>d</b>) IR-ATR spectra of the analysed samples.</p>
Full article ">Figure 3
<p>(<b>a</b>) Photo images of the untreated and studied modified samples with corresponding CIE L*a*b* values; (<b>b</b>) colour change (ΔE<sub>ab</sub>*) of the studied modified samples; (<b>c</b>) colour strength (K/S) spectra of the untreated and studied modified samples.</p>
Full article ">Figure 4
<p>(<b>a</b>) The moisture content (MC) of the untreated and modified samples, and (<b>b</b>) the swelling ratio of the PNCS hydrogel triggered by temperature change (S<sub>T</sub>); (<b>c</b>) the water uptake (WU) of the untreated and modified samples with the (<b>d</b>) swelling ratio of the PNCS hydrogel triggered by pH change (S<sub>pH</sub>).</p>
Full article ">Figure 5
<p>(<b>a</b>) The growth reduction of bacteria <span class="html-italic">E. coli</span> and <span class="html-italic">S. aureus</span> in contact with the studied samples; (<b>b</b>) studied bacteria colonies grown on the agar plates after being in contact with the CV_N and CV_PNCS/1Ag samples; (<b>c</b>) the inhibition zone formed around the studied CV_PNCS/xAg and CV_PNCS + xAG samples after incubation at 20 and 37 °C; (<b>d</b>) silver (Ag) release from the CV_1Ag and CV_PNCS/1Ag samples.</p>
Full article ">Figure 6
<p>(<b>a</b>) UV transmission and (<b>b</b>) reflection spectra of untreated and studied modified samples.</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 303
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 ">
17 pages, 5343 KiB  
Article
In Situ Synthesis of Co3O4 Nanoparticles on N-Doped Biochar as High-Performance Oxygen Reduction Reaction Electrocatalysts
by Renata Matos, Jorge V. Manuel, António J. S. Fernandes, Victor K. Abdelkader-Fernández, Andreia F. Peixoto and Diana M. Fernandes
Catalysts 2024, 14(12), 951; https://doi.org/10.3390/catal14120951 - 23 Dec 2024
Viewed by 333
Abstract
The development of sustainable and high-performance oxygen reduction reaction (ORR) electrocatalysts is fundamental to fuel cell implementation. Non-precious transition metal oxides present interesting electrocatalytic behavior, and their incorporation into N-doped carbon supports leads to excellent ORR performance. Herein, we prepared a shrimp shell-derived [...] Read more.
The development of sustainable and high-performance oxygen reduction reaction (ORR) electrocatalysts is fundamental to fuel cell implementation. Non-precious transition metal oxides present interesting electrocatalytic behavior, and their incorporation into N-doped carbon supports leads to excellent ORR performance. Herein, we prepared a shrimp shell-derived biochar (CC), which was doped with nitrogen via a ball milling approach (N-CC), and then used as support for Co3O4 nanoparticles growth (N-CC@Co3O4). Co3O4 loading was optimized using three different amounts of cobalt precursor: 1.56, 2.33 and 3.11 mmol in N-CC@Co3O4_1, N-CC@Co3O4_2 and N-CC@Co3O4_3, respectively. Interestingly, all prepared electrocatalysts, including the initial biochar CC, presented electrocatalytic activity towards ORR. Both N-doping and the introduction of Co3O4 NPs had a significant positive effect on ORR performance. Meanwhile, the three composites showed distinct ORR behavior, demonstrating that it is possible to tune their electrocatalytic performance by changing the Co3O4 loading. Overall, N-CC@Co3O4_2 achieved the most promising ORR results, displaying an Eonset of 0.84 V vs. RHE, jL of −3.45 mA cm−2 and excellent selectivity for the 4-electron reduction (n = 3.50), besides good long-term stability. These results were explained by a combination of high content of pyridinic-N and graphitic-N, high ratio of pyridinic-N/graphitic-N, and optimized Co3O4 loading interacting synergistically with the porous N-CC support. Full article
(This article belongs to the Special Issue Advances in Biomass-Based Electrocatalysts)
Show Figures

Figure 1

Figure 1
<p>SEM micrographs of (<b>a</b>) CC, (<b>b</b>) N-CC, (<b>c</b>) Co<sub>3</sub>O<sub>4</sub>, (<b>d</b>) N-CC@Co<sub>3</sub>O<sub>4</sub>_1, (<b>e</b>) N-CC@Co<sub>3</sub>O<sub>4</sub>_2 and (<b>f</b>) N-CC@Co<sub>3</sub>O<sub>4</sub>_3, obtained at magnifications of 1000, 25,000, 50,000, 25,000, 25,000 and 25,000×, respectively.</p>
Full article ">Figure 2
<p>Raman spectra of CC, N-CC and N-CC@Co<sub>3</sub>O<sub>4</sub> composites.</p>
Full article ">Figure 3
<p>Diffraction patterns of CC, N-CC, the prepared N-CC@Co<sub>3</sub>O<sub>4</sub> composites and bare Co<sub>3</sub>O<sub>4</sub> NPs.</p>
Full article ">Figure 4
<p>High resolution XPS spectra of N 1s region of (<b>a</b>) CC, (<b>b</b>) N-CC, (<b>c</b>) N-CC@Co<sub>3</sub>O<sub>4</sub>_1, (<b>d</b>) N-CC@Co<sub>3</sub>O<sub>4</sub>_2 and (<b>e</b>) N-CC@Co<sub>3</sub>O<sub>4</sub>_3.</p>
Full article ">Figure 5
<p>High-resolution XPS spectra of region Co 2p of (<b>a</b>) N-CC@Co<sub>3</sub>O<sub>4</sub>_1, (<b>b</b>) N-CC@Co<sub>3</sub>O<sub>4</sub>_2 and (<b>c</b>) N-CC@Co<sub>3</sub>O<sub>4</sub>_3.</p>
Full article ">Figure 6
<p>(<b>a</b>) ORR polarization curves of the prepared electrocatalysts, obtained in O<sub>2</sub>-saturated 0.1 mol dm<sup>−3</sup> KOH solution, at 1600 rpm and 0.005 V s<sup>−1</sup>, (<b>b</b>) influence of applied potential in <span class="html-italic">n</span>, (<b>c</b>) Tafel plots and (<b>d</b>) chronoamperograms of N-CC@Co<sub>3</sub>O<sub>4</sub>_2 and Pt/C at <span class="html-italic">E</span> = 0.47 V vs. RHE and 1600 rpm, in O<sub>2</sub>-saturated 0.1 mol dm<sup>−3</sup> KOH solution.</p>
Full article ">
13 pages, 6569 KiB  
Article
Efficient Electrocatalytic Nitrogen Reduction to Ammonia with Electrospun Hierarchical Carbon Nanofiber/TiO2@CoS Heterostructures
by Zhenjun Chang, Fuxing Jia, Xingyu Ji, Qian Li, Jingren Cui, Zhengzheng Liao and Xiaoling Sun
Molecules 2024, 29(24), 6025; https://doi.org/10.3390/molecules29246025 - 20 Dec 2024
Viewed by 281
Abstract
As a sustainable alternative technology to the cost- and energy-intensive Haber–Bosch method, electrochemical nitrogen (N2) reduction offers direct conversion of N2 to NH3 under ambient conditions. Direct use of noble metals or non-noble metals as electrocatalytic materials results in [...] Read more.
As a sustainable alternative technology to the cost- and energy-intensive Haber–Bosch method, electrochemical nitrogen (N2) reduction offers direct conversion of N2 to NH3 under ambient conditions. Direct use of noble metals or non-noble metals as electrocatalytic materials results in unsatisfactory electrocatalytic properties because of their low electrical conductivity and stability. Herein, three-dimensional flexible carbon nanofiber (CNF/TiO2@CoS) nanostructures were prepared on the surface of CNF by using electrospinning, a hydrothermal method, and in situ growth. We investigated the behavior of CNFs/TiO2@CoS as an electrocatalytic material in 0.1 M sodium sulfate. The highest ammonia yield of the material was 4.61 × 10−11 mol s−1 cm−2 at −0.45 V vs. RHE, and the highest Faraday efficiency, as well as superior long-term durability, was 8.3% at −0.45 V vs. RHE. This study demonstrates the potential of firecracker-shaped nanofiber templates for loading varied noble metals or non-noble metals as a novel development of hybrid composites for electrocatalytic nitrogen reduction. Full article
Show Figures

Figure 1

Figure 1
<p>SEM images of CNFs under low (<b>a</b>) and high (<b>b</b>) magnification. SEM images of CNFs/TiO<sub>2</sub> (<b>c</b>) and CNF/TiO<sub>2</sub>@CoS (<b>d</b>). SEM elemental mapping images of CNF/TiO<sub>2</sub>@CoS (<b>e</b>), C (<b>f</b>), O (<b>g</b>), Ti (<b>h</b>), Co (<b>i</b>), and S (<b>j</b>).</p>
Full article ">Figure 2
<p>XRD patterns for CNF/TiO<sub>2</sub> and CNF/TiO<sub>2</sub>@CoS.</p>
Full article ">Figure 3
<p>XPS spectra of (<b>a</b>) wide-scan, (<b>b</b>) C 1s, (<b>c</b>) Ti 2p, (<b>d</b>) O 1s, (<b>e</b>) Co 2p, and (<b>f</b>) S 2p for CNF/TiO<sub>2</sub>@CoS.</p>
Full article ">Figure 4
<p>(<b>a</b>) Time-dependent current density curves, (<b>b</b>) UV–vis spectra, and (<b>c</b>) ammonia yields and Faradaic efficiencies of the CNF/TiO<sub>2</sub>@CoS nanofibrous membrane at different potentials. (<b>d</b>) Time-dependent current density curve for CNF/TiO<sub>2</sub>@CoS in 0.1 M Na<sub>2</sub>SO<sub>4</sub> electrolyte at −0.45 V vs. RHE for 12 h.</p>
Full article ">Figure 5
<p>(<b>a</b>) Absorbance curves (<b>b</b>) N<sub>2</sub>H<sub>4</sub> yield of p-dimethylaminobenzaldehyde indicator after electrolysis for 2 h at different potentials.</p>
Full article ">Figure 6
<p>(<b>a</b>) Current density time curves; (<b>b</b>) ammonia yield and Faraday efficiency of CNF/TiO<sub>2</sub>@CoS in 0.1 M Na<sub>2</sub>SO<sub>4</sub> at −0.45 V vs. RHE. for 2 h and five times.</p>
Full article ">Figure 7
<p>(<b>a</b>)Absorbance curves and (<b>b</b>)NH<sub>3</sub> yields and FEs of CNF, CNF/TiO<sub>2</sub>, and CNF/TiO<sub>2</sub>@CoS nanofiber membranes after electrolysis at −0.45 V vs. RHE for 2 h.</p>
Full article ">Figure 8
<p>Absorbance curve of p-dimethylaminobenzaldehyde indicator at optimum potential after electrolysis for 12 h.</p>
Full article ">Figure 9
<p>Proposed pathway for the NH<sub>3</sub> synthesis using CNF/TiO<sub>2</sub>@CoS catalyst.</p>
Full article ">
18 pages, 4785 KiB  
Article
A Merging Approach for Improving the Quality of Gridded Precipitation Datasets over Burkina Faso
by Moussa Waongo, Juste Nabassebeguelogo Garba, Ulrich Jacques Diasso, Windmanagda Sawadogo, Wendyam Lazare Sawadogo and Tizane Daho
Climate 2024, 12(12), 226; https://doi.org/10.3390/cli12120226 - 20 Dec 2024
Viewed by 372
Abstract
Satellite precipitation estimates are crucial for managing climate-related risks such as droughts and floods. However, these datasets often contain systematic errors due to the observation methods used. The accuracy of these estimates can be enhanced by integrating spatial and temporal resolution data from [...] Read more.
Satellite precipitation estimates are crucial for managing climate-related risks such as droughts and floods. However, these datasets often contain systematic errors due to the observation methods used. The accuracy of these estimates can be enhanced by integrating spatial and temporal resolution data from in situ observations. Nevertheless, the accuracy of the merged dataset is influenced by the density and distribution of rain gauges, which can vary regionally. This paper presents an approach to improve satellite precipitation data (SPD) over Burkina Faso. Two bias correction methods, Empirical Quantile Mapping (EQM) and Time and Space-Variant (TSV), have been applied to the SPD to yield a bias-corrected dataset for the period 1991–2020. The most accurate bias-corrected dataset is then combined with in situ observations using the Regression Kriging (RK) method to produce a merged precipitation dataset. The findings show that both bias correction methods achieve similar reductions in RMS error, with higher correlation coefficients (approximately 0.8–0.9) and a normalized standard deviation closer to 1. However, EQM generally demonstrates more robust and consistent performance, particularly in terms of correlation and RMS error reduction. On a monthly scale, the superiority of EQM is most evident in June, September, and October. Following the merging process, the final dataset, which incorporates satellite information in addition to in situ observations, demonstrates higher performance. It shows improvements in the coefficient of determination by 83%, bias by 11.4%, mean error by 96.7%, and root-mean-square error by 95.5%. The operational implementation of this approach provides substantial support for decision-making in regions heavily reliant on rainfed agriculture and sensitive to climate variability. Delivering more precise and reliable precipitation datasets enables more informed decisions and significantly enhances policy-making processes in the agricultural and water resources sectors of Burkina Faso. Full article
Show Figures

Figure 1

Figure 1
<p>Spatial distribution of annual precipitation with rain gauge network in the study area.</p>
Full article ">Figure 2
<p>Flow chart describing the steps of the satellite–rain gauge data merging approach.</p>
Full article ">Figure 3
<p>Schematic of the quantile mapping method, with a blue arrow highlighting the quantile-based systematic bias. Adapted from [<a href="#B46-climate-12-00226" class="html-bibr">46</a>].</p>
Full article ">Figure 4
<p>Spatial distribution of rain gauge stations across Burkina Faso (<b>a</b>) and percentage of data completeness at quality-controlled stations for the period 1991–2020 (<b>b</b>). The color scale indicates the percentage of available daily precipitation records at each station.</p>
Full article ">Figure 5
<p>Comparison of average daily precipitation between TAMSAT corrected by TSV (<b>b</b>) and EQM (<b>c</b>) with reference from in situ observations (<b>a</b>).</p>
Full article ">Figure 6
<p>Taylor diagram illustrating the statistics of inter-comparison between three datasets: uncorrected, TSV corrected and EQM corrected for the period of 1991–2020.</p>
Full article ">Figure 7
<p>Taylor diagram illustrating the statistics of inter-comparison between three precipitation datasets at a monthly scale for the wet season.</p>
Full article ">Figure 8
<p>Comparison of extreme daily precipitation between TAMSAT corrected by TSV (<b>b</b>) and EQM (<b>c</b>) with reference from in situ observations (<b>a</b>).</p>
Full article ">Figure 9
<p>Average daily precipitation from TAMSAT satellite data corrected using (<b>a</b>) EQM method and (<b>b</b>) merging the bias-corrected datasets with rain gauge data using the merging approach, both compared with ground-based observations.</p>
Full article ">Figure 10
<p>The spatial distribution of the merging for rainy events on 7 May 2010 (<b>top</b>), 29 July 2010 (<b>middle</b>), and 6 October 2010 (<b>bottom</b>). These three periods correspond to the early season, mid-season, and the end season of the wet season, respectively. Dataset sources are station observations (<b>a</b>,<b>d</b>,<b>g</b>), original TAMSAT data (<b>b</b>,<b>e</b>,<b>h</b>), and merged products (<b>c</b>,<b>f</b>,<b>i</b>).</p>
Full article ">
17 pages, 2438 KiB  
Review
Recent Advances in the Synthesis and Photoelectrocatalysis of Zeolite-Based Composites
by Yitong Zhao, Meng Liu, Yingshuo Guo and Zhijie Wu
Catalysts 2024, 14(12), 938; https://doi.org/10.3390/catal14120938 - 18 Dec 2024
Viewed by 368
Abstract
Zeolites are a class of porous aluminosilicates possessing high surface area, good hydrothermal stability, strong sorption, and high ion-exchanging potential, and which frequently serve as efficient catalytic materials. The composites which integrate zeolite with alternative substances like metal oxides or carbon-based materials steadily [...] Read more.
Zeolites are a class of porous aluminosilicates possessing high surface area, good hydrothermal stability, strong sorption, and high ion-exchanging potential, and which frequently serve as efficient catalytic materials. The composites which integrate zeolite with alternative substances like metal oxides or carbon-based materials steadily outperform individual constituents. Recently, the application of zeolite-based composites in the field of photocatalytic oxidation and electrocatalytic oxidation/reduction, which is mainly focused on pollution treatment in sewage and air, have garnered significant attention. Several synthesis strategies for zeolite-based composites including post-treatment and in situ hydrothermal synthesis methods are explicated. Meanwhile, multifarious types of zeolite-based photoelectric catalytic composites are also summarized. Finally, we highlight the advancements improving the performance of zeolite-based composites in the photocatalytic treatment of organic pollutants in wastewater and the electrocatalytic reduction of CO2 and organics. Full article
(This article belongs to the Special Issue State of the Art and Future Challenges in Zeolite Catalysts)
Show Figures

Figure 1

Figure 1
<p>The structure of the nanofiber membrane functionalized with silver nanoparticles. (Reprinted with permission from reference [<a href="#B19-catalysts-14-00938" class="html-bibr">19</a>]. Copyright 2011 Journal of Membrane Science.)</p>
Full article ">Figure 2
<p>The design and preparation process of metal-modified TS-1 composites (M@TS-1) and the downstream product of furfural oxidation. (Reprinted with permission from reference [<a href="#B44-catalysts-14-00938" class="html-bibr">44</a>]. Copyright 2024 Applied Catalysis B: Environmental.)</p>
Full article ">Figure 3
<p>Schematic diagram of two-dimensional honeycomb-like ZnO nanowalls/zeolite. (<b>a</b>,<b>b</b>) ball models of zeolite, (<b>c</b>) (1 0 0) crystal surface, (<b>d</b>) (0 0 2) crystal surface, (<b>e</b>,<b>f</b>) two-dimensional honeycomb-like ZnO nanowalls and (<b>g</b>) a honeycomb. (Reprinted with permission from reference [<a href="#B37-catalysts-14-00938" class="html-bibr">37</a>]. Copyright 2014 Chemical Engineering Journal.)</p>
Full article ">Figure 4
<p>Schematic diagram of the preparation process of CZP. (Reprinted with permission from reference [<a href="#B52-catalysts-14-00938" class="html-bibr">52</a>]. Copyright 2024 Journal of Solid State Chemistry.)</p>
Full article ">Figure 5
<p>The photodegradation mechanism of MB by RGO@Pt/Ti-MFI-NSs composites. (Reprinted with permission from reference [<a href="#B42-catalysts-14-00938" class="html-bibr">42</a>]. Copyright 2018 Microporous and Mesoporous Materials.)</p>
Full article ">Figure 6
<p>The proposed mechanism of TC degradation by TiO<sub>2</sub>/BEA ion-exchanged photocatalysts under visible light. (Reprinted with permission from reference [<a href="#B61-catalysts-14-00938" class="html-bibr">61</a>]. Copyright 2024 Heliyon.)</p>
Full article ">Figure 7
<p>The electric degradation mechanism of m-nitrophenol by PbO<sub>2</sub>-zeo composites. (Reprinted with permission from reference [<a href="#B65-catalysts-14-00938" class="html-bibr">65</a>]. Copyright 2024 Journal of Environmental Chemical Engineering).</p>
Full article ">
12 pages, 6125 KiB  
Article
Real-Time Operational Trial of Atmosphere–Ocean–Wave Coupled Model for Selected Tropical Cyclones in 2024
by Sin Ki Lai, Pak Wai Chan, Yuheng He, Shuyi S. Chen, Brandon W. Kerns, Hui Su and Huisi Mo
Atmosphere 2024, 15(12), 1509; https://doi.org/10.3390/atmos15121509 - 17 Dec 2024
Viewed by 382
Abstract
An atmosphere–ocean–wave coupled regional model, the UWIN-CM, began its operational trial in real time at the Hong Kong Observatory (HKO) in the second half of 2024. Its performance in the analysis of three selected tropical cyclones, Severe Tropical Storm Prapiroon, Super Typhoon Gaemi, [...] Read more.
An atmosphere–ocean–wave coupled regional model, the UWIN-CM, began its operational trial in real time at the Hong Kong Observatory (HKO) in the second half of 2024. Its performance in the analysis of three selected tropical cyclones, Severe Tropical Storm Prapiroon, Super Typhoon Gaemi, and Super Typhoon Yagi, are studied in this paper. The forecast track and intensity of the tropical cyclones were verified against the operational analysis. It is shown that the track error of the UWIN-CM was lower than other regional numerical weather prediction (NWP) models in operation at the HKO, with a reduction in mean direct positional error of up to 50% for the first 48 forecast hours. For cyclone intensity, the performance of the UWIN-CM was the best out of the available global and regional models at HKO for Yagi at forecast hours T + 36 to T + 84 h. The model captured the rapid intensification of Yagi over the SCS with a lead time of 24 h or more. The forecast winds were compared with the in situ measurements of buoy and with the wind field analysis obtained from synthetic-aperture radar (SAR). The correlation of forecast winds with measurements from buoy and SAR ranged between 65–95% and 50–70%, respectively. The model was found to perform generally satisfactorily in the above comparisons. Full article
(This article belongs to the Special Issue Tropical Cyclones: Observations and Prediction (2nd Edition))
Show Figures

Figure 1

Figure 1
<p>(<b>a</b>) Domain configuration of the coupled model UWIN-CM. Atmospheric model WRF consists of 3 domains, denoted by d01, d02, and d03, with a horizontal resolution of 12 km, 4 km, and 1.33 km, respectively. Ocean model HYCOM consists of 1 domain (denoted by the purple box) with a horizontal resolution of 0.04 degrees. Wave model UMWM3 consists of 1 domain, which coincides with d02 of WRF with a horizontal resolution of 4 km. (<b>b</b>) Major exchange fields among models in the UWIN-CM at regular time intervals as defined by the time step. Field exchange is enabled by coupler ESMF.</p>
Full article ">Figure 2
<p>Forecast tracks of various initial times of model runs for (<b>a</b>) Prapiroon, (<b>b</b>) Gaemi, and (<b>c</b>) Yagi. The initial times of the model runs are denoted in the legend. The red stars denoted as “HKO Warn” are the HKO warning positions or, equivalently, the operational analysis positions of the TCs.</p>
Full article ">Figure 3
<p>(<b>a</b>) Zoom-in of the forecast track of Gaemi when it was close to landfall over Taiwan for various model initial times. (<b>b</b>) Forecast track of various global models with the initial time of 24 Jul 00Z for Gaemi. (<b>c</b>) Zoom-in of the forecast landfall location of Yagi for various model initial times of the UWIN-CM. (<b>d</b>) Forecast track of various regional models available in HKO. In (<b>a</b>,<b>c</b>), the initial time of model runs are denoted in the legend. The red stars denoted as “HKO Warn” are the HKO warning positions or, equivalently, the analysis positions of the TC centre. The HKO warning positions are in 3 hourly intervals. The model output data are in hourly intervals.</p>
Full article ">Figure 4
<p>Scatter plots of model forecast intensity against HKO warning intensity, or, equivalently, analysis intensity, for various model runs in terms of maximum wind speed of TC (<b>a</b>) Prapiroon, (<b>b</b>) Gaemi, (<b>c</b>) and Yagi. Dotted lines are the best-fit curve with the equation shown at the top-left corner of the figures.</p>
Full article ">Figure 5
<p>(<b>a</b>) Time series of forecast intensity of Yagi at model initial time of (<b>a</b>) 00Z 2 Sept and (<b>b</b>) 00Z 3 Sept. Also showed are the HKO warning intensity. The time range shaded with light blue is the time where Yagi underwent RI according to HKO warning intensity. Time stamps in the horizontal axis are month-date followed by hours in UTC.</p>
Full article ">Figure 6
<p>Scatter plots of forecasted 10-metre wind speeds and wind direction against the corresponding measured metrics at Maoming buoy located at 20.7° N, 111.7° E for Prapiroon ((<b>a</b>) for winds speed, (<b>b</b>) for wind direction) and for Yagi ((<b>c</b>) for wind speed, (<b>d</b>) for wind direction) for model runs listed in <a href="#atmosphere-15-01509-f002" class="html-fig">Figure 2</a>. Corresponding plots for Gaemi ((<b>e</b>) for wind speed, (<b>f</b>) for wind direction) with measurements taken from Buoy TTU01 located at 21.2° N, 123.9° E. Dotted lines are the best-fit curve with the equation shown at the top-left corner of the figures. For (<b>d</b>,<b>f</b>), as a number of data correspond to wind direction close to 0 and 360 degrees, metrics like best-fit equation, correlation coefficient, and RMSE cannot reflect their similar northerly direction and are thus not used. The dotted line in (<b>d</b>,<b>f</b>) represents x = y guidance to the eye.</p>
Full article ">Figure 7
<p>Forecast wind speed against wind speed from synthetic aperture radar (SAR) measurements for (<b>a</b>) Prapiroon, (<b>b</b>) Gaemi, and (<b>c</b>) Yagi. The timestamp of the SAR image used in (<b>a</b>) is valid at 21 Jul 10:49Z and is compared against model forecast at 21 Jul 11Z. The SAR image used in (<b>b</b>) is valid at 22 Jul 09:52Z and is compared against model forecast at 22 Jul 10Z. The SAR image used in (<b>c</b>) is valid at 05 Sep 10:33Z and is compared against model forecast at 05 Sep 11Z. Dotted lines are the best-fit curves, with the equation shown at the top-left corner of the figures. (<b>d</b>) Contour plot of model wind speed subtracting SAR-measured wind speed for the same SAR images and model forecast used in (<b>c</b>) for Yagi.</p>
Full article ">
17 pages, 5303 KiB  
Article
Carbon Soil Mapping in a Sustainable-Managed Farm in Northeast Italy: Geochemical and Geophysical Applications
by Gian Marco Salani, Enzo Rizzo, Valentina Brombin, Giacomo Fornasari, Aaron Sobbe and Gianluca Bianchini
Environments 2024, 11(12), 289; https://doi.org/10.3390/environments11120289 - 14 Dec 2024
Viewed by 537
Abstract
Recently, there has been increasing interest in organic carbon (OC) certification of soil as an incentive for farmers to adopt sustainable agricultural practices. In this context, this pilot project combines geochemical and geophysical methods to map the distribution of OC contents in agricultural [...] Read more.
Recently, there has been increasing interest in organic carbon (OC) certification of soil as an incentive for farmers to adopt sustainable agricultural practices. In this context, this pilot project combines geochemical and geophysical methods to map the distribution of OC contents in agricultural fields, allowing us to detect variations in time and space. Here we demonstrated a relationship between soil OC contents estimated in the laboratory and the apparent electrical conductivity (ECa) measured in the field. Specifically, geochemical elemental analyses were used to evaluate the OC content and relative isotopic signature in collected soil samples from a hazelnut orchard in the Emilia–Romagna region of Northeastern Italy, while the geophysical Electromagnetic Induction (EMI) method enabled the in situ mapping of the ECa distribution in the same soil field. According to the results, geochemical and geophysical data were found to be reciprocally related, as both the organic matter and soil moisture were mainly incorporated into the fine sediments (i.e., clay) of the soil. Therefore, such a relation was used to create a map of the OC content distribution in the investigated field, which could be used to monitor the soil C sequestration on small-scale farmland and eventually develop precision agricultural services. In the future, this method could be used by farmers and regional and/or national policymakers to periodically certify the farm’s soil conditions and verify the effectiveness of carbon sequestration. These measures would enable farmers to pursue Common Agricultural Policy (CAP) incentives for the reduction of CO2 emissions. Full article
Show Figures

Figure 1

Figure 1
<p>(<b>a</b>) Location of the sampling area (MB), in the Northeast sector of the municipality of Ferrara in the Emilia–Romagna region (Northeastern Italy); (<b>b</b>) the hazel orchard–grassland field before the geochemical and geophysical investigation of 19 October 2021; (<b>c</b>) soil sampling locations represented by light blue dots; (<b>d</b>) at each location, a sample was collected and mixed with five aliquots of soil per square probed at a depth of 0–30 cm; (<b>e</b>) geophysical measurements were indicated with red dots and georeferenced with an internal GPR; and (<b>f</b>) a Profiler EMP-400 (GSSI) was used to acquire the Hp and Hs electromagnetic fields at different positions.</p>
Full article ">Figure 2
<p>Elemental and isotopic composition of the total carbon (TC), organic carbon (OC), and inorganic carbon (IC) fractions of the soil samples.</p>
Full article ">Figure 3
<p>Boxplots of the (<b>a</b>) LOI 105 °C, (<b>b</b>) LOI 550 °C, (<b>c</b>) LOI 1000 °C, (<b>d</b>) TC, (<b>e</b>) OC, (<b>f</b>) IC, (<b>g</b>) δ<sup>13</sup>C<sub>TC</sub>, and (<b>h</b>) δ¹³C<sub>OC</sub> of the samples divided into three classes based on their aspect in the field and OC/IC ratio (see the text for details). In each box plot, the black line represents the median. Letters below the box plots represent the results of the Tukey post hoc test. Different letters denote significant differences between classes. The one-way ANOVA results are also reported (** <span class="html-italic">p</span> &lt; 0.001; *** <span class="html-italic">p</span> &lt; 0.0001).</p>
Full article ">Figure 4
<p>Spatial variability and distribution of the ECa values obtained from the EMI acquisition field survey using three different frequencies: (<b>a</b>) 16, (<b>b</b>) 14, and (<b>c</b>) 10 kHz.</p>
Full article ">Figure 5
<p>The elemental TC contents and δ¹³C<sub>TC</sub> of MB samples and average elemental TC contents and δ¹³C<sub>TC</sub> recognized as deposits from the paleochannel and levee of the easternmost Padanian plain soils, as studied by Natali et al. [<a href="#B36-environments-11-00289" class="html-bibr">36</a>] and Salani et al. [<a href="#B37-environments-11-00289" class="html-bibr">37</a>].</p>
Full article ">Figure 6
<p>OC/IC (in logarithmic scale) versus (<b>a</b>) δ<sup>13</sup>C<sub>TC</sub> shows a strong negative correlation; the insets reproduce the relationships between OC/IC, (<b>b</b>) δ<sup>13</sup>C<sub>IC</sub>, and (<b>c</b>) δ<sup>13</sup>C<sub>OC</sub>.</p>
Full article ">Figure 7
<p>Principal Component Analysis (PCA) for δ<sup>13</sup>CTC, OC, IC, TC, and ECa (measured at 10 kHz), clustered in Class I (green dots and dash-dotted line ellipse), Class II (yellow triangles and solid line ellipse), and Class III (red squares and dashed line ellipse).</p>
Full article ">Figure 8
<p>Linear regression graphics used to observe the relationships between the ECa measured at 10 kHz and (<b>a</b>) OC, (<b>b</b>) OC/IC, and (<b>c</b>) δ<sup>13</sup>C<sub>TC</sub>. The data are represented as green dots, yellow triangles, and red squares, for Class I, Class II, and Class III, respectively. The regression line (in black) and relative equation, R<sup>2</sup> value, and 95% confidence intervals (the red curves) are provided for each plot.</p>
Full article ">Figure 9
<p>Predictive maps realized using ordinary kriging for (<b>a</b>) the OC values, (<b>b</b>) the ECa values measured at 10 kHz, and cokriging to predict (<b>c</b>) a new OC surface, with the OC values and the ECa values at 10 kHz as a covariate variable. The legend values for each map represent a quantile classification.</p>
Full article ">
11 pages, 3932 KiB  
Article
Influence of Complex Lithology Distribution on Fracture Propagation Morphology in Coalbed Methane Reservoir
by Weiping Ouyang, Luoyi Huang, Jinghua Liu, Mian Zhang and Guanglong Sheng
Appl. Sci. 2024, 14(24), 11681; https://doi.org/10.3390/app142411681 - 14 Dec 2024
Viewed by 368
Abstract
The mineral composition in coalbed methane (CBM) reservoirs significantly influences fracture morphology, making the description of reservoir heterogeneity challenging. This study develops a fracture propagation model for CBM reservoirs that incorporates the varying mineral properties within the reservoir’s lithology. Dynamic logging data are [...] Read more.
The mineral composition in coalbed methane (CBM) reservoirs significantly influences fracture morphology, making the description of reservoir heterogeneity challenging. This study develops a fracture propagation model for CBM reservoirs that incorporates the varying mineral properties within the reservoir’s lithology. Dynamic logging data are considered to characterize rock mechanical properties, which form the basis for in situ stress estimation. Using an adjusted critical circumferential stress calculation for coal rock, the model considers the impact of complex lithology on fracture propagation. A comprehensive fractal index is introduced to capture the influence of different minerals on fracture morphology and propagation randomness. Models representing clay, quartz, and pyrite with varied compositions were constructed to explore the effects of each mineral on fracture characteristics. In single-component models, clay-rich reservoirs exhibited the highest induced fracture density, with quartz and pyrite showing approximately 65% and 20% of the fracture density observed in clay, respectively. Fractures primarily propagated toward quartz-rich regions, while pyrite significantly inhibited fracture growth. In mixed-mineral models, increasing the quartz proportion by 40% resulted in a 20 m increase in fracture length and a 30% reduction in fracture density. Fractures predominantly propagated around pyrite boundaries, demonstrating pyrite’s resistance to fracture penetration. Clay and quartz promote fracture development, whereas pyrite hinders fracture formation. The fracture inversion model presented here effectively captures the influence of complex mineral distributions on fracture morphology, offering valuable insights for optimizing fracturing production strategies. Full article
(This article belongs to the Special Issue Artificial Intelligence (AI) in Enhanced Oil Recovery)
Show Figures

Figure 1

Figure 1
<p>Node connection system of CBM reservoirs.</p>
Full article ">Figure 2
<p>The direction distribution of fracture propagation based on random function and probability distribution.</p>
Full article ">Figure 3
<p>Hydraulic fracture propagation model with different lithologies.</p>
Full article ">Figure 4
<p>Hydraulic fracture propagation process considering different lithologies.</p>
Full article ">Figure 5
<p>Actual microseismic monitoring of fracture morphology.</p>
Full article ">Figure 6
<p>Microseismic data points and fracture morphology.</p>
Full article ">Figure 7
<p>Fracture morphology of a single mineral.</p>
Full article ">Figure 8
<p>Fracture morphology of different proportions of quartz and clay.</p>
Full article ">Figure 9
<p>Fracture morphology of different proportions of pyrite and clay.</p>
Full article ">Figure 10
<p>Fracture morphology of different proportions of minerals. (<b>a</b>) The proportion of clay, quartz, and pyrite is 2:2:1; (<b>b</b>) The proportion of clay, quartz, and pyrite is 1:1:1; (<b>c</b>) The proportion of clay, quartz, and pyrite is 1:2:2.</p>
Full article ">
13 pages, 4116 KiB  
Article
Unveiling the Influence of Activation Protocols on Cobalt Catalysts for Sustainable Fuel Synthesis
by M. Amine Lwazzani, Andrés A. García Blanco, Martí Biset-Peiró, Elena Martín Morales and Jordi Guilera
Catalysts 2024, 14(12), 920; https://doi.org/10.3390/catal14120920 - 13 Dec 2024
Viewed by 391
Abstract
The Fischer–Tropsch Synthesis process is projected to have a significant impact in the near future due to its potential for synthesizing sustainable fuels from biomass, carbon dioxide and organic wastes. In this catalytic process, catalyst activation plays a major role in the overall [...] Read more.
The Fischer–Tropsch Synthesis process is projected to have a significant impact in the near future due to its potential for synthesizing sustainable fuels from biomass, carbon dioxide and organic wastes. In this catalytic process, catalyst activation plays a major role in the overall performance of Fischer–Tropsch Synthesis. Catalyst activation temperatures are considerably higher than the typical operating conditions of industrial reactors. Consequently, ex situ activation is often required for industrial Fischer–Tropsch Synthesis processes. This study evaluated the influence of different activation approaches (in situ, ex situ, passivation and low-temperature activation). Catalytic experiments were conducted in a fixed-bed reactor at 230 °C and 20 bar·g using a reference supported Co/γ-Al2O3 catalyst. Experimental results demonstrate that catalysts can be effectively reduced ex situ. This work reveals that re-activation of the catalyst after ex situ reduction is unnecessary, as the reaction conditions themselves re-reduce any superficial oxides formed, owing to the reducing nature of the reactant mixture. This approach could simplify reactor design by enabling temperature requirements to match operating conditions (e.g., 230 °C), thereby reducing both investment and operational costs and eliminating additional catalyst preparation steps. Full article
Show Figures

Figure 1

Figure 1
<p>(<b>Left</b>) Cross-section of the reference Co catalyst under electron microscopy. (<b>Right</b>) Mapping of the Co presence, in yellow spots, in the same catalyst particle.</p>
Full article ">Figure 2
<p>XRD diffraction patterns of the catalyst samples.</p>
Full article ">Figure 3
<p>XRD of the ex situ reduced sample after 15 and 48 h air exposition. * represents the metallic Co peak.</p>
Full article ">Figure 4
<p>TPR profiles of the reduced catalysts.</p>
Full article ">Figure 5
<p>DRIFT spectra of the different reduction procedure samples.</p>
Full article ">Figure 6
<p>Conversion results of the reduced catalysts under FTS conditions, 20 bar·g and 230 °C.</p>
Full article ">Figure 7
<p>DRIFT of the ex situ catalyst under reaction conditions showing active CO chemisorption sites.</p>
Full article ">Figure 8
<p>Methane Selectivity of the catalysts.</p>
Full article ">
20 pages, 21853 KiB  
Article
Thermal Evolution of Expanded Phases Formed by PIII Nitriding in Super Duplex Steel Investigated by In Situ Synchrotron Radiation
by Bruna Corina Emanuely Schibicheski Kurelo, João Frederico Haas Leandro Monteiro, Gelson Biscaia de Souza, Francisco Carlos Serbena, Carlos Maurício Lepienski, Rodrigo Perito Cardoso and Silvio Francisco Brunatto
Metals 2024, 14(12), 1396; https://doi.org/10.3390/met14121396 - 5 Dec 2024
Viewed by 552
Abstract
The Plasma Immersion Ion Implantation (PIII) nitriding was used to form a modified layer rich in expanded austenite (γN) and expanded ferrite (αN) phases in super duplex steel. The thermal stability of these phases was investigated through the in [...] Read more.
The Plasma Immersion Ion Implantation (PIII) nitriding was used to form a modified layer rich in expanded austenite (γN) and expanded ferrite (αN) phases in super duplex steel. The thermal stability of these phases was investigated through the in situ synchrotron X-ray diffraction. All the surfaces were analyzed by SEM, EDS, and nanoindentation. During the heating stage of the thermal treatments, the crystalline structure of the γN phase expanded thermally up to a temperature of 350 °C and, above this temperature, a reduction in the lattice parameter was observed due to the diffusion of nitrogen into the substrate. During the isothermal heating, the gradual diffusion of nitrogen continued and the lattice parameter of the γN phase decreased. Increasing the treatment temperature from 450 °C to 550 °C, a greater reduction in the lattice parameter of the γN phase occured and the peaks related to the CrN, α, and αN phases became more evident in the diffractograms. This phenomenon is associated with the decomposition of the γN phase into CrN + α + αN. After the heat treatments, the thickness of the modified layers increased and the hardness values close to the surface decreased, according to the diffusion of the nitrogen to the substrate. Full article
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Experimental setup for thermal treatments using in situ synchrotron X-ray diffraction.</p>
Full article ">Figure 2
<p>Scanning electron microscopy images of cross-sectioned samples to visualize the layers formed by nitriding: (<b>a</b>) 350-4; (<b>b</b>) TT450; and (<b>c</b>) TT550.</p>
Full article ">Figure 3
<p>Nitrogen concentration, in at.%, for (<b>a</b>) the 350-4 condition measured in the ferrite and austenite grains, and (<b>b</b>) a comparison between nitrogen concentrations of the nitrided sample (350-4) and the thermally treated sample at 550 °C (TT550). (<b>c</b>,<b>d</b>) The EDS spectra for selected points in (<b>a</b>). N1s peaks are clearly seen at top surfaces while, in measurements taken deeper, they are indistinguishable from the background.</p>
Full article ">Figure 4
<p>(<b>a</b>) Diffractograms of duplex steel UNS S32750 in the untreated condition and of two samples nitrided at 350 °C for 4 h (350-4). These nitrided samples were subsequently and separately submitted to heat treatments at 450 °C (TT450) and 550 °C (TT550). In the inset (<b>b</b>), the normalized diffractograms are presented for better visualization of the contribution of the α<sub>N</sub> phase peaks in the diffractograms.</p>
Full article ">Figure 5
<p>X-ray diffractograms of the TT450 condition at various temperatures during the heating stage, up to 450 °C. The inset shows the enlarged region with the main peaks of austenite and ferrite.</p>
Full article ">Figure 6
<p>(<b>a</b>) X-ray diffractograms of the TT450 condition at various times during the isothermal heating at 450 °C. The inset (<b>b</b>) shows the enlarged region of the main peaks of austenite and ferrite. In (<b>c</b>), a comparison is shown between the first (start) and the last (108 min) diffractograms at 450 °C.</p>
Full article ">Figure 7
<p>X-ray diffractograms of the TT450 condition at room temperature, taken before and after heat treatment, with incidence angles (<b>a</b>) θ = 10° and (<b>b</b>) θ = 2°.</p>
Full article ">Figure 7 Cont.
<p>X-ray diffractograms of the TT450 condition at room temperature, taken before and after heat treatment, with incidence angles (<b>a</b>) θ = 10° and (<b>b</b>) θ = 2°.</p>
Full article ">Figure 8
<p>Variation of the average lattice parameters of the austenite, ferrite, expanded austenite, and expanded ferrite phases during (<b>a</b>) the heating stage and (<b>b</b>) the isothermal treatment, as a function of temperature and time, respectively, for the TT450 condition.</p>
Full article ">Figure 8 Cont.
<p>Variation of the average lattice parameters of the austenite, ferrite, expanded austenite, and expanded ferrite phases during (<b>a</b>) the heating stage and (<b>b</b>) the isothermal treatment, as a function of temperature and time, respectively, for the TT450 condition.</p>
Full article ">Figure 9
<p>(<b>a</b>) Variation of the lattice parameter of the expanded austenite phase during the isothermal treatment, calculated from the interplanar distances of different crystallographic orientations, for the TT450 condition. In (<b>b</b>), the crystal structure of austenite simulated by the Vesta 3 software [<a href="#B39-metals-14-01396" class="html-bibr">39</a>] is shown, highlighting the diffraction planes (111), (200), and (220).</p>
Full article ">Figure 10
<p>X-ray diffractograms during the heating stage at various temperatures for the condition heat-treated up to 550 °C (TT550). The inset shows the region of the main peaks of austenite (γ), ferrite (α), expanded austenite (γ<sub>N</sub>), expanded ferrite (α<sub>N</sub>), and CrN.</p>
Full article ">Figure 11
<p>(<b>a</b>) X-ray diffractograms of the TT550 condition at various times during the isothermal treatment at 550 °C. The inset (<b>b</b>) shows the enlarged region of the main peaks of austenite and ferrite and (<b>c</b>) shows a comparison between the first and the last diffractogram obtained at 550 °C.</p>
Full article ">Figure 12
<p>X-ray diffractograms of the TT550 condition at room temperature, taken before and after heat treatment, with incidence angles (<b>a</b>) θ = 10° and (<b>b</b>) θ = 2°.</p>
Full article ">Figure 13
<p>Variation of the lattice parameter of the austenite, ferrite, expanded austenite, and expanded ferrite phases during (<b>a</b>) the heating stage and (<b>b</b>) the isothermal treatment, as a function of temperature and time, respectively, for the TT550 condition.</p>
Full article ">Figure 14
<p>(<b>a</b>) Hardness and (<b>b</b>) elastic modulus profiles of the nitrided duplex steel compared with the heat-treated conditions TT450 and TT550. The dashed line in (<b>a</b>) indicates the substrate hardness value.</p>
Full article ">Figure 14 Cont.
<p>(<b>a</b>) Hardness and (<b>b</b>) elastic modulus profiles of the nitrided duplex steel compared with the heat-treated conditions TT450 and TT550. The dashed line in (<b>a</b>) indicates the substrate hardness value.</p>
Full article ">
17 pages, 9855 KiB  
Article
A Rod-like Bi2O3 Photocatalyst Derived from Bi-Based MOFs for the Efficient Adsorption and Catalytic Reduction of Cr(VI)
by Qin Fang, Luying Chen, Qiucheng Fu, Yongjuan Chen, Jiao He, Liang Jiang, Zhiying Yan and Jiaqiang Wang
Int. J. Mol. Sci. 2024, 25(23), 13052; https://doi.org/10.3390/ijms252313052 - 4 Dec 2024
Viewed by 491
Abstract
Heavy metal ion pollution poses a serious threat to the natural environment and human health. Photoreduction through Bi-based photocatalysts is regarded as an advanced green technology for solving environmental problems. However, their photocatalytic activity is limited by the rapid recombination of photogenerated e [...] Read more.
Heavy metal ion pollution poses a serious threat to the natural environment and human health. Photoreduction through Bi-based photocatalysts is regarded as an advanced green technology for solving environmental problems. However, their photocatalytic activity is limited by the rapid recombination of photogenerated e and h+ pairs and a low photo-quantum efficiency. In this work, an optimal precursor of Bi-based MOFs was identified by using different solvents, and rod-like Bi2O3 materials were derived by in situ oxidation of Bi atoms in the precursor. The adsorption and photocatalytic reduction efficiency of the prepared Bi2O3 materials for Cr(VI) were evaluated under visible light irradiation. The results showed that the prepared materials had a large specific surface area and enhanced visible light absorption. Bi2O3(DMF/MeOH-3)-400 had a large specific surface area and many active adsorption sites, and it had the highest adsorption of Cr(VI) (49.13%) among the materials. Bi2O3(DMF/MeOH-3)-400 also had the highest photocatalytic reduction efficiency, and it achieved 100% removal of 10 mg·L−1 Cr(VI) within 90 min under light. In addition, the material showed remarkable stability after three consecutive photocatalytic cycles. The enhanced photocatalytic performance was mainly attributed to the fast separation of electron–hole pairs and efficient electron transfer in the MOF-derived materials, which was confirmed by electrochemical tests and PL spectroscopy. Reactive species trapping experiments confirmed that electrons were the main active substances; accordingly, a possible photocatalytic mechanism was proposed. In conclusion, this work provides a new perspective for designing novel photocatalysts that can facilitate the removal of Cr(VI) from water. Full article
(This article belongs to the Special Issue Properties and Applications of Nanoparticles and Nanomaterials)
Show Figures

Figure 1

Figure 1
<p>XRD patterns of Bi-BTC precursors and the as-prepared samples at 300 °C, 400 °C, and 500 °C (<b>a</b>), and using different solvents (<b>b</b>).</p>
Full article ">Figure 2
<p>SEM images: (<b>a</b>) Bi-BTC(DMF/MeOH-3), (<b>b</b>) Bi<sub>2</sub>O<sub>3</sub>(DMF/MeOH-3)-400, (<b>c</b>) Bi<sub>2</sub>O<sub>3</sub>(DMF)-400, and (<b>d</b>) Bi<sub>2</sub>O<sub>3</sub>(MeOH)-400.</p>
Full article ">Figure 3
<p>(<b>a</b>–<b>c</b>) TEM images of Bi<sub>2</sub>O<sub>3</sub>(DMF/MeOH-3)-400, and (<b>d</b>) HRTEM image of Bi<sub>2</sub>O<sub>3</sub> (DMF/MeOH-3)-400.</p>
Full article ">Figure 4
<p>N<sub>2</sub> adsorption–desorption isotherms were used to obtain the specific surface area and pore structure of Bi-BTC (<b>a</b>) and the as-prepared samples (<b>b</b>).</p>
Full article ">Figure 5
<p>XPS spectra of Bi<sub>2</sub>O<sub>3</sub>(DMF/MeOH-3)-400: (<b>a</b>) survey scan, (<b>b</b>) Bi 4f, (<b>c</b>) O 1s, and (<b>d</b>) C 1s.</p>
Full article ">Figure 6
<p>FT−IR spectrum of the Bi<sub>2</sub>O<sub>3</sub>(DMF/MeOH-3)-400 samples.</p>
Full article ">Figure 7
<p>(<b>a</b>) UV−Vis DRS spectra and (<b>b</b>) Tauc plots of as-prepared samples.</p>
Full article ">Figure 8
<p>Photocatalytic reduction performance for Cr(VI) by the as-prepared samples and commercial Bi<sub>2</sub>O<sub>3</sub> (<b>a</b>). The corresponding apparent first−order reaction kinetics curve (<b>b</b>).</p>
Full article ">Figure 9
<p>Performance of the photocatalyst in the reduction of Cr(VI) at different initial pH values (<b>a</b>). The corresponding apparent first−order reaction kinetics curve (<b>b</b>).</p>
Full article ">Figure 10
<p>(<b>a</b>) Reusability of Bi<sub>2</sub>O<sub>3</sub>(DMF/MeOH-3)-400 in the photocatalytic reduction of Cr(VI). Comparison of (<b>b</b>) XRD patterns, (<b>c</b>) XPS survey before and after Bi<sub>2</sub>O<sub>3</sub>(DMF/MeOH-3)-400 was used. (<b>d</b>) Cr 2p spectra after Bi<sub>2</sub>O<sub>3</sub>(DMF/MeOH-3)-400 was used.</p>
Full article ">Figure 11
<p>(<b>a</b>) Steady−state PL spectra, (<b>b</b>) EIS Nyquist plots, and (<b>c</b>) TPR plots of prepared Bi<sub>2</sub>O<sub>3</sub> and commercial Bi<sub>2</sub>O<sub>3</sub>. (<b>d</b>) Mott−Schottky plots of prepared Bi<sub>2</sub>O<sub>3</sub> at 500, 1000, 1500 Hz.</p>
Full article ">Figure 12
<p>Reactive species trapping experiments of Bi<sub>2</sub>O<sub>3</sub>(DMF/MeOH-3)-400.</p>
Full article ">Scheme 1
<p>Synthetic route of the rod−like Bi<sub>2</sub>O<sub>3</sub> samples.</p>
Full article ">Scheme 2
<p>Proposed photocatalytic mechanism of Bi<sub>2</sub>O<sub>3</sub>(DMF/MeOH−3)-400.</p>
Full article ">
14 pages, 6124 KiB  
Article
Feature Extraction and Attribute Recognition of Aerosol Particles from In Situ Light-Scattering Measurements Based on EMD-ICA Combined LSTM Model
by Heng Zhao, Yanyan Zhang, Dengxin Hua, Jiamin Fang, Jie Zhang and Zewen Yang
Atmosphere 2024, 15(12), 1441; https://doi.org/10.3390/atmos15121441 - 30 Nov 2024
Viewed by 359
Abstract
Accurate identification and monitoring of aerosol properties is crucial for understanding their sources and impacts on human health and the environment. Therefore, we propose a feature extraction and attribute recognition method from in situ light-scattering measurements based on Bayesian Optimization, wavelet scattering transform, [...] Read more.
Accurate identification and monitoring of aerosol properties is crucial for understanding their sources and impacts on human health and the environment. Therefore, we propose a feature extraction and attribute recognition method from in situ light-scattering measurements based on Bayesian Optimization, wavelet scattering transform, and long short-term memory neural network (BO-WST-LSTM), with empirical mode decomposition (EMD) and independent component analysis (ICA) algorithm for signal preprocessing. In this study, an experimental platform was utilized to gather light-scattering signals from particles with varying characteristics. The signals are then processed using the EMD-ICA noise reduction technique. Then, the wavelet scattering network is used to realize the adaptive extraction of the characteristics of the particle light-scattering signal, and the Bayesian Optimization model is used to optimize the hyperparameters of the LSTM neural network. The extracted scattering coefficient matrix is input into the LSTM for iterative training. Finally, the SoftMax layer’s probability classification method is applied to the identification of particle attributes. The results show that the multi-angle particle light-scattering signal detection system designed and built in this study performs well and is capable of effectively collecting particle light-scattering signals. At the same time, the proposed new method for particle property recognition demonstrates good classification performance for six different types of particles with a particle size of 2 μm, achieving a classification accuracy of 98.83%. This proves its effectiveness in recognizing particle properties and provides a solid foundation for particle identification. Full article
(This article belongs to the Special Issue Characteristics and Control of Particulate Matter)
Show Figures

Figure 1

Figure 1
<p>Differences in scattering properties of different substances.</p>
Full article ">Figure 2
<p>Particle attribute recognition model based on the BO-WST-LSTM network.</p>
Full article ">Figure 3
<p>Multi-angle detection of particle light-scattering signal system: (<b>a</b>) Schematic diagram of the platform; (<b>b</b>) Physical diagram of the platform.</p>
Full article ">Figure 4
<p>Experimental diagram: (<b>a</b>) Optical path diagram; (<b>b</b>) Local optical path diagram.</p>
Full article ">Figure 5
<p>Denoise model based on EMD-ICA.</p>
Full article ">Figure 6
<p>The decomposition framework of Wavelet scattering transform.</p>
Full article ">Figure 7
<p>Scatter diagram of wavelet scattering of first-order scattering coefficient.</p>
Full article ">Figure 8
<p>Scatter diagram of wavelet scattering of second-order scattering coefficient.</p>
Full article ">Figure 9
<p>Flowchart of Bayesian Optimization.</p>
Full article ">Figure 10
<p>Results of confusion matrix: (<b>a</b>) Confusion matrix of training set; (<b>b</b>) Confusion matrix of test set.</p>
Full article ">
11 pages, 1170 KiB  
Article
Impact of Patient’s Age and Physician’s Professional Background on the Number Needed to Treat in Malignant Melanoma Detection
by Laura Schreieder, Veronika Zenderowski, Mark Berneburg, Sebastian Haferkamp, Konstantin Drexler and Dennis Niebel
Cancers 2024, 16(23), 4014; https://doi.org/10.3390/cancers16234014 - 29 Nov 2024
Viewed by 401
Abstract
Background/Objectives: With regard to excision of pigmented lesions for detection of malignant melanoma (MM), the number needed to treat (NNT) describes the number of melanocytic nevi that need to be biopsied/excised to detect one MM. The aim should be a low NNT. Methods [...] Read more.
Background/Objectives: With regard to excision of pigmented lesions for detection of malignant melanoma (MM), the number needed to treat (NNT) describes the number of melanocytic nevi that need to be biopsied/excised to detect one MM. The aim should be a low NNT. Methods: Single-center data analysis, including dermatohistopathological records of all nevi and MM cases during 2004–2013 at the Department of Dermatology, University Hospital Regensburg (UKR), was performed. We calculated the NNT, correlating it with the patient’s age and referring physician. The MM to MM in situ ratio was calculated to quantify early detection. As a secondary objective, we stratified into a pre- and post-2008 dataset, coinciding with the introduction of statutory skin cancer screening in Germany. Results: The overall NNT of 118,668 pigmented lesions was 17.2. We found a linear decrease in NNT towards older patients (R2 = 62%; p < 0.001). The impact of skin cancer screening in 2008 was marked by a reduction in biopsies/excisions, a shift in age distribution, and a decrease in the NNT from 20.3 to 14.7. Office-based dermatologists had an NNT of 22.3, UKR-based dermatologists had an NNT of 8.0, and non-dermatologists had an NNT of 16.5. Conclusions: The age-related decrease in the NNT emphasizes the importance of age stratification for pigmented lesions. The NNT differed between professional settings. The implementation of skin cancer screening in 2008 was associated with a reduced NNT. Full article
(This article belongs to the Section Cancer Causes, Screening and Diagnosis)
Show Figures

Figure 1

Figure 1
<p>Bar graph displaying the number of nevi (grey, n = 111,767) and malignant melanomas (black, n = 6901) at different ages, ranging from 0 to 98 years. The age with the highest number of excised pigmented lesions was 40. The median age of diagnosis of nevi is 39, while the median age of diagnosis of melanoma is 61.</p>
Full article ">Figure 2
<p>Scatterplot showing the exponentially decreasing trend of the NNT with advancing age, indicating that the proportion of nevi to melanoma decreases in older age.</p>
Full article ">Figure 3
<p>Bar graph displaying the number of diagnoses of nevi (grey) and malignant melanoma (black) at different ages before (<b>A</b>) and after (<b>B</b>) introduction of statutory skin cancer screening in Germany in 2008. The total number of excisions declined (2003–2008: n = 62,112; 2009–2013: n = 56,556), with a shift towards elderly patients. Comparing the periods before and after implementation of the screening, the median age at diagnosis increased by 3 years for nevi (38 to 41 years) and melanomas (59 to 62 years) (<span class="html-italic">p</span> &lt; 0.001).</p>
Full article ">Figure 4
<p>Observed NNT values with 95% confidence intervals (dots with error bars) and the fitted values based on the log-linear regression model (dashed line) over the years 2004 to 2013. The log-linear regression demonstrates a consistent decline in the NNT over time (<span class="html-italic">p</span> &lt; 0.001, adjusted R<sup>2</sup> 72.4%).</p>
Full article ">
Back to TopTop