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Clean preparation of rutile from Ti-containing mixed molten slag by CO2 oxidation

  • Jiqing Han EMAIL logo , Qiuping Feng and Li Zhang EMAIL logo
Published/Copyright: October 10, 2023
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Abstract

The effects of SiO2 and CO2 on the crystallization action of Ti-containing mixed molten slag (molten Ti-containing blast furnace slag and molten Ti slag) were discussed by thermodynamic calculation and specific experiments. The results of thermodynamic calculation indicated that the increase of SiO2 addition mass and CO2 oxidation time can promote the transformation of anosovite and sphene to rutile. The experiment results showed that the phase composition of modification slag was only rutile under the SiO2 addition mass of 110 g and the CO2 oxidation time of 180 s. Moreover, the formation theory of rutile was investigated. Using CO2 as an oxidizing gas can not only prepare rutile but also achieve carbon neutrality, which is a clean preparation method.

1 Introduction

China has rich Ti resources, which mainly are present as V–Ti magnetite. Its total reserve is approximately 10 billion tons, 90% of which are located in the Panzhihua and Xichang regions of Sichuan province. After beneficiation, 50% of titanium components enter the V–Ti magnetite concentrate. After blast furnace ironmaking, the Ti components in the concentrate enter the slag to form Ti-containing blast furnace slag (20–25% TiO2). The multipurpose use of Ti-containing blast furnace slag has been a technical difficulty in China. Because the Ti compositions in this slag are dispersedly distributed in different fine Ti-containing phases, conventional beneficiation methods make it difficult to separate the Ti-containing phase from the gangue phase. Therefore, the multipurpose use of Ti-containing blast furnace slag is extremely difficult.

To realize the multipurpose use of Ti-containing blast furnace slag, a lot of related studies have been carried out. According to the classification of products, research methods can be divided into the following categories: building materials [1], titanium alloy [2], photocatalytic materials [3], titanium white [4], titanium tetrachloride [5], perovskite [6], anosovite [7,8], and rutile [9,10,11,12,13,14,15,16]. Although the previous methods can realize the multipurpose use of Ti-containing blast furnace slag, they generally have the disadvantages of high energy consumption and high cost. So far, Ti-containing blast furnace slag can only be stacked in the slag yard, causing the squander of Ti resources and environmental pollution.

To resolve the above-mentioned problems, the platform technology [17] for molten slag metallurgy, mineral regeneration, and resource recycling were proposed by Professor Zhang Li of Northeastern University. In view of the mineral characteristics of metallurgical molten slag, a separation technology for oxide mineral settling was proposed for the first time to realize the efficient utilization of physical heat and the efficient recovery of minerals. The platform technology is developed by the interdisciplinary integration of geology, minerals, materials, metallurgy, and thermal energy. It has the characteristics of short process, low cost, cleanness, low carbon, and high efficiency. It does not require heating or a small amount of heating and realizes energy utilization, mineral regeneration, resources recycling, and environmental protection.

Based on the platform technology, the clean, high-efficiency, and low-carbon utilization technology of Ti-containing mixed molten slag (molten Ti-containing blast furnace slag and molten Ti slag) was proposed. This technology consists of two parts:

  1. Mineral regeneration: Taking full the merits of the high physical heat and chemical activity of molten Ti-containing blast furnace slag and molten Ti slag, the two molten slags are mixed. With the help of oxidation and modification, Ti components form a man-made mineral (rutile) with a high melting temperature, high density, and high crystallization temperature. The impurity components form a glassy phase with a low melting temperature, low density, and low crystallization temperature.

  2. Rutile settling: Under the action of crystallization differentiation and gravity differentiation, the man-made mineral (rutile) begins to settle, realizing the transformation from lean ore into rich ore.

The previous studies [18,19,20] have achieved the transformation of Ti components in Ti-containing mixed molten slag to rutile by O2 oxidation. In this article, the preparation of rutile from Ti-containing mixed molten slag by CO2 oxidation was first proposed. Using CO2 as an oxidizing gas can not only prepare rutile but also achieve carbon neutrality, which is a clean preparation method.

The objective of this article is to propose a method for the clean preparation of rutile from Ti-bearing mixed molten slag by CO2 oxidation. The effects of SiO2 and CO2 on the crystallization action of the Ti-containing mixed molten slag were studied by thermodynamic calculation and specific experiments. Furthermore, the formation theory of rutile was investigated.

2 Materials and methods

2.1 Materials

Ti-containing blast furnace slag and Ti slag were gotten from the Panzhihua (Sichuan province, China). The chemical components and phase compositions of Ti-containing blast furnace slag and Ti slag are illustrated in Table 1 and Figure 1.

Table 1

Chemical components of (1) Ti-containing blast furnace slag and (2) Ti slag

NO. TiO2 Ti2O3 CaO SiO2 Al2O3 MgO MFe FeO
1 17.58 3.86 26.87 25.13 14.08 7.86 2.18 1.51
2 60.72 14.65 4.32 8.85 2.64 2.02 0.96

Note: %, mass fraction; MFe is the content of metallic iron.

Figure 1 
                  Phase compositions of (a) Ti-containing blast furnace slag and (b) Ti slag.
Figure 1

Phase compositions of (a) Ti-containing blast furnace slag and (b) Ti slag.

As illustrated in Figure 1, the phase components of Ti-containing blast furnace slag were perovskite, magnesia-alumina spinel, diopside, and akermanite. The phase components of Ti slag were anosovite and anorthite.

2.2 Experimental procedures

2.2.1 Thermodynamic calculation

The schematic diagram of experimental process is shown in Figure 2. As illustrated in Figure 2, the effects of SiO2 and CO2 on the crystallization action of Ti-containing mixed molten slag were calculated by the equilibrium module of software Factsage with FToxid and FactPS databases (version 7.1). The chemical compositions of Ti-containing mixed molten slag, the addition mass of SiO2, and CO2 oxidation time were input into the software. Then, it will output the type and mass of precipitation phases.

Figure 2 
                     Schematic diagram of experimental process.
Figure 2

Schematic diagram of experimental process.

2.2.2 Modification experiments

Based on the above-mentioned thermodynamic calculation, 278 g of Ti slag, 222 g of Ti-containing blast furnace slag, and a definite mass of silicon dioxide (50, 70, 90, and 110 g) were placed in a crucible at 1,460°C for 30 min. Whereupon, CO2 was introduced into the mixed molten slag with a given time (60, 120, 180, and 240 s) and a flow rate of 4 L·min−1. Afterward, the modification slag was cooled to room temperature with a cooling rate of 6°C·min−1. The SiO2 was of analytical grade, and the purity of CO2 was 99% (mass fraction). The schematic diagram of the modified experimental device is shown in Figure 3. As shown in Figure 3, the heating equipment was a vertical MoSi2 furnace with a B-type thermocouple. It was estimated that the overall absolute temperature accuracy of the furnace was ±3°C.

Figure 3 
                     Schematic diagram of modified experimental device.
Figure 3

Schematic diagram of modified experimental device.

2.3 Characterization

The phase components were determined by X-ray diffraction (X’PERT PROMPD/PW3040). The microstructure and element distribution were determined by scanning electron microscopy (TESCAN VEGA III) equipped with an energy-dispersive spectrometer (INCA Energy 350).

3 Results and discussion

3.1 Thermodynamic calculation on CO2 oxidation time

The addition mass of silicon dioxide was fixed at 50 g. After that, the influence of CO2 oxidation time on the crystallization action of the mixed molten slag was investigated by software. The calculation results are illustrated in Figures 46.

Figure 4 
                  Effects of CO2 oxidation time on the crystallization action: (a) 0 s, (b) 60 s, (c) 120 s, (d) 180 s, (e) 240 s, and (f) 300 s.
Figure 4

Effects of CO2 oxidation time on the crystallization action: (a) 0 s, (b) 60 s, (c) 120 s, (d) 180 s, (e) 240 s, and (f) 300 s.

Figure 5 
                  Effect of CO2 oxidation time on the crystallized temperature of rutile.
Figure 5

Effect of CO2 oxidation time on the crystallized temperature of rutile.

Figure 6 
                  Influence of CO2 oxidation time on the final mass of Ti-containing precipitation phases.
Figure 6

Influence of CO2 oxidation time on the final mass of Ti-containing precipitation phases.

As illustrated in Figure 4a and b, the main titanium-bearing mineral phases are anosovite ((AO·2TiO2) m ·(B2O3·TiO2) n ) and sphene (CaSiTiO5) while the CO2 oxidation times are 0 and 60 s. As illustrated in Figure 4c–f, the titanium-bearing mineral phases are rutile, sphene, and anosovite, while the CO2 oxidation times are 120, 180, 240, and 300 s. It can be seen that other phases begin to precipitate when the mass of rutile precipitation reaches the maximum value. Moreover, as shown in Figure 5, the crystallized temperature of rutile rises as CO2 oxidation time improves. To sum up, the improvement of CO2 oxidation time can promote the crystallization of rutile crystals and inhibit the crystallization of other crystals.

As illustrated in Figure 6, with the CO2 oxidation time improving from 0 to 180 s, the mass of rutile precipitation markedly rises, and the mass of anosovite and sphene precipitation decreases rapidly. As the CO2 oxidation time improves to 300 s, the mass of rutile precipitation no longer improves, and the mass of anosovite and sphene precipitation no longer decreases. Therefore, the optimal CO2 oxidation time is 180 s. It can be seen that the improving of CO2 oxidation time can promote the transformation of anosovite and sphene to rutile.

3.2 Experimental verification on CO2 oxidation time

The addition mass of silicon dioxide was fixed at 50 g. After that, the influence of CO2 oxidation time on the crystallization action of the mixed molten slag was investigated by specific experiments. The experiment results are shown in Figures 7 and 8 and Table 2.

Figure 7 
                  Phase components of the modification slags with diverse CO2 oxidation times.
Figure 7

Phase components of the modification slags with diverse CO2 oxidation times.

Figure 8 
                  Microstructure of the modification slag with diverse CO2 oxidation times: (a) 60 s, (b) 120 s, (c) 180 s, and (d) 240 s.
Figure 8

Microstructure of the modification slag with diverse CO2 oxidation times: (a) 60 s, (b) 120 s, (c) 180 s, and (d) 240 s.

Table 2

Element distribution of every point in Figure 8

Points O (wt%) Mg (wt%) Al (wt%) Si (wt%) Ca (wt%) Ti (wt%) Mn (wt%) Fe (wt%)
P1 36.85 8.74 14.03 16.79 14.11 2.73 3.41 3.34
P2 36.51 2.42 2.13 57.86 0.74 0.34
P3 33.87 66.13
P4 37.42 8.36 13.15 16.82 14.64 2.03 3.69 3.89
P5 38.54 1.65 1.83 57.23 0.45 0.30
P6 36.48 63.52
P7 37.51 8.17 13.74 16.55 14.43 2.19 3.74 3.67
P8 38.62 1.54 1.76 57.04 0.57 0.47
P9 38.53 61.47
P10 37.41 8.03 14.12 16.27 14.75 2.04 3.89 3.49
P11 38.96 1.13 1.52 57.31 0.42 0.66
P12 39.13 60.87

As illustrated in Figure 7, the phase components of the modification slag were unchanged while the CO2 oxidation time was 60–240 s, that is, rutile and anosovite. Nevertheless, the diffraction peaks of anosovite reduced and the peak intensity significantly decreased when the CO2 oxidation time increased from 60 to 180 s, meaning that the improvement of CO2 oxidation time promoted the transformation of anosovite to rutile. It can be seen from Figure 8 and Table 2 that P3, P6, P9, and P12 were rutile. P2, P5, P8, and P11 were anosovite. P1, P4, P7, and P10 were matrix phases. The above-mentioned results imply that the phase components of the modification slag were rutile and anosovite while the CO2 oxidation time was 60–240 s. Moreover, as the CO2 oxidation time improved from 60 to 240 s, the Ti content of rutile reduced from 66.13 to 60.87 wt%, and the O content of rutile increased from 33.87 to 39.13 wt%. When the CO2 oxidation time was 240 s, the mass ratio of Ti with O was 60.87/39.13. The ratio was close to the Ti/O mass ratio (6/4) of TiO2, meaning that the improvement of CO2 oxidation time accelerated the transformation of anosovite to rutile. To sum up, the experimental results were consistent with the thermodynamic calculation results; that is, the improvement of CO2 oxidation time accelerated the transformation of anosovite to rutile.

3.3 Thermodynamic calculation on the addition mass of SiO2

The CO2 oxidation time was fixed at 180 s. After that, the influence of the addition mass of silicon dioxide on the crystallization action of the mixed molten slag was investigated by FactSage software. The calculation results are shown in Figures 911.

Figure 9 
                  Effects of the addition mass of SiO2 on the crystallization behavior: (a) 30 g, (b) 50 g, (c) 70 g, (d) 90 g, (e) 110 g, and (f) 130 g.
Figure 9

Effects of the addition mass of SiO2 on the crystallization behavior: (a) 30 g, (b) 50 g, (c) 70 g, (d) 90 g, (e) 110 g, and (f) 130 g.

Figure 10 
                  Effects of the addition mass of SiO2 on the crystallized temperature of rutile.
Figure 10

Effects of the addition mass of SiO2 on the crystallized temperature of rutile.

Figure 11 
                  Effects of the addition mass of SiO2 on the final mass of Ti-bearing precipitation phases.
Figure 11

Effects of the addition mass of SiO2 on the final mass of Ti-bearing precipitation phases.

As illustrated in Figure 9a–f, the Ti-bearing mineral phases are rutile, sphene, and anosovite while the addition mass of silicon dioxide is 30–130 g. Moreover, it can be seen that other phases begin to precipitate when the mass of rutile precipitation reaches the maximum value. As illustrated in Figure 10, the crystallization temperature of rutile raises as the addition mass of silicon dioxide improves. To sum up, the improvement of the SiO2 addition mass can promote the crystallization of rutile crystals and inhibit the crystallization of other crystals.

As illustrated in Figure 11, when the addition mass of silicon dioxide improves from 30 to 110 g, the mass of rutile precipitation observably improves, and the mass of anosovite and sphene precipitation decreases rapidly. With the addition mass of silicon dioxide improving to 130 g, the mass of rutile precipitation remained unchanged, and the mass of anosovite and sphene precipitation also remained unchanged. Thus, the optimum addition mass of SiO2 is 110 g. It can be seen that the improvement of the SiO2 addition mass can promote the transformation of anosovite and sphene to rutile.

3.4 Experimental verification on the addition mass of SiO2

The CO2 oxidation time was fixed at 180 s. After that, the influence of the addition mass of silicon dioxide on the crystallization action of the mixed molten slag was investigated by relevant experiments. The experiment results are shown in Figures 12 and 13 and Table 3.

Figure 12 
                  Phase components of the modification slags with diverse addition mass of SiO2.
Figure 12

Phase components of the modification slags with diverse addition mass of SiO2.

Figure 13 
                  Microstructure of the modification slag with diverse addition mass of SiO2: (a) 50 g, (b) 70 g, (c) 90 g, and (d) 110 g.
Figure 13

Microstructure of the modification slag with diverse addition mass of SiO2: (a) 50 g, (b) 70 g, (c) 90 g, and (d) 110 g.

Table 3

Element distribution of every point in Figure 13

Points O (wt%) Mg (wt%) Al (wt%) Si (wt%) Ca (wt%) Ti (wt%) Mn (wt%) Fe (wt%)
P1 41.68 6.12 11.61 16.42 15.13 1.87 3.43 3.74
P2 42.36 7.56 6.89 39.57 1.13 2.49
P3 35.45 64.55
P4 38.42 7.53 12.13 16.89 15.02 2.16 3.56 4.29
P5 41.13 6.03 5.13 45.26 0.86 1.59
P6 35.87 64.13
P7 36.75 8.65 13.42 17.13 13.46 2.36 3.42 4.81
P8 40.76 3.37 2.34 52.26 0.51 0.76
P9 36.47 63.53
P10 36.02 10.15 13.78 17.47 13.14 1.43 3.87 4.14
P11 40.45 59.55
P12 40.51 59.49

As illustrated in Figure 12, the phase component of the modification slag was unchanged when the addition mass of silicon dioxide improved from 50 to 90 g, i.e., rutile and anosovite. However, the diffraction peaks of anosovite reduced and the peak intensity significantly decreased. With the addition mass of SiO2 improving from 90 to 110 g, anosovite phase disappeared, and the Ti-bearing phase of the modification slag was only rutile. Furthermore, it can be seen from Figure 13 and Table 3 that P2, P5, and P8 were all anosovite. P3, P6, and P9 were all rutile. P1, P4, and P7 were matrix phases. The above results imply that the phase components of the modification slag were rutile and anosovite when the addition mass of silicon dioxide was 50–90 g. With the addition mass of silicon dioxide improving from 90 to 110 g, the anosovite phase disappeared, and the Ti-bearing phase of the modification slag was only rutile. To sum up, the experimental results are consistent with the thermodynamic calculation results; that is, the improvement of the SiO2 addition mass promoted the transformation of anosovite to rutile.

It can be seen from the above results that the thermodynamic calculation contained different phases, but the experiment did not. This is because theoretical calculation only considered thermodynamic conditions and ignored kinetic conditions. Because the purpose of this article was to obtain rutile, we only focused on the transformation of titanium-containing phases. According to the results of thermodynamic calculation, the main Ti-bearing phases (due to the very low mass of Ti20O39 and perovskite, they were ignored) were rutile, anosovite, and sphene. According to the results of experiments, the main Ti-bearing phases were rutile and anosovite. It can be seen that the theoretical calculation results were consistent with the experimental results. The only difference is that the titanium-bearing phases of the experimental results did not include sphene. This may be because thermodynamic calculation ignored the effect of kinetics conditions.

3.5 Theory of rutile precipitation

In order to investigate the theory of rutile precipitation, the standard Gibbs free-energy changes (∆G Φ) of relevant reactions were calculated by the reaction module of Factsage software. The calculation results are illustrated in Figure 14.

Figure 14 
                  ∆G
                     Φ of reactions 1–12.
Figure 14

G Φ of reactions 1–12.

As illustrated in Figure 14, the products of reactions (4–7) are all anosovite. The ∆G Φ of reactions (1) and (2) are less than those of reactions (3–5), meaning that reactions (3–5) are restrained as the addition mass of SiO2 improves. In other words, the precipitation of anosovite and perovskite is inhibited. Thus, the addition of SiO2 can promote the conversion of anosovite and perovskite to Ti oxides (TiO2, Ti3O5, Ti2O3, and TiO). As shown in Figure 14, the ∆G Φ of reactions (8–12) is less than those of reactions (6–7), indicating that reactions (6–7) are restrained as CO2 oxidation time improves. In other words, the precipitation of anosovite is inhibited. It is well known that anosovite is a solid solution based on Ti3O5. Thus, CO2 oxidation can eliminate low-valent titanium oxides including Ti3O5 and promote the transformation of anosovite into rutile. To sum up, reactions (3–7) are restrained, and Ti compositions are present as rutile while CO2 and SiO2 are concurrently added to the mixed molten slag.

4 Conclusions

  1. The improvement of SiO2 addition mass and CO2 oxidation time can promote the transformation of anosovite to rutile.

  2. The optimal experiment conditions were the SiO2 addition mass of 110 g and the CO2 oxidation time of 180 s, and the phase composition of slag was only rutile under the above conditions.

  3. Using CO2 as an oxidizing gas can not only prepare rutile but also achieve carbon neutrality, which is a clean preparation method.

  1. Funding information: This work was supported by Funding Project for National Science and Technology Support Program of China (grant number: 2015BAB18B00).

  2. Author contributions: Li Zhang: methodology, resources; Jiqing Han: writing – original draft, writing – review and editing, visualization, methodology; Qiuping Feng: writing – review and editing.

  3. Conflict of interest: The authors state no conflict of interest.

  4. Data Availability Statement: The datasets generated during and/or analysed during the current study are available from the corresponding author on reasonable request.

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Received: 2023-05-28
Revised: 2023-07-22
Accepted: 2023-08-14
Published Online: 2023-10-10

© 2023 the author(s), published by De Gruyter

This work is licensed under the Creative Commons Attribution 4.0 International License.

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  46. Catalysts based on nickel salt heteropolytungstates for selective oxidation of diphenyl sulfide
  47. Powerful antibacterial nanocomposites from Corallina officinalis-mediated nanometals and chitosan nanoparticles against fish-borne pathogens
  48. Removal behavior of Zn and alkalis from blast furnace dust in pre-reduction sinter process
  49. Environmentally friendly synthesis and computational studies of novel class of acridinedione integrated spirothiopyrrolizidines/indolizidines
  50. The mechanisms of inhibition and lubrication of clean fracturing flowback fluids in water-based drilling fluids
  51. Adsorption/desorption performance of cellulose membrane for Pb(ii)
  52. A one-pot, multicomponent tandem synthesis of fused polycyclic pyrrolo[3,2-c]quinolinone/pyrrolizino[2,3-c]quinolinone hybrid heterocycles via environmentally benign solid state melt reaction
  53. Green synthesis of silver nanoparticles using durian rind extract and optical characteristics of surface plasmon resonance-based optical sensor for the detection of hydrogen peroxide
  54. Electrochemical analysis of copper-EDTA-ammonia-gold thiosulfate dissolution system
  55. Characterization of bio-oil production by microwave pyrolysis from cashew nut shells and Cassia fistula pods
  56. Green synthesis methods and characterization of bacterial cellulose/silver nanoparticle composites
  57. Photocatalytic research performance of zinc oxide/graphite phase carbon nitride catalyst and its application in environment
  58. Effect of phytogenic iron nanoparticles on the bio-fortification of wheat varieties
  59. In vitro anti-cancer and antimicrobial effects of manganese oxide nanoparticles synthesized using the Glycyrrhiza uralensis leaf extract on breast cancer cell lines
  60. Preparation of Pd/Ce(F)-MCM-48 catalysts and their catalytic performance of n-heptane isomerization
  61. Green “one-pot” fluorescent bis-indolizine synthesis with whole-cell plant biocatalysis
  62. Silica-titania mesoporous silicas of MCM-41 type as effective catalysts and photocatalysts for selective oxidation of diphenyl sulfide by H2O2
  63. Biosynthesis of zinc oxide nanoparticles from molted feathers of Pavo cristatus and their antibiofilm and anticancer activities
  64. Clean preparation of rutile from Ti-containing mixed molten slag by CO2 oxidation
  65. Synthesis and characterization of Pluronic F-127-coated titanium dioxide nanoparticles synthesized from extracts of Atractylodes macrocephala leaf for antioxidant, antimicrobial, and anticancer properties
  66. Effect of pretreatment with alkali on the anaerobic digestion characteristics of kitchen waste and analysis of microbial diversity
  67. Ameliorated antimicrobial, antioxidant, and anticancer properties by Plectranthus vettiveroides root extract-mediated green synthesis of chitosan nanoparticles
  68. Microwave-accelerated pretreatment technique in green extraction of oil and bioactive compounds from camelina seeds: Effectiveness and characterization
  69. Studies on the extraction performance of phorate by aptamer-functionalized magnetic nanoparticles in plasma samples
  70. Investigation of structural properties and antibacterial activity of AgO nanoparticle extract from Solanum nigrum/Mentha leaf extracts by green synthesis method
  71. Green fabrication of chitosan from marine crustaceans and mushroom waste: Toward sustainable resource utilization
  72. Synthesis, characterization, and evaluation of nanoparticles of clodinofop propargyl and fenoxaprop-P-ethyl on weed control, growth, and yield of wheat (Triticum aestivum L.)
  73. The enhanced adsorption properties of phosphorus from aqueous solutions using lanthanum modified synthetic zeolites
  74. Separation of graphene oxides of different sizes by multi-layer dialysis and anti-friction and lubrication performance
  75. Visible-light-assisted base-catalyzed, one-pot synthesis of highly functionalized cinnolines
  76. The experimental study on the air oxidation of 5-hydroxymethylfurfural to 2,5-furandicarboxylic acid with Co–Mn–Br system
  77. Highly efficient removal of tetracycline and methyl violet 2B from aqueous solution using the bimetallic FeZn-ZIFs catalyst
  78. A thermo-tolerant cellulase enzyme produced by Bacillus amyloliquefaciens M7, an insight into synthesis, optimization, characterization, and bio-polishing activity
  79. Exploration of ketone derivatives of succinimide for their antidiabetic potential: In vitro and in vivo approaches
  80. Ultrasound-assisted green synthesis and in silico study of 6-(4-(butylamino)-6-(diethylamino)-1,3,5-triazin-2-yl)oxypyridazine derivatives
  81. A study of the anticancer potential of Pluronic F-127 encapsulated Fe2O3 nanoparticles derived from Berberis vulgaris extract
  82. Biogenic synthesis of silver nanoparticles using Consolida orientalis flowers: Identification, catalytic degradation, and biological effect
  83. Initial assessment of the presence of plastic waste in some coastal mangrove forests in Vietnam
  84. Adsorption synergy electrocatalytic degradation of phenol by active oxygen-containing species generated in Co-coal based cathode and graphite anode
  85. Antibacterial, antifungal, antioxidant, and cytotoxicity activities of the aqueous extract of Syzygium aromaticum-mediated synthesized novel silver nanoparticles
  86. Synthesis of a silica matrix with ZnO nanoparticles for the fabrication of a recyclable photodegradation system to eliminate methylene blue dye
  87. Natural polymer fillers instead of dye and pigments: Pumice and scoria in PDMS fluid and elastomer composites
  88. Study on the preparation of glycerylphosphorylcholine by transesterification under supported sodium methoxide
  89. Wireless network handheld terminal-based green ecological sustainable design evaluation system: Improved data communication and reduced packet loss rate
  90. The optimization of hydrogel strength from cassava starch using oxidized sucrose as a crosslinking agent
  91. Green synthesis of silver nanoparticles using Saccharum officinarum leaf extract for antiviral paint
  92. Study on the reliability of nano-silver-coated tin solder joints for flip chips
  93. Environmentally sustainable analytical quality by design aided RP-HPLC method for the estimation of brilliant blue in commercial food samples employing a green-ultrasound-assisted extraction technique
  94. Anticancer and antimicrobial potential of zinc/sodium alginate/polyethylene glycol/d-pinitol nanocomposites against osteosarcoma MG-63 cells
  95. Nanoporous carbon@CoFe2O4 nanocomposite as a green absorbent for the adsorptive removal of Hg(ii) from aqueous solutions
  96. Characterization of silver sulfide nanoparticles from actinobacterial strain (M10A62) and its toxicity against lepidopteran and dipterans insect species
  97. Phyto-fabrication and characterization of silver nanoparticles using Withania somnifera: Investigating antioxidant potential
  98. Effect of e-waste nanofillers on the mechanical, thermal, and wear properties of epoxy-blend sisal woven fiber-reinforced composites
  99. Magnesium nanohydroxide (2D brucite) as a host matrix for thymol and carvacrol: Synthesis, characterization, and inhibition of foodborne pathogens
  100. Synergistic inhibitive effect of a hybrid zinc oxide-benzalkonium chloride composite on the corrosion of carbon steel in a sulfuric acidic solution
  101. Review Articles
  102. Role and the importance of green approach in biosynthesis of nanopropolis and effectiveness of propolis in the treatment of COVID-19 pandemic
  103. Gum tragacanth-mediated synthesis of metal nanoparticles, characterization, and their applications as a bactericide, catalyst, antioxidant, and peroxidase mimic
  104. Green-processed nano-biocomposite (ZnO–TiO2): Potential candidates for biomedical applications
  105. Reaction mechanisms in microwave-assisted lignin depolymerisation in hydrogen-donating solvents
  106. Recent progress on non-noble metal catalysts for the deoxydehydration of biomass-derived oxygenates
  107. Rapid Communication
  108. Phosphorus removal by iron–carbon microelectrolysis: A new way to achieve phosphorus recovery
  109. Special Issue: Biomolecules-derived synthesis of nanomaterials for environmental and biological applications (Guest Editors: Arpita Roy and Fernanda Maria Policarpo Tonelli)
  110. Biomolecules-derived synthesis of nanomaterials for environmental and biological applications
  111. Nano-encapsulated tanshinone IIA in PLGA-PEG-COOH inhibits apoptosis and inflammation in cerebral ischemia/reperfusion injury
  112. Green fabrication of silver nanoparticles using Melia azedarach ripened fruit extract, their characterization, and biological properties
  113. Green-synthesized nanoparticles and their therapeutic applications: A review
  114. Antioxidant, antibacterial, and cytotoxicity potential of synthesized silver nanoparticles from the Cassia alata leaf aqueous extract
  115. Green synthesis of silver nanoparticles using Callisia fragrans leaf extract and its anticancer activity against MCF-7, HepG2, KB, LU-1, and MKN-7 cell lines
  116. Algae-based green AgNPs, AuNPs, and FeNPs as potential nanoremediators
  117. Green synthesis of Kickxia elatine-induced silver nanoparticles and their role as anti-acetylcholinesterase in the treatment of Alzheimer’s disease
  118. Phytocrystallization of silver nanoparticles using Cassia alata flower extract for effective control of fungal skin pathogens
  119. Antibacterial wound dressing with hydrogel from chitosan and polyvinyl alcohol from the red cabbage extract loaded with silver nanoparticles
  120. Leveraging of mycogenic copper oxide nanostructures for disease management of Alternaria blight of Brassica juncea
  121. Nanoscale molecular reactions in microbiological medicines in modern medical applications
  122. Synthesis and characterization of ZnO/β-cyclodextrin/nicotinic acid nanocomposite and its biological and environmental application
  123. Green synthesis of silver nanoparticles via Taxus wallichiana Zucc. plant-derived Taxol: Novel utilization as anticancer, antioxidation, anti-inflammation, and antiurolithic potential
  124. Recyclability and catalytic characteristics of copper oxide nanoparticles derived from bougainvillea plant flower extract for biomedical application
  125. Phytofabrication, characterization, and evaluation of novel bioinspired selenium–iron (Se–Fe) nanocomposites using Allium sativum extract for bio-potential applications
  126. Erratum
  127. Erratum to “Synthesis, characterization, and evaluation of nanoparticles of clodinofop propargyl and fenoxaprop-P-ethyl on weed control, growth, and yield of wheat (Triticum aestivum L.)”
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