[go: up one dir, main page]

 
 
Sign in to use this feature.

Years

Between: -

Subjects

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Journals

Article Types

Countries / Regions

Search Results (207)

Search Parameters:
Keywords = diatomite

Order results
Result details
Results per page
Select all
Export citation of selected articles as:
16 pages, 6270 KiB  
Article
C/Co3O4/Diatomite Composite for Microwave Absorption
by Yan Liao, Dashuang Wang, Wenrui Zhu, Zhilan Du, Fanbo Gong, Tuo Ping, Jinsong Rao, Yuxin Zhang and Xiaoying Liu
Molecules 2024, 29(18), 4336; https://doi.org/10.3390/molecules29184336 - 12 Sep 2024
Viewed by 226
Abstract
Transition metal oxides have been widely used in microwave-absorbing materials, but how to improve impedance matching is still an urgent problem. Therefore, we introduced urea as a polymer carbon source into a three-dimensional porous structure modified by Co3O4 nanoparticles and [...] Read more.
Transition metal oxides have been widely used in microwave-absorbing materials, but how to improve impedance matching is still an urgent problem. Therefore, we introduced urea as a polymer carbon source into a three-dimensional porous structure modified by Co3O4 nanoparticles and explored the influence of different heat treatment temperatures on the wave absorption properties of the composite. The nanomaterials, when calcined at a temperature of 450 °C, exhibited excellent microwave absorption capabilities. Specifically, at an optimized thickness of 9 mm, they achieved a minimum reflection loss (RLmin) of −97.3 dB, accompanied by an effective absorption bandwidth (EAB) of 9.83 GHz that comprehensively covered both the S and Ku frequency bands. On the other hand, with a thickness of 3 mm, the RLmin was recorded as −17.9 dB, with an EAB of 5.53 GHz. This excellent performance is attributed to the multi-facial polarization and multiple reflections induced by the magnetic loss capability of Co3O4 nanoparticles, the electrical conductivity of C, and the unique three-dimensional structure of diatomite. For the future development of bio-based microwave absorption, this work provides a methodology and strategy. Full article
(This article belongs to the Special Issue Functional Nanomaterials in Green Chemistry, 2nd Edition)
Show Figures

Figure 1

Figure 1
<p>(<b>a</b>–<b>c</b>) SEM images of C/Co<sub>3</sub>O<sub>4</sub>/De-300, (<b>d</b>–<b>f</b>) C/Co<sub>3</sub>O<sub>4</sub>/De-450, and (<b>g</b>–<b>i</b>) C/Co<sub>3</sub>O<sub>4</sub>/De-600; (<b>j</b>–<b>l</b>) TEM images of C/Co<sub>3</sub>O<sub>4</sub>/De-600; and (<b>m</b>–<b>p</b>) HAADF-EDS element mapping images of Co, C, Si, and O of C/Co<sub>3</sub>O<sub>4</sub>/De-450.</p>
Full article ">Figure 2
<p>(<b>a</b>) XRD patterns and (<b>b</b>) XPS spectra of full survey scan, (<b>c</b>) C 1s spectrum, (<b>d</b>) Co 2p spectrum, (<b>e</b>) O 1s spectrum, and (<b>f</b>) N 1s spectrum of C/Co<sub>3</sub>O<sub>4</sub>/De-450.</p>
Full article ">Figure 3
<p>(<b>a</b>) FTIR spectra, (<b>b</b>) TGA, and (<b>c</b>) magnetic hysteresis loops for C/Co<sub>3</sub>O<sub>4</sub>/De-300, C/Co<sub>3</sub>O<sub>4</sub>/De-450, and C/Co<sub>3</sub>O<sub>4</sub>/De-600.</p>
Full article ">Figure 4
<p>(<b>a</b>) Real part of permittivity, (<b>b</b>) imaginary part of permittivity, and (<b>c</b>) dielectric loss tangent plots of all the samples; (<b>d</b>) real part of permeability, (<b>e</b>) imaginary part of permeability, and (<b>f</b>) dielectric loss tangent plots of all samples.</p>
Full article ">Figure 5
<p>(<b>a</b>) Cole–Cole plots of C/Co<sub>3</sub>O<sub>4</sub>/De-300, (<b>b</b>) C/Co<sub>3</sub>O<sub>4</sub>/De-450, (<b>c</b>) C/Co<sub>3</sub>O<sub>4</sub>/De-600; plots of (<b>d</b>) impedance matching, (<b>e</b>) attenuation constants, and (<b>f</b>) eddy current loss of all the samples.</p>
Full article ">Figure 6
<p>A 3D loss diagram, contour plot of RL with thickness and frequency (S, C, X and Ku bands), and frequency–loss 1D diagram of (<b>a</b>–<b>d</b>) C/Co<sub>3</sub>O<sub>4</sub>/De-300, (<b>e</b>–<b>h</b>) C/Co<sub>3</sub>O<sub>4</sub>/De-450, and (<b>i</b>–<b>l</b>) C/Co<sub>3</sub>O<sub>4</sub>/De-600.</p>
Full article ">Figure 7
<p>Schematic representation of EMW absorption diagram for C/Co<sub>3</sub>O<sub>4</sub>/De-450 composite.</p>
Full article ">Figure 8
<p>The CST simulation results for (<b>a</b>) C/Co<sub>3</sub>O<sub>4</sub>/De-300, (<b>b</b>) C/Co<sub>3</sub>O<sub>4</sub>/De-450, (<b>c</b>) C/Co<sub>3</sub>O<sub>4</sub>/De-600. (<b>d</b>) The simulated RCS curves of the PEC and C/Co<sub>3</sub>O<sub>4</sub>/De at a scattering angle of 0–180°. (<b>e</b>) The RCS reduction values (the RCS values of PEC minus that of the samples) for all the samples.</p>
Full article ">Figure 9
<p>The synthesis process of C/Co<sub>3</sub>O<sub>4</sub>/De.</p>
Full article ">
15 pages, 3299 KiB  
Article
Study of Properties of Water-Dispersion Paint and Varnish Compositions with the Content of Modified Mineral Filler
by Ruslan E. Nurlybayev, Erzhan I. Kuldeyev, Zaure N. Altayeva, Zhanar O. Zhumadilova, Axaya S. Yestemessova and Yelzhan S. Orynbekov
Coatings 2024, 14(9), 1154; https://doi.org/10.3390/coatings14091154 - 8 Sep 2024
Viewed by 527
Abstract
This article presents the results of research work devoted to improving the characteristics of paint and varnish coatings based on aqueous dispersions of polyacrylates; it is proposed to modify them by introducing mineral raw materials as fillers and hydrated lime, with subsequent processing [...] Read more.
This article presents the results of research work devoted to improving the characteristics of paint and varnish coatings based on aqueous dispersions of polyacrylates; it is proposed to modify them by introducing mineral raw materials as fillers and hydrated lime, with subsequent processing in a vortex layer apparatus. The introduction of activated diatomite does not cause the deterioration of covering power, adhesion or an increase in the porosity of the paint material. The modification of coatings contributes to an increase in their operational properties, which can be associated with a reduction in the free volume in the composite and the formation of polymer boundary layers with modified physical and chemical properties. The aim of this study is to obtain a water-dispersion paint and varnish composition containing modified diatomite on a polyacrylate basis and, subsequently, study its main physical and mechanical parameters. The work has been carried out by the following method: determination of porosity, adhesion, elasticity and covering power of the control composition; determination of porosity, adhesion, elasticity and covering power of the obtained composites using modified filler; investigation of the influence of radiation on the infrared spectrum of the paint coating surface using a FLIRB620 thermal imager. As a result of this research work, it was noticed that the modification of water dispersions with silica-activated diatomite helps to eliminate the main disadvantages of materials and coatings based on acrylate binders—low water resistance and low physical and mechanical characteristics. The introduction of modified diatomite into water-emulsion paint on an acrylate base does not lead to the deterioration of the main performance characteristics of paint coatings—porosity, adhesion, elasticity and covering. Full article
Show Figures

Figure 1

Figure 1
<p>X-ray phase analysis of diatomite raw materials with low iron content (low-iron variety).</p>
Full article ">Figure 2
<p>Granulometric composition of diatomite of Zhalpak deposit.</p>
Full article ">Figure 3
<p>Microphotographs of natural diatomite powders from the Zhalpak deposit magnified to (<b>a</b>) 3000×; (<b>b</b>) 6000×; (<b>c</b>) 12,000× multiples.</p>
Full article ">Figure 4
<p>Temperature distribution over the surface of a container painted with a water-dispersion paint and varnish composition without the addition of modified diatomite.</p>
Full article ">Figure 5
<p>Temperature distribution over the surface of a container painted with a water-dispersion paint and varnish composition with the addition of modified diatomite (20 parts by weight·h).</p>
Full article ">Figure 6
<p>Temperature distribution over the surface of a container painted with a water-dispersion paint and varnish composition with the addition of modified diatomite (10 parts by weight·h).</p>
Full article ">Figure 7
<p>Temperature distribution over the surface of a container painted with a water-dispersion paint and varnish composition with the addition of modified diatomite + lime (40 parts by weight·h).</p>
Full article ">Figure 8
<p>Temperature distribution over the surface of a container painted with a water-dispersion paint and varnish composition with the addition of modified diatomite (13 parts by weight·h).</p>
Full article ">
109 pages, 1729 KiB  
Review
The Use of Natural Minerals as Reinforcements in Mineral-Reinforced Polymers: A Review of Current Developments and Prospects
by Anna Fajdek-Bieda and Agnieszka Wróblewska
Polymers 2024, 16(17), 2505; https://doi.org/10.3390/polym16172505 - 3 Sep 2024
Viewed by 752
Abstract
Natural minerals play a key role in the burgeoning field of mineral-reinforced polymers, providing an important element in strengthening and toughening the properties of composite materials. This article presents a comprehensive overview of the use of minerals in mineral-reinforced polymers, covering various aspects [...] Read more.
Natural minerals play a key role in the burgeoning field of mineral-reinforced polymers, providing an important element in strengthening and toughening the properties of composite materials. This article presents a comprehensive overview of the use of minerals in mineral-reinforced polymers, covering various aspects of their applications and impact on the final properties of these materials. The potential of various types of natural minerals (for example talc, montmorillonite, halloysite, diatomite) as reinforcements in mineral-reinforced polymers is discussed. Techniques for producing mineral-reinforced polymers using minerals, including the mixing method, impregnation, and coating application, are presented in detail. In addition, the effects of process parameters and component ratios on the final properties of mineral-reinforced polymers are discussed. The latest research on the use of minerals in mineral-reinforced polymers is also presented, including their effects on the strength, stiffness, resistance to environmental conditions, and biodegradation of the materials. Finally, the development prospects and potential applications of mineral-reinforced polymers with minerals in various industrial sectors, including packaging, automotive, construction, and medicine, are discussed. Full article
(This article belongs to the Special Issue Biopolymers and Bio-Based Polymer Composites)
Show Figures

Figure 1

Figure 1
<p>Groups of polymers modified with natural minerals (own elaboration).</p>
Full article ">Figure 2
<p>Examples of some natural plastic fillers (own study).</p>
Full article ">Figure 3
<p>Hydrated halloysite structure (<b>A</b>) and dehydrated halloysite structure (<b>B</b>).</p>
Full article ">
20 pages, 5431 KiB  
Article
Catalytic Ozonation of Sulfachloropyridazine Sodium by Diatomite-Modified Fe2O3: Mechanism and Pathway
by Yang Yu, Lingling Wang, Zhandong Wu, Xuguo Liu, Zhen Liu, Lijian Zhang and Lixin Li
Catalysts 2024, 14(8), 540; https://doi.org/10.3390/catal14080540 - 19 Aug 2024
Viewed by 462
Abstract
A diatomite-modified Fe2O3 (Fe2O3/Dia) catalyst was prepared to catalyze the ozonation degradation of sulfachloropyridazine sodium (SPDZ). The chemical oxygen demand (COD) was used as the index of pollutant degradation. The catalytic ozonation experiment showed that the [...] Read more.
A diatomite-modified Fe2O3 (Fe2O3/Dia) catalyst was prepared to catalyze the ozonation degradation of sulfachloropyridazine sodium (SPDZ). The chemical oxygen demand (COD) was used as the index of pollutant degradation. The catalytic ozonation experiment showed that the COD removal rate of SPDZ was 87% under Fe2O3/Dia catalysis, which was much higher than that obtained when using Fe2O3 as the catalyst. The characteristics of the Fe2O3/Dia catalyst were investigated, and the successful synthesis of the Fe2O3/Dia composite catalyst was proved by XRD, XPS, SEM, FTIR, BET and other characterization methods. The catalytic mechanism of degradation by ozone with Fe2O3/Dia was analyzed. According to free-radical trapping experiments and an in situ electron paramagnetic spectrometer characterization analysis, the main oxidizing species in the catalytic Fe2O3/Dia ozone system is ·OH. The intermediates in the degradation process of SPDZ were detected and analyzed in detail by liquid chromatography-coupled mass spectrometry. The degradation mechanism and three degradation paths of SPDZ were proposed. Full article
(This article belongs to the Section Environmental Catalysis)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Effect of (<b>a</b>) catalyst dosage, (<b>b</b>) ozone dosages, (<b>c</b>) pH and (<b>d</b>) temperature on COD degradation of sulfonamide chlordazine sodium catalyzed by Fe<sub>2</sub>O<sub>3</sub>/Dia.</p>
Full article ">Figure 2
<p>COD degradation curve for various systems. Reaction conditions: [SPDZ]<sub>0</sub> = 2 g·L<sup>−1</sup>, catalyst dosage = 2 g·L<sup>−1</sup>.</p>
Full article ">Figure 3
<p>Effect of (<b>a</b>) TBA, (<b>b</b>) HCO<sub>3</sub><sup>−</sup>, and (<b>c</b>) PBQ on the catalytic ozonation of SPDZ. Reaction conditions: [SPDZ]<sub>0</sub> = 2 g·L<sup>−1</sup>, catalyst dosage = 2 g·L<sup>−1</sup>.</p>
Full article ">Figure 4
<p>EPR signal of reactive oxygen species. (<b>a</b>) DMPO-·OH, (<b>b</b>) DMPO- O<sub>2</sub>·<sup>−</sup>.</p>
Full article ">Figure 4 Cont.
<p>EPR signal of reactive oxygen species. (<b>a</b>) DMPO-·OH, (<b>b</b>) DMPO- O<sub>2</sub>·<sup>−</sup>.</p>
Full article ">Figure 5
<p>(<b>a</b>) Effect of PO<sub>4</sub><sup>3−</sup> on the catalytic ozonation of SPDZ with Fe<sub>2</sub>O<sub>3</sub>/Dia. (<b>b</b>) Effect of various PO<sub>4</sub><sup>3−</sup> concentrations on the catalytic ozonation of SPDZ with Fe<sub>2</sub>O<sub>3</sub>/Dia. Reaction conditions: [SPDZ]<sub>0</sub> = 2 g·L<sup>−1</sup>, catalyst dosage = 2 g·L<sup>−1</sup>.</p>
Full article ">Figure 6
<p>(<b>a</b>,<b>b</b>) SEM of diatomite before modification. (<b>c</b>,<b>d</b>) SEM of diatomite after modification. (<b>e</b>,<b>f</b>) SEM of diatomite-modified Fe<sub>2</sub>O<sub>3</sub>.</p>
Full article ">Figure 7
<p>XRD spectra of (<b>a</b>) diatomaceous earth, (<b>b</b>) Fe<sub>2</sub>O<sub>3</sub>, and (<b>c</b>) Fe<sub>2</sub>O<sub>3</sub>/Dia.</p>
Full article ">Figure 8
<p>XPS spectra of Fe<sub>2</sub>O<sub>3</sub>/Dia: (<b>a</b>) survey spectrum, (<b>b</b>) Fe 2p spectrum, (<b>c</b>) Si 2p spectrum.</p>
Full article ">Figure 9
<p>Mechanism diagram of ROS formation from ozone catalyzed by the Fe<sub>2</sub>O<sub>3</sub>/Dia composite catalyst.</p>
Full article ">Figure 10
<p>FTIR spectra of Fe<sub>2</sub>O<sub>3</sub>/Dia: (<b>a</b>) full spectrum, (<b>b</b>) selected range.</p>
Full article ">Figure 11
<p>The catalytic ozonation pathway of SPDZ was proposed.</p>
Full article ">Figure 12
<p>Recycling tests of SPDZ degradation by Fe<sub>2</sub>O<sub>3</sub>/Dia-catalyzed ozonation.</p>
Full article ">
12 pages, 15092 KiB  
Article
Utilisation of Biosilica as Active Silica Source for Metakaolin-Based Geopolymers
by Haozhe Guo, Zhihao Huang, Thammaros Pantongsuk, Ting Yu, Baifa Zhang, Jinghan Luo and Peng Yuan
Minerals 2024, 14(8), 816; https://doi.org/10.3390/min14080816 - 12 Aug 2024
Viewed by 539
Abstract
This study explores the potential of biosilica including diatom and diatomaceous earth as alternative silica sources for metakaolin-based geopolymers. Diatomaceous earth, composed of fossilised diatom frustules rich in amorphous silica, and diatoms, a sustainable source of renewable biosilica, are investigated for their effectiveness [...] Read more.
This study explores the potential of biosilica including diatom and diatomaceous earth as alternative silica sources for metakaolin-based geopolymers. Diatomaceous earth, composed of fossilised diatom frustules rich in amorphous silica, and diatoms, a sustainable source of renewable biosilica, are investigated for their effectiveness in enhancing geopolymer properties. Through detailed analyses including FTIR, XRD, and SEM, the study evaluates the impact of these biosilica sources on geopolymer compressive strength and microstructure, comparing them with conventional sodium silicate. Results show that diatoms exhibit significant promise, achieving 28-day strength up to 17.9 MPa at a 30% mass fraction, while diatomaceous earth reaches 26.2 MPa at a 50% addition rate, demonstrating their potential as active silica sources. Furthermore, the study elucidates the role of organic matter in biosilica on geopolymerisation, highlighting its influence on active silica release and the strength performance of products. This study proposes a novel pathway to enhance the sustainability of geopolymers through the utilisation of biosilica from diatoms, contributing to advancements in eco-efficient construction materials. Full article
(This article belongs to the Section Clays and Engineered Mineral Materials)
Show Figures

Figure 1

Figure 1
<p>(<b>a</b>) The compressive strength of geopolymers at 7 and 28 days with the error bar representing the upper and lower 95% confidence interval; (<b>b</b>) The growth rate of compressive strengths between 7 to 28 days.</p>
Full article ">Figure 2
<p>(<b>a</b>) XRD patterns of DB, CDB, G<sub>B30</sub>, and G<sub>CB30</sub>; (<b>b</b>) XRD patterns of DE, CDE, G<sub>E50</sub>, and G<sub>CE50</sub>. The XRD patterns of all the geopolymers were obtained at 28 days. (A: albite; C: chlorite; M: muscovite; P: paragonite; Q: quartz).</p>
Full article ">Figure 3
<p>(<b>a</b>) FTIR spectra of DB, CDB, G<sub>B30</sub>, and G<sub>CB30</sub>; (<b>b</b>) FTIR spectra of DE, CDE, G<sub>E50</sub>, and G<sub>CE50</sub>. The FTIR spectra of all the geopolymers were obtained at 28 days.</p>
Full article ">Figure 4
<p>SEM images of (<b>a</b>) DB, (<b>b</b>) G<sub>B30</sub>, (<b>c</b>) CDB, (<b>d</b>) G<sub>CB30</sub>, (<b>e</b>) DE, (<b>f</b>) G<sub>E50</sub>, (<b>g</b>) DE, and (<b>h</b>) G<sub>CB50</sub>. The SEM images of the geopolymers and the corresponding EDS analysis results, listed below, were measured at 28 d.</p>
Full article ">
19 pages, 12499 KiB  
Article
Trace Elements Anomalous Concentrations in Building Materials—The Impact of Secondary Mineralisation Processes
by Agnieszka Pękala, Piotr Koszelnik, Michał Musiał and Tomasz Galek
Materials 2024, 17(16), 3909; https://doi.org/10.3390/ma17163909 - 7 Aug 2024
Viewed by 595
Abstract
The Pb, Cr, Cd, Ni, Zn, Cu, Co, As, Sr, Ba, and Zr content has been determined in the tested rock raw materials. The concentration of cadmium (Cd) was found to be elevated in all types of rock materials and was found on [...] Read more.
The Pb, Cr, Cd, Ni, Zn, Cu, Co, As, Sr, Ba, and Zr content has been determined in the tested rock raw materials. The concentration of cadmium (Cd) was found to be elevated in all types of rock materials and was found on average to be: 1.39 mg/kg in limestones, 0.86 mg/kg—sandstones, 0.44 mg/kg—diatomites, 0.55 mg/kg—opoka rocks, 0.89 mg/kg—marls, 0.21 mg/kg—gaizes 0.42 mg/kg—kaolin clays, and 2.13 mg/kg—decalcified opoka rocks. Higher concentrations of arsenic (As) have also been recorded in sandstones and diatomites, as well as lead (Pb) in limestones and sandstones. The results obtained indicate that the anomalous level of elements is of natural origin and the results of identified secondary mineralisation processes that have affected the tested materials. Pyritization and sulfatization processes have been detected. Mineralogical research has shown that these processes can be associated with the activity of biochemical processes caused by the decomposition of the soft tissues of animal organisms and the organic substances of plant origin that fill the stylolites. It has been shown that the content of strontium (Sr) increases in geologically older Jurassic formations compared to younger Cretaceous formations, which can be used in the monitoring of building materials. Full article
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Area of research carried out. Bełchatów lignite deposit (<b>A</b>) cross section through the Bełchatów lignite deposit [<a href="#B21-materials-17-03909" class="html-bibr">21</a>]; (<b>B</b>) location of the study area depicted in the colour composition of a Sentinel satellite image.</p>
Full article ">Figure 2
<p>Limestone microsections. Iron sulphides filling of oncoids (<b>a</b>) stylolite seams (<b>b</b>), (blue arrows).</p>
Full article ">Figure 3
<p>Lead (Pb) content in rock raw materials.</p>
Full article ">Figure 4
<p>Concentration of trace elements in clays.</p>
Full article ">Figure 5
<p>Cadmium (Cd) content in the rock raw materials studied.</p>
Full article ">Figure 6
<p>Arsenic (As) content in the rock raw materials studied.</p>
Full article ">Figure 7
<p>Concentration of trace elements in sandstones.</p>
Full article ">Figure 8
<p>Zirconium (Zr) content in the rock raw materials studied.</p>
Full article ">Figure 9
<p>Celestine crystal isolated from a crack in the outcrop. SEM/EDS research.</p>
Full article ">Figure 10
<p>Spectrum of celestine from limestone. EDS/BSE research.</p>
Full article ">Figure 11
<p>Iron sulphides filling the voids (<b>a</b>) stylolite seams (<b>b</b>) (markings: yellow arrows). Polarising microscope, 2P. (explanations: P-polariser).</p>
Full article ">Figure 12
<p>Organogenic limestone. Iron sulphides selectively fill organic remains. (<b>a</b>,<b>b</b>) carbonate sparite replaced by iron sulphides in ooids; (<b>c</b>,<b>d</b>) pyrite fills intracellular spaces in carbonate-type bioclasts. (<b>e</b>,<b>f</b>) selective replacement of carbonates with pyrite in bioclasts. Image of the polarising microscope 1P, 2P (explanations: P-polariser).</p>
Full article ">Figure 13
<p>Average strontium content (Sr) in rock raw materials.</p>
Full article ">Figure 14
<p>Distribution of strontium (Sr) in opoka rocks.</p>
Full article ">Figure 15
<p>Distribution of strontium (Sr) in limestones.</p>
Full article ">Figure 16
<p>Examples of Sr distribution profiles in the tested rock raw materials.</p>
Full article ">
18 pages, 10167 KiB  
Article
Preparation of Fe-Modified Diatomite-Based Ceramsite for Efficient Phosphate Adsorption: Utilizing Diatomite’s Distinctive Porous Structure and Surface Silanol Groups
by Zhichao Chen, Yulin Min, Xin Zhao, Penghui Shi and Hongxiu Lu
Water 2024, 16(16), 2218; https://doi.org/10.3390/w16162218 - 6 Aug 2024
Viewed by 875
Abstract
Ceramsites are extensively employed as substrates for adsorbents in studies focused on phosphorus adsorption, leaving ceramsites crafted from diatomite less explored. Diatomite-based ceramsite, with its distinct porous architecture and surface silanol functionalities, is adept at supporting a variety of metal oxides, presenting a [...] Read more.
Ceramsites are extensively employed as substrates for adsorbents in studies focused on phosphorus adsorption, leaving ceramsites crafted from diatomite less explored. Diatomite-based ceramsite, with its distinct porous architecture and surface silanol functionalities, is adept at supporting a variety of metal oxides, presenting a distinct advantage over other ceramsite variants. In light of this, the present study embarked on producing diatomite-based ceramsite using diatomite as the foundational material, subsequently enhancing it through the incorporation of Fe, thus yielding an Fe-modified diatomite-based ceramsite. Through adsorption testing, the modified ceramsite demonstrated a significantly improved adsorption capacity of 4.06 mg P/g, marking a substantial enhancement from the initial capacity of 0.9 mg P/g. The process of phosphorus adsorption exhibited a strong alignment with the Langmuir isotherm model and the pseudo-second-order kinetic model. In-depth analyses employing XRD, FTIR, zeta potential, and XPS techniques have revealed that the principal mechanisms driving the adsorption process are centered on interactions involving electrostatic forces, the formation of chemical precipitates, and the exchange of ligands. This investigation not only opens new avenues for the application of diatomite-based ceramsite but also lays down a theoretical foundation for its modification, thereby enriching the spectrum of its utility. Full article
(This article belongs to the Section Wastewater Treatment and Reuse)
Show Figures

Figure 1

Figure 1
<p>Effect of activated carbon content (<b>a</b>) and sintering temperature (<b>c</b>) on the apparent porosity and bulk density of DC.the effect of activated carbon content (<b>b</b>) and sintering temperature (<b>d</b>) on the water absorption and compressive strength of DC. Effect of activated carbon and sintering temperature on the performance of ceramsite.</p>
Full article ">Figure 2
<p>(<b>a</b>) XRD patterns of DC at different sintering temperatures. (<b>b</b>–<b>e</b>) Pore structures of DC sintered at various temperatures. (<b>f</b>) Magnified view of the local surface structure of DC. The influence of varying sintering temperatures on the crystalline structure and pore characteristics of DC.</p>
Full article ">Figure 3
<p>The SEM images of diatomite (<b>a</b>), DC (<b>b</b>), and Fe-DC (<b>c</b>). (<b>d</b>) Time-dependent adsorption curves for adsorbents modified at varying ratios. Nitrogen adsorption–desorption curves (<b>e</b>) alongside the BJH analysis of pore size distribution for Fe-DC (<b>f</b>).</p>
Full article ">Figure 4
<p>Kinetic curves of phosphorus adsorption by Fe-DC (<span class="html-italic">C</span><sub>0</sub> = 100 mg/L, pH = 7.00, <span class="html-italic">T</span> = 298 K, m = 2 g, <span class="html-italic">V</span> = 100 mL); (<b>a</b>) pseudo-first-order kinetic models, (<b>b</b>) pseudo-second-order kinetic models, (<b>c</b>) Elovich kinetic models, (<b>d</b>) Richie kinetic models, (<b>e</b>) intraparticle diffusion models, (<b>f</b>) Bangham kinetic models.</p>
Full article ">Figure 5
<p>Variation in adsorption capacity with different phosphorus concentrations and over time. (<b>a</b>) Adsorption isotherm models on Fe-DC (<span class="html-italic">C</span><sub>0</sub> = 100 mg/L, pH = 7.00, <span class="html-italic">T</span> = 298 K, m = 2 g, <span class="html-italic">V</span> = 100 mL), (<b>b</b>) Langmuir model, (<b>c</b>) Freundlich model, (<b>d</b>) Sips model.</p>
Full article ">Figure 6
<p>The effect of temperature on P adsorption by Fe-DC at various concentrations (<b>a</b>) and linear curves of ln<span class="html-italic">K<sub>C</sub></span> vs. 1/<span class="html-italic">T</span> for the adsorption process (<b>b</b>).</p>
Full article ">Figure 7
<p>XRD patterns (<b>a</b>) and FTIR spectra (<b>b</b>) of Fe-DC before and after P adsorption.</p>
Full article ">Figure 8
<p>The XPS spectra of Fe-DC before and after phosphate adsorption. (<b>a</b>) Full spectra. High-resolution XPS spectrum of P 2p (<b>b</b>), Fe 2p (<b>c</b>), and O 1s (<b>d</b>).</p>
Full article ">Figure 9
<p>(<b>a</b>) The effect of pH alterations in the solution on the adsorption of P by Fe-DC (<span class="html-italic">C</span><sub>0</sub> = 100 mg/L, <span class="html-italic">T</span> = 298 K, m = 2 g, <span class="html-italic">V</span> = 100 mL). (<b>b</b>) Changes in the distribution of phosphorus morphology and the zeta potential of Fe-DC across varying pH levels.</p>
Full article ">Figure 10
<p>Mechanisms of phosphate adsorption onto Fe-enhanced diatomite-based ceramsite.</p>
Full article ">
16 pages, 2964 KiB  
Article
Towards Safe Diatomite Sludge Management: Lead Immobilisation via Geopolymerisation
by Haozhe Guo, Zhihao Huang, Baifa Zhang, Ting Yu, Thammaros Pantongsuk and Peng Yuan
Minerals 2024, 14(8), 763; https://doi.org/10.3390/min14080763 - 27 Jul 2024
Viewed by 674
Abstract
Diatomite, a natural adsorbent rich in active silica, serves as a valuable precursor for geopolymer synthesis. The safe disposal of diatomite as a failed lead (Pb(II)) adsorbent is critical to prevent secondary contamination. This study investigated the immobilisation efficiency of geopolymerisation for Pb(II)-rich [...] Read more.
Diatomite, a natural adsorbent rich in active silica, serves as a valuable precursor for geopolymer synthesis. The safe disposal of diatomite as a failed lead (Pb(II)) adsorbent is critical to prevent secondary contamination. This study investigated the immobilisation efficiency of geopolymerisation for Pb(II)-rich diatomite sludge. Low-grade diatomite with high ignition loss was utilised in the synthesis of alkali-activated geopolymers. It was demonstrated that the geopolymers achieved a compressive strength of 28.3 MPa with a 50% replacement rate of metakaolin by diatomite sludge, which was not a compromise in strength compared to that of the geopolymer with no Pb(II) (26.2 MPa). The leaching behaviour of Pb(II) was evaluated using water and acetic acid, yielding concentrations below 3 mg/L and immobilisation efficiencies of 95% in both scenarios. Analytical techniques including Fourier transform infrared spectroscopy (FTIR), X-ray diffraction (XRD), and scanning electron microscopy (SEM) elucidated the mineral composition and chemical environment of the geopolymers. These analyses revealed that Pb(II) migrated from diatomite pores, potentially forming soluble hydroxides under sufficient hydroxide, which then participated in condensation with silicon and aluminium monomers, effectively immobilising Pb(II) within amorphous aluminosilicate gels. Furthermore, the formation of the amorphous gels within diatomite pores hindered Pb(II) leaching, encapsulating Pb(II) effectively. This study presents a novel approach to immobilising heavy metals within building materials, enhancing mineral resource utilisation efficiency while addressing environmental contamination concerns. Full article
Show Figures

Figure 1

Figure 1
<p>(<b>a</b>) XRD patterns of Dt and MK, (<b>b</b>) SEM image of Dt, and (<b>c</b>) SEM image of MK.</p>
Full article ">Figure 2
<p>The compressive strength of Dt-based geopolymers at 7 d and 28 d with the error bar representing the upper and lower 95% confidence interval.</p>
Full article ">Figure 3
<p>XRD patterns of GDt<sub>50</sub> and Pb-GDt<sub>50</sub> at 28 d.</p>
Full article ">Figure 4
<p>FTIR spectra of MK, Dt, GDt<sub>50</sub>, and Pb-GDt<sub>50</sub> at 28 d.</p>
Full article ">Figure 5
<p>SEM images and EDS analysis results (indicated by the position of the circle) of (<b>a</b>) GDt<sub>50</sub> and (<b>b</b>) Pb-GDt<sub>50</sub> at 28 d. The Si/Al and Na/Al ratios were calculated based on the EDS results from at least 10 points per sample.</p>
Full article ">
20 pages, 12562 KiB  
Article
The Diatomite Grinding Technology Concept for the Protection of Diatomite Shells and the Control of Product Grading
by Agata Stempkowska, Tomasz Gawenda and Krzysztof Smoroń
Materials 2024, 17(15), 3662; https://doi.org/10.3390/ma17153662 - 24 Jul 2024
Viewed by 480
Abstract
Diatomite deposits in Poland are located in the Podkarpackie Voivodeship, and the only active deposit is in Jawornik Ruski. Therefore, it is a unique material. Improved rock processing methods are constantly in demand. In the research presented here, we have used research methods [...] Read more.
Diatomite deposits in Poland are located in the Podkarpackie Voivodeship, and the only active deposit is in Jawornik Ruski. Therefore, it is a unique material. Improved rock processing methods are constantly in demand. In the research presented here, we have used research methods such as X-ray diffraction (XRD), scanning electron microscope (SEM), particle shape analysis, and appropriate sets of crushing machines. Diatomite comminution tests were carried out on test stands in different crushers (jaw crusher, hammer crusher, high-pressure roller press, ball mill) using different elementary crushing force actions: crushing, abrasion, and impact, occurring separately or in combination. The machines were tested with selected variable parameters to obtain products with a wide range of grain sizes ranging from 0 to 10 mm. The ball mill (yield 87%, system C3) and the hammer crusher with HPGR (high-pressure grinding roller) (yield 79%, system D2 + D3) have the greatest impact on diatom shell release and accumulation in the finest 0–5 μm and 5–10 μm fractions. For commercial purposes, it is important to obtain very fine fractions while keeping the shells undisturbed. Full article
Show Figures

Figure 1

Figure 1
<p>Location of diatomite deposits and an example image of the rock.</p>
Full article ">Figure 2
<p>Diatomite feed delivered for testing and grain composition curve of diatomite feed.</p>
Full article ">Figure 3
<p>SEM images with diatoms of different types: (<b>a</b>) cylindrical, (<b>b</b>) disc shaped, (<b>c</b>) preserved both parts of the shell, and (<b>d</b>) filled with silica.</p>
Full article ">Figure 4
<p>Silica recrystallized by geological processes from practically no preserved diatom shells.</p>
Full article ">Figure 5
<p>Conglomerate of diatom shells larger than 45 µm.</p>
Full article ">Figure 6
<p>Analysis of a microarea diatom composed of silica (spot 1) and visible elongated gypsum crystals (spot 2).</p>
Full article ">Figure 7
<p>Gypsum brush form, feed sample.</p>
Full article ">Figure 8
<p>Other mineral forms present in diatomite, most likely chlorite.</p>
Full article ">Figure 9
<p>Iron-rich spherical forms identified as pyrite.</p>
Full article ">Figure 10
<p>Silica flowstone form (opal).</p>
Full article ">Figure 11
<p>Presence of organic carbon.</p>
Full article ">Figure 12
<p>Crushing and screening machines: jaw crusher (<b>a</b>), hammer crusher (<b>b</b>), high-pressure grinding rolls (<b>c</b>), ball mill (<b>d</b>), vibrating screen (<b>e</b>), and shaker with analytical sieves (<b>f</b>).</p>
Full article ">Figure 13
<p>Diagrams of technological systems.</p>
Full article ">Figure 13 Cont.
<p>Diagrams of technological systems.</p>
Full article ">Figure 14
<p>Visible sharp-edged silica and crushed diatom shells.</p>
Full article ">Figure 15
<p>Visible incomplete crushing after pressure pressing—visible microcracks on silica crystal (<b>left</b>) and diatom shell (<b>right</b>).</p>
Full article ">Figure 16
<p>Quantitative analysis of diatom shells in relevant grain classes after different grinding processes.</p>
Full article ">Figure 17
<p>Schematic design of a technological system for grinding and classification with drying of diatomite with a capacity of up to 20 Mg/h.</p>
Full article ">
18 pages, 2255 KiB  
Article
Anti-Inflammatory, Antidiabetic, and Antioxidant Properties of Extracts Prepared from Pinot Noir Grape Marc, Free and Incorporated in Porous Silica-Based Supports
by Mihaela Deaconu, Anil Abduraman, Ana-Maria Brezoiu, Nada K. Sedky, Simona Ioniță, Cristian Matei, Laila Ziko and Daniela Berger
Molecules 2024, 29(13), 3122; https://doi.org/10.3390/molecules29133122 - 30 Jun 2024
Viewed by 882
Abstract
This study presents properties of hydroethanolic extracts prepared from Pinot Noir (PN) grape pomace through conventional, ultrasound-assisted or solvothermal extraction. The components of the extracts were identified by HPLC. The total content of polyphenols, flavonoids, anthocyanins, and condensed tannins, as well as antioxidant [...] Read more.
This study presents properties of hydroethanolic extracts prepared from Pinot Noir (PN) grape pomace through conventional, ultrasound-assisted or solvothermal extraction. The components of the extracts were identified by HPLC. The total content of polyphenols, flavonoids, anthocyanins, and condensed tannins, as well as antioxidant activity and α-glucosidase inhibitory activity of extracts were evaluated using UV-vis spectroscopy. All extracts were rich in phenolic compounds, proving a good radical scavenging activity. The extract obtained by conventional extraction at 80 °C showed the best α-glucosidase inhibitory activity close to that of (-)-epigallocatechin gallate. To improve the chemical stability of polyphenols, the chosen extract was incorporated in porous silica-based supports: amine functionalized silica (MCM-NH2), fucoidan-coated amine functionalized silica (MCM-NH2-Fuc), MCM-41, and diatomite. The PN extract exhibited moderate activity against Gram-positive S. aureus (MIC = 156.25 μg/mL) better than against Gram-negative E. coli (MIC = 312.5 μg/mL). The biocompatibility of PN extract, free and incorporated in MCM-NH2 and MCM-NH2-Fuc, was assessed on RAW 264.7 mouse macrophage cells, and the samples showcased a good cytocompatibility at 10 µg/mL concentration. At this concentration, PN and PN@MCM-NH2-Fuc reduced the inflammation by inhibiting NO production. The anti-inflammatory potential against COX and LOX enzymes of selected samples was evaluated and compared with that of Indomethacin and Zileuton, respectively. The best anti-inflammatory activity was observed when PN extract was loaded on MCM-NH2-Fuc support. Full article
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Spectrometric determinations for the prepared extracts: TP as gallic acid equivalents, GAE (<b>A</b>); TF as quercetin equivalents, QE (<b>B</b>); TAC as cyanidin-glucoside equivalents, CGE (<b>C</b>); RSA as Trolox equivalents, TE (<b>D</b>).</p>
Full article ">Figure 2
<p>Small-angle X-ray diffraction patterns of MCM-41-type support (<b>A</b>); FTIR spectra of diatomite, MCM-NH<sub>2</sub>, MCM-NH<sub>2</sub>-Fuc, and fucoidan denoted Fuc (<b>B</b>); Wide-angle XRD analysis of diatomite (<b>C</b>); SEM micrographs of MCM-NH<sub>2</sub> sample (<b>D</b>), MCM-NH<sub>2</sub>-Fuc support (<b>E</b>), sulfur (red) mapping of MCM-NH<sub>2</sub>-Fuc surface (<b>F</b>), and diatomite (<b>G</b>).</p>
Full article ">Figure 3
<p>TGA-DTA curves for MCM-NH<sub>2</sub> and MCM-NH<sub>2</sub>-Fuc supports.</p>
Full article ">Figure 4
<p>TGA-DTG curves of PN (<b>A</b>), PN@MCM-NH<sub>2</sub> and PN@MCM-NH<sub>2</sub>-Fuc (<b>B</b>); as well as for PN@MCM-41 and PN@Diatomite (<b>C</b>).</p>
Full article ">Figure 5
<p>XRD patterns of PN, PN(C), PN@diatomite, and PN@MCM-41 (<b>A</b>); FTIR spectra of PN@diatomite in comparison with that for PN extract (<b>B</b>); radical scavenging activity of PN@MCM-41 and PN@Diatomite in comparison with that of PN free extract and corresponding supports using DPPH solution as control after 12 months of storage at 4 °C (<b>C</b>).</p>
Full article ">Figure 6
<p>Cell viability and NO production inhibitory effects in RAW 264.7 cells. (<b>A</b>) Cellular viability after 72 h of exposure to the test samples compared to the Control group (Untreated cells). (<b>B</b>) NO generation in cells treated with the different test samples for 1 h before the addition of LPS and induction of inflammation as compared to the Control (cells that received LPS only). The symbol (*) indicates significant difference from the control, while the symbol (♦) refers to significant difference from 10 µg/mL concentration of the test sample. The use of each symbol for once, twice, and thrice indicate <span class="html-italic">p</span>-values &lt; 0.05, &lt;0.01, and &lt;0.001, respectively. (<b>C</b>) Anti-inflammatory potential against COX-1 and COX-2 in comparison with Indomethacin, and LOX compared to Zileuton. Data displayed as the average of triplicates ± standard deviation (SD).</p>
Full article ">
28 pages, 11580 KiB  
Article
Durable and High-Temperature-Resistant Superhydrophobic Diatomite Coatings for Cooling Applications
by José Pereira, Reinaldo Souza, António Moreira and Ana Moita
Coatings 2024, 14(7), 805; https://doi.org/10.3390/coatings14070805 - 28 Jun 2024
Viewed by 760
Abstract
The present work is aimed at the development of superhydrophobic coatings and surfaces with enhanced robustness and boiling temperature resistance. We will address the synthesis method of the coatings, which was based on the preparation of a composite of silanized diatomite particles embedded [...] Read more.
The present work is aimed at the development of superhydrophobic coatings and surfaces with enhanced robustness and boiling temperature resistance. We will address the synthesis method of the coatings, which was based on the preparation of a composite of silanized diatomite particles embedded in epoxy resin. After the synthesis of the composite solution, it was applied by dip-coating in stainless steel substrates and submitted to a post-treatment cure in an oven. The method proved to be a comparatively fast and simple one. Then, the substrate/coating sets were characterized using different techniques, including Fourier transform infrared spectroscopy and scanning electron microscopy, and their water contact angle and roughness were measured. Apart from this, the physical and chemical robustness of the sets was also tested using diverse resistance tests like adhesion strength, abrasion resistance, resistance to strong acids and bases, and resistance to boiling water. The main results are that we obtained robust coatings, with wettability defined by water contact angles above 150°. Also, the synthesized coatings revealed good resistance to boiling water, as their properties were almost unchanged after the completion of a long period of tests. The characterization of the produced coatings suggested their propensity to be explored for use in water boiling surfaces and interfaces for cooling purposes in boiling heat transfer systems. Full article
Show Figures

Figure 1

Figure 1
<p>Schematic diagram of the coating synthesis procedure.</p>
Full article ">Figure 2
<p>Used substrate and obtained coatings: (<b>a</b>) stainless steel substrate, (<b>b</b>) etched stainless steel substrate, (<b>c</b>) untreated diatomite coating, (<b>d</b>) 25% particle loading coating, (<b>e</b>) 35% particle loading coating, and (<b>f</b>) 45% particle loading coating.</p>
Full article ">Figure 3
<p>Fourier transform infrared spectroscopy spectra of the coating constitutive nanopowders: diatomite in its as-received state (blue line), diatomite with the addition of APTES followed by the addition of PFOTS (orange line), and diatomite with the initial addition of PFOTS followed by the addition of APTES (gray line).</p>
Full article ">Figure 4
<p>Diatomite–PFOTS–APTES–EPOXY coating after immersion for 48 h in rhodamine B.</p>
Full article ">Figure 5
<p>Three-dimensional scanning of the coating at 20× magnification.</p>
Full article ">Figure 6
<p>Three-dimensional scanning of the coating at 20× magnification.</p>
Full article ">Figure 7
<p>Samples for SEM analysis: (<b>a</b>) untreated diatomite powder, (<b>b</b>) treated diatomite powder, (<b>c</b>) untreated diatomite coating, (<b>d</b>) 25% particle loading coating, (<b>e</b>) 35% particle loading coating, and (<b>f</b>) 45% particle loading coating.</p>
Full article ">Figure 8
<p>SEM micrographs of the untreated diatomite powder: (<b>a</b>) General view of the microstructure, (<b>b</b>) Detail of a diatomite disk.</p>
Full article ">Figure 9
<p>SEM micrographs of the treated diatomite powder: (<b>a</b>) General view of the microstructure, (<b>b</b>) Detail of a diatomite disk.</p>
Full article ">Figure 10
<p>SEM micrographs of the DIATOMITE–EPOXY coating: (<b>a</b>) General view of the microstructure, (<b>b</b>) Detail of a diatomite disk.</p>
Full article ">Figure 11
<p>SEM micrographs of the DIATOMITE–PFOTS–APTES–EPOXY coating with 25% particle loading: (<b>a</b>) General view of the microstructure, (<b>b</b>) Detail of a diatomite disk.</p>
Full article ">Figure 12
<p>SEM micrographs of the DIATOMITE–PFOTS–APTES–EPOXY coating with 35% particle loading: (<b>a</b>) General view of the microstructure, (<b>b</b>) Detail of a diatomite disk.</p>
Full article ">Figure 13
<p>SEM micrographs of the DIATOMITE–PFOTS–APTES–EPOXY coating with 45% particle loading: (<b>a</b>) General view of the microstructure, (<b>b</b>) Detail of a diatomite disk.</p>
Full article ">Figure 14
<p>Surface roughness measurement: (<b>a</b>) <span class="html-italic">Dektak 3—Veeco</span> profilometer, (<b>b</b>–<b>d</b>) Obtained roughness profiles for the coating.</p>
Full article ">Figure 15
<p>Optical tensiometer theta from Attension<sup>®</sup>: (<b>a</b>) general view of the optical tensiometer and (<b>b</b>) deposition of a droplet using a dosimeter and fixation of the sample with polyamide tape to ensure that the sample is totally flat.</p>
Full article ">Figure 16
<p>Water contact angles for (<b>a</b>) DE–APTES–EPOXY, (<b>b</b>) two-layer DE–PFOTS–EPOXY, (<b>c</b>) DE–PFOTS–APTES–EPOXY, and (<b>d</b>) two-layer DE–PFOTS–APTES–EPOXY.</p>
Full article ">Figure 17
<p>Water contact angle for the stainless steel substrate.</p>
Full article ">Figure 18
<p>Schematic illustration of the adhesion resistance test procedure of the coating.</p>
Full article ">Figure 19
<p>Plot water contact angle vs. number of pull-off cycles.</p>
Full article ">Figure 20
<p>Schematic illustration of the abrasion resistance test procedure for the coatings.</p>
Full article ">Figure 21
<p>Plot water contact angle vs. number of abrasive cycles.</p>
Full article ">Figure 22
<p>Schematic illustration of the apparatus used for the solid impact resistance test.</p>
Full article ">Figure 23
<p>Schematic illustration of the water jet impact resistance testing apparatus.</p>
Full article ">Figure 24
<p>Chart of the water contact angle vs. immersion time for nitric acid and aqua regia.</p>
Full article ">Figure 25
<p>Chart of the water contact angle vs. immersion time for sodium hydroxide.</p>
Full article ">Figure 26
<p>General view of the IN+ pool boiling equipment.</p>
Full article ">Figure 27
<p>DE–PFOTS–APTES–EPOXY coating (<b>a</b>) before and (<b>b</b>) after water boiling immersion for 192 h.</p>
Full article ">Figure A1
<p>Top view of the coatings at 5× magnification.</p>
Full article ">Figure A2
<p>Top view of the coatings at 63× magnification.</p>
Full article ">Figure A3
<p>Thermal conductivity measuring sample preparation: (<b>a</b>) 3D printing mold, (<b>b</b>) diatomite–APTES–PFOTS–epoxy solution poured in the mold, and (<b>c</b>) post-cured coating disk for thermal conductivity measurement.</p>
Full article ">Figure A4
<p>Thermal conductivity hot disk thermal analyzer: (<b>a</b>) general view of the apparatus, (<b>b</b>) front view of the hot disk thermal analyzer, (<b>c</b>) sample holder, and (<b>d</b>) sensor.</p>
Full article ">Figure A5
<p>View of the pool boiling chamber and condenser sections.</p>
Full article ">Figure A6
<p>Stainless steel base of the pool boiling chamber (<b>a</b>) upper side and (<b>b</b>) underside.</p>
Full article ">
25 pages, 1838 KiB  
Review
Achievements and Challenges of Matrix Solid-Phase Dispersion Usage in the Extraction of Plants and Food Samples
by Agnieszka Zgoła-Grześkowiak, Tomasz Grześkowiak, Magdalena Ligor and Robert Frankowski
Processes 2024, 12(6), 1146; https://doi.org/10.3390/pr12061146 - 1 Jun 2024
Viewed by 718
Abstract
A review of the application of matrix solid-phase dispersion (MSPD) in the extraction of biologically active compounds and impurities from plants and food samples with a particular emphasis on conventional and new types of sorbents has been provided. An overview of MSPD applications [...] Read more.
A review of the application of matrix solid-phase dispersion (MSPD) in the extraction of biologically active compounds and impurities from plants and food samples with a particular emphasis on conventional and new types of sorbents has been provided. An overview of MSPD applications for the isolation of organic residues from biological samples, determined using chromatographic and spectroscopic techniques, has been presented. In this study, procedural solutions that may extend MSDP applicability for the extraction such as vortex-assisted, ultrasound-assisted, microwave-assisted, and extraction with a magnetic sorbent have been discussed. Special attention has been paid to MSPD sorbents including modified silica, diatomite, magnesium silicate, alumina, carbon materials (carbon nanotubes, graphene oxide, graphene, or graphite), molecularly imprinted polymers, and cyclodextrin. An important aspect of the MSPD procedure is the use of high-purity and environmentally friendly solvents for extraction (e.g., deep eutectic solvents), with such criteria being the most important for modern analytical chemistry. Many advantages of MSPD are presented, such as high recoveries, the requirement for a smaller volume of solvent, and shorter procedure times than classical methods. Full article
(This article belongs to the Special Issue Separation and Extraction Techniques in Food Processing and Analysis)
Show Figures

Figure 1

Figure 1
<p>Word cloud (also known as tag cloud, word collage or wordle) and timeline results by year for the catchword “matrix solid phase dispersion—MSPD” (source according to <a href="https://www.sciencedirect.com/" target="_blank">https://www.sciencedirect.com/</a>, accessed on 27 May 2024).</p>
Full article ">Figure 2
<p>Scheme of the MSPD procedure.</p>
Full article ">Figure 3
<p>Different technical solutions used in MSPD methods.</p>
Full article ">Figure 4
<p>The methods of performing MSPD extraction procedure. UA-MSPD—ultrasonic-assisted MSPD; MWA-MSPD—microwave-assisted MSPD; VA-MSPD—vortex-assisted MSPD; MA-MSPD—magnetically assisted MSPD.</p>
Full article ">
19 pages, 28912 KiB  
Article
Multifunctional Anatase–Silica Photocatalytic Material for Cements and Concretes
by Valeria Strokova, Yulia Ogurtsova, Ekaterina Gubareva, Sofya Nerovnaya and Marina Antonenko
J. Compos. Sci. 2024, 8(6), 207; https://doi.org/10.3390/jcs8060207 - 31 May 2024
Viewed by 535
Abstract
The purpose of this research was to study the influence of multifunctional anatase–silica photocatalytic materials (ASPMs) with various photocatalytic and pozzolanic activities on the properties of white portland cement and fine-grained concrete. ASPMs were synthesized by a sol–gel method, during which the levels [...] Read more.
The purpose of this research was to study the influence of multifunctional anatase–silica photocatalytic materials (ASPMs) with various photocatalytic and pozzolanic activities on the properties of white portland cement and fine-grained concrete. ASPMs were synthesized by a sol–gel method, during which the levels of photocatalytic and pozzolanic activity were regulated by a certain amount of solvent. ASPMb, obtained with the use of a smaller amount of solvent, was characterized by increased pozzolanic activity due to the lower degree of coating of the surface of diatomite particles with titanium dioxide and the higher content of an opal–cristobalite–tridymite-phase and Bronsted acid sites. They promoted the reaction of diatomite with portlandite of cement stone and allowed significant decreases in the strength of cement–sand mortar to be avoided when replacing 15% of the cement with ASPMs. This allowed self-cleaning fine-grained concrete to be produced, which, after forced carbonization, simulating the natural aging of the product during operation, retained the ability of self-cleaning without changes. ASPMc, produced with the use of a larger amount of solvent with a more uniform distribution of titanium dioxide on the surface of diatomite, allowed fine-grained concrete with a high self-cleaning ability to be obtained, but with a lesser manifestation of the pozzolanic effect. Full article
(This article belongs to the Section Composites Manufacturing and Processing)
Show Figures

Figure 1

Figure 1
<p>Diffraction patterns of the initial diatomite and synthesized ASPMs.</p>
Full article ">Figure 2
<p>The morphology of ASPMb (<b>a</b>,<b>c</b>) and ASPMc (<b>b</b>,<b>d</b>).</p>
Full article ">Figure 2 Cont.
<p>The morphology of ASPMb (<b>a</b>,<b>c</b>) and ASPMc (<b>b</b>,<b>d</b>).</p>
Full article ">Figure 3
<p>The granulometric composition of the initial diatomite and synthesized ASPMs.</p>
Full article ">Figure 4
<p>The absorption of CaO from lime solution of 1 g of the studied material: (<b>—</b>)—integral, (- -)—differential.</p>
Full article ">Figure 5
<p>Differential (<b>a</b>) and integral (<b>b</b>) heat release curves during cement hydration in the presence of various additives.</p>
Full article ">Figure 6
<p>Kinetics of the compressive strength of cement stone depending on the type of additive over time.</p>
Full article ">Figure 7
<p>X-ray diffraction patterns of cement stone at the age of 28 days of hardening.</p>
Full article ">Figure 8
<p>The microstructure of samples after 28 days of hardening.</p>
Full article ">Figure 9
<p>Self-cleaning ability of cement stone samples.</p>
Full article ">Figure 10
<p>Mapping the surface of fine-grained concrete with ASPMs.</p>
Full article ">
20 pages, 5623 KiB  
Article
Improving Sag Resistance in Geopolymer Coatings Using Diatomite Filler: Effects on Rheological Properties and Early Hydration
by Yuan Hu, Zuquan Jin, Bo Pang, Zhantao Du, Xiangxiang Li and Yuxin Huang
Materials 2024, 17(11), 2516; https://doi.org/10.3390/ma17112516 - 23 May 2024
Viewed by 565
Abstract
The reduction in the rheological parameters and dissolution rate of precursors in geopolymer coatings during early hydration significantly contributes to sagging. This study aims to improve the sag resistance of these coatings by incorporating diatomite filler. Rheological testing was conducted to assess the [...] Read more.
The reduction in the rheological parameters and dissolution rate of precursors in geopolymer coatings during early hydration significantly contributes to sagging. This study aims to improve the sag resistance of these coatings by incorporating diatomite filler. Rheological testing was conducted to assess the impact of diatomite and its concentration on the yield stress, plastic viscosity, and thixotropy of the geopolymer coatings. The results indicated that diatomite’s large specific surface area and high reactivity have a significant influence on the rheological parameters and early dissolution rate of precursors. With a diatomite concentration of 1.1%, the coating exhibited a yield stress of 2.749 Pa and a plastic viscosity of 0.921 Pa·s, maintaining stability, homogeneity, and no sagging at a thickness of 600 μm. Furthermore, the highly active SiO2 in diatomite participates in the secondary hydration reaction of the geopolymer materials led to the formation of substantial C-(A)-S-H gel. This gel enhances internal interconnectivity within the coating, thereby improving its rheological and mechanical properties. Full article
(This article belongs to the Section Construction and Building Materials)
Show Figures

Figure 1

Figure 1
<p>(<b>a</b>) Morphology of the raw materials and (<b>b</b>) particle size distributions of the precursor and diatomite.</p>
Full article ">Figure 2
<p>Preparation process of the geopolymer coatings.</p>
Full article ">Figure 3
<p>(<b>a</b>) Photograph of the DHR-2 rheometer and (<b>b</b>) rheological test procedure.</p>
Full article ">Figure 4
<p>(<b>a</b>) The surface morphology and (<b>b</b>) pore structure of diatomite; (<b>c</b>) the internal crystal structure and diffraction patterns of diatomite; (<b>d</b>) XRD results of diatomite.</p>
Full article ">Figure 5
<p>(<b>a</b>) Shear stress–shear rate curves of the alkaline activator and (<b>b</b>) rheological curves of GPC-D0.</p>
Full article ">Figure 6
<p>(<b>a</b>) Dynamic viscosity–shear rate curves and (<b>b</b>) shear stress–shear rate curves of the geopolymer coatings. The Bingham model was fitted to the data.</p>
Full article ">Figure 7
<p>Effect of diatomite content on the rheological parameters of geopolymer coatings.</p>
Full article ">Figure 8
<p>Internal structure model of GPCs with different diatomite contents.</p>
Full article ">Figure 9
<p>The sagging behavior of geopolymer coatings when applied to a vertical concrete surface.</p>
Full article ">Figure 10
<p>Assessment of (<b>a</b>) free water volume and (<b>b</b>) dehydration performance in geopolymer coatings; testing of (<b>c</b>) setting time and (<b>d</b>) drying time for geopolymer coatings.</p>
Full article ">Figure 11
<p>Mechanical strength of the coatings: (<b>a</b>) bonding strength and (<b>b</b>) surface hardness.</p>
Full article ">Figure 12
<p>SEM images of diatomite reaction process in geopolymer coatings.</p>
Full article ">Figure 13
<p>(<b>a</b>) Hydration exothermic rate curves and (<b>b</b>) total hydration exothermic curves of the geopolymer coatings.</p>
Full article ">Figure 14
<p>(<b>a</b><sub>1</sub>) TGA curves of GPCs with different diatomite content and (<b>a</b><sub>2</sub>) a partial enlarged view of the first peak (Ⅰ). TGA curves of (<b>b</b>) GPC-D0 and (<b>c</b>) GPC-D1.1.</p>
Full article ">
21 pages, 11460 KiB  
Article
The Influence of Environmental Factors on the Degradation of PLA/Diatomaceous Earth Composites
by Marta Dobrosielska, Renata Dobrucka, Dariusz Brząkalski, Martyna Pajewska-Szmyt, Krzysztof J. Kurzydłowski and Robert E. Przekop
Polymers 2024, 16(11), 1450; https://doi.org/10.3390/polym16111450 - 21 May 2024
Viewed by 748
Abstract
In the present study, tests were carried out on composite samples on a polylactide matrix containing 25% by weight of mineral filler in the form of diatomaceous earth, base, and silanized with GPTMOS (3-glycidoxypropyltrimethoxysilane), OTES (n-octyltriethoxysilane), and MTMOS (methyltrimethoxysilane) silanes. The addition of [...] Read more.
In the present study, tests were carried out on composite samples on a polylactide matrix containing 25% by weight of mineral filler in the form of diatomaceous earth, base, and silanized with GPTMOS (3-glycidoxypropyltrimethoxysilane), OTES (n-octyltriethoxysilane), and MTMOS (methyltrimethoxysilane) silanes. The addition of two types of waxes, synthetic polyamide wax and natural beeswax, were used as a factor to increase the rheological properties of the composites. The obtained samples were characterized in terms of the effect of filler silanization on the degradation rate of the composites. The tests were conducted under different conditioning conditions, i.e., after exposure to strong UV radiation for 250 and 500 h, and under natural sunlight for 21 days. The conditioning carried out under natural conditions showed that the modified samples exhibit up to twice the degradation rate of pure polylactide. The addition of synthetic wax to the composites increases the tendency to agglomerate diatomaceous earth, while natural wax has a positive effect on filler dispersion. For composites modified with GPTMOS and OTES silanes, it was noted that the addition of natural wax inhibited the degree of surface degradation, compared to the addition of synthetic wax, while the addition of MTMOS silane caused the opposite effect and samples with natural wax degraded more strongly. It was shown that, despite the high degree of surface degradation, the process does not occur significantly deep into the composite and stops at a certain depth. Full article
(This article belongs to the Section Polymer Physics and Theory)
Show Figures

Figure 1

Figure 1
<p>UV-aging sample holder.</p>
Full article ">Figure 2
<p>Average daily air temperature, and maximum air temperature and minimum air temperature (<b>A</b>); average daily wind speed, average cloud cover, sunshine hours, and average daily rainfall (<b>B</b>); UV index (<b>C</b>); and average humidity and average pressure (<b>D</b>) between 15 June 2021 and 6 July 2021.</p>
Full article ">Figure 3
<p>Tensile strength and elongation at break of the composites in as-received state and after aging under natural conditions.</p>
Full article ">Figure 4
<p>MWD curve of polylactide conditioned at room temperature and at 500 h in an aging chamber and G/2S-modified composite conditioned at 500 h in an aging chamber.</p>
Full article ">Figure 5
<p>Determined chain degradation for the polymer samples tested.</p>
Full article ">Figure 6
<p>Determined dispersity index (Ð) for the tested samples, after different aging periods.</p>
Full article ">Figure 7
<p>GPC-RI analysis for PLA sample without additive and with addition of diatomaceous earth.</p>
Full article ">Figure 8
<p>Particle size distribution of diatomaceous earth.</p>
Full article ">Figure 9
<p>Differences in color of composites conditioned in an aging chamber for 250 and 500 h and under natural conditions.</p>
Full article ">Figure 10
<p>Luminance of composites conditioned in an aging chamber for 250 and 500 h and under natural conditions.</p>
Full article ">Figure 11
<p>Composites before and after conditioning in a UV-aging chamber for 250 and 500 h.</p>
Full article ">Figure 12
<p>Surfaces of composites before and after placement in UV chamber (250 h and 500 h); systems without silanization.</p>
Full article ">Figure 13
<p>Surfaces of composites before and after placement in UV chamber for 250 and 500 h; silanized systems.</p>
Full article ">Figure 14
<p>Edge structures of composite breakthroughs before and after placement in UV chamber (250 h and 500 h); systems without silanization.</p>
Full article ">Figure 15
<p>Edge structures of composite breakthroughs before and after placement in UV chamber for 250 and 500 h; silanized systems.</p>
Full article ">
Back to TopTop