Next Article in Journal
Mineralogical-Petrographical Record of Melt-Rock Interaction and P–T Estimates from the Ozren Massif Ophiolites (Bosnia and Herzegovina)
Next Article in Special Issue
Crystal Transformation of Sericite during Fluidized Roasting: A Study Combining Experiment and Simulation
Previous Article in Journal
The Migration of Cd in Granitic Residual Soil and Marine Clay: Batch and Column Studies
Previous Article in Special Issue
Study on Microstructure Evolution of Oolitic Hematite during Microwave Fluidization Roasting
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Effects of NaOH Content on the Reduction Kinetics of Hematite by Using Suspension Magnetization Roasting Technology

1
School of Resources and Civil Engineering, Northeastern University, Shenyang 110819, China
2
National-Local Joint Engineering Research Center of High-Efficient Exploitation Technology for Refractory Iron Ore Resources, Shenyang 110819, China
*
Author to whom correspondence should be addressed.
Minerals 2022, 12(9), 1107; https://doi.org/10.3390/min12091107
Submission received: 30 June 2022 / Revised: 21 August 2022 / Accepted: 30 August 2022 / Published: 30 August 2022
(This article belongs to the Special Issue Mineral Processing Technologies of Complex Refractory Iron Ore)

Abstract

:
Red mud is a potential iron resource that needs to be urgently exploited and utilized. However, due to the properties of high alkalinity, fine particle size and complex mineral composition, the utilization of red mud is difficult. Focusing on red mud’s prominent feature of high alkalinity, this paper studies the influence of NaOH content on the reduction kinetics of hematite, which is the main component of red mud. The results show that the conversion degree of hematite was strongly inhibited by NaOH, and the magnetization and specific magnetic susceptibility of reduction products was significantly decreased with the increase in NaOH content. Meanwhile, the results of the calculation of kinetics parameters demonstrate that the addition of NaOH did not affect the control step of the reduction of hematite, while it dramatically decreased the reduction rate of hematite. Moreover, thermodynamic analysis and SEM-EDS detection were conducted to uncover the inhibited mechanism of NaOH on the reduction of hematite, which indicated that sodium ferrite could be produced spontaneously under the experimental conditions and that it is hard for it to be further reduced by CO. Furthermore, the produced sodium ferrite formed a dense film, which covered the surface of the hematite particles, inhibiting the diffusion of CO and thereby hindering the reduction of the interior hematite.

1. Introduction

Red mud, one of the major waste materials, is produced in the alumina extraction process. Due to its fine particle size, strong corrosivity and complex mineral composition, the efficient utilization of untreated red mud is hard to realize [1,2,3]. According to statistics, the global reserves of red mud have more than 4 billion tons, and it continues to grow by about 175.5 million tons per year [4,5]. As the largest producer of alumina, China possesses large quantities of red mud and the storage has exceeded 600 million tons. Furthermore, there are also over 100 million tons of red mud per year produced in China [5,6]. At present, land stockpiling is the main method to treat red mud. However, it results in a series of environmental–hydrogeological problems and destroys the balance of the ecological environment [7,8].
Red mud has a remarkable economic worth, since it contains abundant valuable metal elements such as iron, aluminum, vanadium and titanium [9,10,11]. Among these elements, the iron in high-iron red mud is usually more than 30%, which is higher than that of raw iron ore in the most Chinese mines. Therefore, the efficient recycling and utilization of iron from high-iron red mud has significant influence on the development of the national economy and the comprehensive improvement of the ecosystem environment.
In the last few decades, plenty of studies have been conducted to investigate the most efficient method of extracting iron from red mud. Among them, suspension magnetization roasting (SMR) developed by the Han research tem (Northeastern University) is regarded as a potentially efficient method to treat refractory iron ore due to its low roasting temperatures, high quality, high energy utilization and lower pollution [12,13,14,15,16]. Liu et al. [17] studied the effect of SMR operation parameters on the recovery of iron from red mud in a laboratory, and it was found that a good indicator with iron recovery of 88.45% and iron grade of 56.41% was acquired under the optimized conditions of 540 °C roasting temperature, 15 min reduction time, 500 mL/min gas flow rate and 30% CO concentration. Moreover, the feasibility of the SMR technique for the extraction of iron from red mud was further verified by the semi-industrial scale test [18]. Even though these investigations have proposed and proved the advantages of the SMR technique for the recycling of red mud, the reduction mechanism, including kinetics, phase transformation and structure evolution, is still unclear. Particularly, the influence of alkali content on the reduction of red mud is not reported, which is a key factor to limit the recycling of the resource. The compositions of red mud are very complex, containing a variety of minerals [19]. According to the different compositions, red mud can be divided into different types. Regardless of types, however, the major mineral of red mud is hematite, and it is also the most useful mineral that is worth being recycled from the red mud. Therefore, the investigation of the influence of alkali content on the hematite can reflect the common problems within red mud reduction. In order to make the study more universal for all of the red mud resources, it is very meaningful to investigate the effects of NaOH content on the reduction of hematite.
In this paper, the effects of alkali content on the reduction kinetics of hematite were studied systematically by using SMR technology. In addition, the influence mechanism of alkali content on the reduction of hematite were uncovered by vibrating sample magnetometer (VSM), X-ray diffraction (XRD) and scanning electron microscopy (SEM).

2. Materials and Methods

2.1. Materials

The sample of pure hematite was obtained from Liaoning Province, China. The obtained sample was first picked by hand to remove a small amount of gangue minerals associated with hematite, and then the sample was crushed and ground to −0.5 mm. After that, the sample particles with different size fractions of −0.5 + 0.15 mm, −0.15 + 0.074 mm, −0.074 + 0.045 mm and −0.045 mm were acquired through wet-sieving. In order to simulate the reduction process of red mud ore, the size composition of the sample used in the reduction experiments consisted of −0.5 + 0.15 mm (13.68%), −0.15 + 0.074 mm (16.87%), −0.074 + 0.045 mm (22.69%) and −0.045 mm (46.76%). The chemical composition analyses and X-ray diffraction (XRD) detection were conducted to determine the purity of the sample [20,21,22], and the results are presented in Figure 1 and Table 1, respectively. From the results, it can easily be found that the purity of the hematite sample was 98.21%, which can meet the test requirements very well.

2.2. Methods

2.2.1. Experimental Apparatus and Procedure

The reduction experiments were performed in a vertical suspension furnace (OFT-1200X-S-VT, HFKJ, Hefei, China), and the schematic diagram of the experimental equipment is presented in Figure 2. For each experiment, 5 g hematite sample was first heated in the reaction tube to a desired temperature under a nitrogen flow of 100 mL/min. The heating speed was set as 15 °C/min. Once it reached the required temperature, the reducing gas mixture of 20 mL/min CO and 80 mL/min N2 was introduced into the reaction tube, and the reduction process began. After reducing for a period of time, the pure nitrogen flow of 100 mL/min was introduced again to remove the remaining reducing gas in the reaction tube, and the reduction products were then cooled down to room temperature under the nitrogen conditions. Each set of tests was conducted three times, and the average was adopted as the reported result.

2.2.2. Sample Characterization

In order to calculate the conversion of the reduction reaction, chemical analysis was adopted to determine the FeO content of reduction products. The detailed detection process was in accordance with our previous study [23]. X-ray diffraction detection (PW3040, Philips Co., The Netherlands) was used to characterize the phase transformation of the reduction products. VSM (JDAW-2000D) and SEM-EDS (JEM-3200FS) were adopted to analyze the changes in the mineral magnetism and microstructure of reduction products during the reduction process, respectively.

2.2.3. Dynamic Analysis Method

For hematite sample, the major reaction in the suspended reduction processing is the transformation of hematite to magnetite [24] (Equation (1)). The results from the chemical analysis indicate that the purity of the hematite sample is 98.21%; thus, 5 g experiment sample contains 4.91 g hematite. According to the law of conservation of mass, the iron metal equilibrium is listed as Equation (2) to (4).
3 F e 2 O 3 ( s ) + C O ( g ) = 2 F e 3 O 4 ( s ) + C O 2 ( g )
m F e 3 O 4 = 4.75 α
m F e O = 72 232 m F e 3 O 4 = 1.47 α
ω F e O = m F e O m F e 3 O 4 + m F e 2 O 3 + 0.09 = 1.47 α 5 0.16 α
where α refers the conversion of the reduction reaction, m F e 3 O 4 presents the weight of the new producing of Fe3O4 in the sample (g), ω F e O is the mass fraction of FeO in the sample (%), m F e O is the weight of FeO in the sample (g), and m F e 2 O 3 is the weight of Fe2O3 in the sample (g).
Based on Equation (4), the relation between α and ω F e O can also be described as Equation (5). Therefore, α can be calculated based on the FeO analysis results.
α = 5 ω F eO 1.47 + 0.16 ω F eO
The reaction rate is measured by the change in conversion of the reduction reaction per unit time; thus, the reaction rate of the suspension reduction can be obtained through the conversion of the reduction reaction (α) and reaction time, and the kinetics equation of the isothermal dynamics also can be determined (Equation (6)) [25,26]. Moreover, the most probable mechanism function can be determined by the analysis of the linear correlation between the fitting line and the experimental data.
v = d α d t = k ( T ) f ( α )
where v is the reaction rate (s−1), t is the reaction time (s), T is the temperature of the reaction (K) and k is the reaction rate constant, and it can be characterized by Arrhenius equation as [27,28]:
k ( T ) = A exp ( E α R T )
Herein, A is the pre-exponential factor (s−1), E α is the apparent activation energy (J/mol) and R is the gas constant (8.314 J/(mol·K)).
ln k = ln A E α R T
By taking the log of Equation (7), the formula transforms to Equation (8). From Equation (8), it can be seen that ln k is linearly related to 1 T . Therefore, after carrying on the linear data fitting to the experimental findings, E α and A can be obtained from the slope and intercept, respectively [27,28].

3. Results and Discussion

3.1. Influence of the NaOH Content on the Conversion Fractions of Hematite

Figure 3 shows the conversion degree of hematite versus reaction time under different reaction conditions. As shown in Figure 3, for a same amount of NaOH, the conversion degree and reduction rate of hematite increased with the increase in reduction temperature, which indicates that the increase in reduction temperature improved the activity of the reactants and promoted the reaction. On the other hand, the conversion degree of hematite decreased with the increasing amount of NaOH, and the reduction process of hematite was significantly prolonged with the increasing addition of NaOH at a constant reduction temperature. These results indicate that the addition of NaOH could strongly hinder the conversion of hematite and thereby reduce its reduction. Moreover, it also could be found that the inhibition effects of NaOH on the reduction of hematite were more distinct in low-temperature conditions. For a deeper understanding of the effect of NaOH on the conversion of hematite during the suspension reduction process, the reduction products treated with different NaOH content were analyzed by XRD and VSM; the results are shown in Figure 4 and Figure 5, respectively. As shown in Figure 4, the intensity of the magnetite diffraction peaks gradually decreased with the increase in NaOH content, while those of hematite continuously increased in intensity. These results confirmed that the conversion of hematite to magnetite was strongly inhibited by NaOH. A similar conclusion also could be drawn from Figure 5: with the increase in NaOH content, the magnetization and specific magnetic susceptibility of reduction products decreased, which would cause more hematite loss in the magnetic separation tailings.

3.2. Influence of NaOH Content on the Reduction Kinetics of Hematite

The results show in Section 3.1 illustrated that the addition of NaOH not only affected the conversion degree of hematite, but also influenced the reduction process of it. Reduction kinetics have been considered one of the most efficient ways to evaluate the reduction process, and it is very meaningful for the application of reduction kinetics to analyze the reduction behavior of the mineral and thereby to understand and optimize the reduction process. In this study, thirty common reduction kinetic models (Table 2) were used to fit and determine the most probable reduction mechanism model of hematite under different conditions [23].
By comparing the linear coefficient between the experimental data and the fitting line, the most probable reaction model for the reduction of hematite at different additions of NaOH has been determined and the results are depicted in Figure 6 and Table 3. As shown in Table 3, the reduction processes of hematite with and without addition of NaOH were met well with the A3 reaction models of the nucleation model, and the control step of hematite reduction was not affected by the addition of NaOH. Meanwhile, it could also be seen that the reaction rate increased with the increase in temperature at a constant of NaOH content, which further confirmed that the increase in temperature facilitated and accelerated the reduction of hematite. However, for a similar temperature, the increasing addition of NaOH content would obviously inhibit the reduction of hematite, and the reaction rate of hematite significantly decreased, especially in low-temperature conditions.
In order to better understand the influence of NaOH on the reduction of hematite, the apparent activation energy (Eα) and the pre-exponential factor (A) were also calculated by Equations (7) and (8), and the results are summarized as Figure 7. As shown in Figure 7, the apparent activation energy of the hematite reduction increased significantly after the addition of NaOH, which indicated that the reaction energy barrier for the reduction of hematite was improved by the addition of NaOH, and thus made it more difficult. Furthermore, the increase in the pre-exponential factor also demonstrated that the collision efficiency of the reactants was reduced and the reduction rate was decreased after the addition of NaOH.

3.3. Inhibited Reduction Mechanism Analysis

The above experiments and analyses demonstrated that the conversion of hematite to magnetite could be significantly inhibited by the addition of NaOH during the suspension reduction process, while the essential inhibition mechanism of NaOH on the reduction of hematite was still unclear. Herein, thermodynamic analysis and SEM-EDS detections were conducted to reveal this essential mechanism, the results are shown in Table 4, Figure 8 and Figure 9. The thermodynamic date was calculated via the FactSage software. Figure 8 shows the relationship between the Gibbs free energy and temperature of the possible reaction equations in the process of suspension reduction. As shown in Figure 8, the ∆G of Equation (13) was less than zero, which indicates that sodium ferrite could be produced spontaneously in the experimental conditions. However, it was hard for the produced sodium ferrite to be reduced by CO because the ∆G of Equation (14) was much more than zero. Meanwhile, from Figure 9, it could be seen that the element of Na was evenly distributed in the hematite surface and it also coexisted with Fe closely, which further proved that sodium ferrite occurred during the suspension reduction process after the addition of NaOH. Moreover, Figure 9 also shows that the dense film of sodium ferrite was presented in the surface of hematite, which would inhibit the diffusion of CO and further hinder the reduction of hematite in the interior.

4. Conclusions

In this study, the influence of NaOH content on the reduction kinetics of hematite was investigated systematically through the suspension magnetization roasting technique at the optimum reduction temperature (560 °C). The present research demonstrates that the conversion of hematite to magnetite was strongly inhibited by the addition of NaOH, and the magnetization and specific magnetic susceptibility of the reduction products was significantly decreased with the increase in NaOH content. Even the control step of the reduction of hematite was not affected by the addition of NaOH; its reduction rate was dramatically decreased by the addition of NaOH. Meanwhile, the apparent activation energy and the pre-exponential factor of the hematite reduction increased significantly from 26.745 kJ/mol to 83.482 kJ/mol and 3.658 min−1 to 6987.443 min−1, respectively, after the addition of NaOH from 0% to 2%. Thermodynamic analysis indicated that sodium ferrite could be produced spontaneously under the experimental conditions, and it is hard for it to be further reduced by CO. The SEM-EDS results confirm that the produced sodium ferrite formed a dense film, which covered the surface of hematite particle, and it not only decreased the conversion degree of hematite, but also inhibited the diffusion of CO and thereby hindered the reduction of hematite in the interior.

Author Contributions

Conceptualization, S.Y. and X.W.; methodology, S.Y.; software, X.L.; validation, S.Y., X.W. and Y.L.; formal analysis, H.Z.; investigation, H.Z.; resources, S.Y.; data curation, H.Z.; writing—original draft preparation, X.W.; writing—review and editing, X.W.; visualization, S.Y.; supervision, Y.L.; project administration, X.L.; funding acquisition, S.Y. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by [National Natural Science Foundation of China] grant number [52174240; 51904058] and [National Key Research and Development Program of China] grant number [Nos. 2018YFC1901902].

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Lyu, F.; Hu, Y.; Wang, L.; Sun, W. Dealkalization processes of bauxite residue: A comprehensive review. J. Hazard. Mater. 2021, 403, 123671. [Google Scholar] [CrossRef] [PubMed]
  2. Archambo, M.; Kawatra, S.K. Red mud: Fundamentals and new avenues for utilization. Miner. Process. Extr. Metall. Rev. 2020, 42, 427–450. [Google Scholar] [CrossRef]
  3. Yang, Y.; Guo, Y.-Q.; Zhu, W.-S.; Huang, J.-B. Environmental impact assessment of China’s primary aluminum based on life cycle assessment. Trans. Nonferrous Met. Soc. China 2019, 29, 1784–1792. [Google Scholar] [CrossRef]
  4. Lu, G.-Z.; Zhang, T.-A.; Ma, L.-N.; Wang, Y.-X.; Zhang, W.-G.; Zhang, Z.-M.; Wang, L. Utilization of Bayer red mud by a calcification–carbonation method using calcium aluminate hydrate as a calcium source. Hydrometallurgy 2019, 188, 248–255. [Google Scholar] [CrossRef]
  5. Milačič, R.; Zuliani, T.; Ščančar, J. Environmental impact of toxic elements in red mud studied by fractionation and speciation procedures. Sci. Total Environ. 2012, 426, 359–365. [Google Scholar] [CrossRef]
  6. Alam, S.; Das, S.K.; Rao, B.H. Characterization of coarse fraction of red mud as a civil engineering construction material. J. Clean. Prod. 2017, 168, 679–691. [Google Scholar] [CrossRef]
  7. Arroyo, F.; Luna-Galiano, Y.; Leiva, C.; Vilches, L.F.; Fernández-Pereira, C. Environmental risks and mechanical evaluation of recycling red mud in bricks. Environ. Res. 2020, 186, 109537. [Google Scholar] [CrossRef]
  8. Liu, X.; Han, Y.; He, F.; Gao, P.; Yuan, S. Characteristic, hazard and iron recovery technology of red mud—A critical review. J. Hazard. Mater. 2021, 420, 126542. [Google Scholar] [CrossRef]
  9. Khairul, M.A.; Zanganeh, J.; Moghtaderi, B. The composition, recycling and utilisation of Bayer red mud. Resour. Conserv. Recycl. 2019, 141, 483–498. [Google Scholar] [CrossRef]
  10. Liu, Y.; Naidu, R. Hidden values in bauxite residue (red mud): Recovery of metals. Waste Manag. 2014, 34, 2662–2673. [Google Scholar] [CrossRef]
  11. Yuan, S.; Zhou, W.; Han, Y.; Li, Y. Efficient enrichment of low-grade refractory rhodochrosite by preconcentration-neutral suspension roasting-magnetic separation process. Powder Technol. 2020, 361, 529–539. [Google Scholar] [CrossRef]
  12. Tang, Z.; Zhang, Q.; Sun, Y.; Gao, P.; Han, Y. Pilot-scale extraction of iron from flotation tailings via suspension magnetization roasting in a mixture of CO and H2 followed by magnetic separation. Resour. Conserv. Recycl. 2021, 172, 105680. [Google Scholar] [CrossRef]
  13. Zhang, Q.; Sun, Y.; Han, Y.; Li, Y. Pyrolysis behavior of a green and clean reductant for suspension magnetization roasting. J. Clean. Prod. 2020, 268, 122173. [Google Scholar] [CrossRef]
  14. Tang, Z.; Liu, X.; Gao, P.; Han, Y.; Xu, B. Effective induction of magnetite on suspension magnetization roasting of hematite and reaction kinetics verification. Adv. Powder Technol. 2022, 33, 103593. [Google Scholar] [CrossRef]
  15. Tang, Z.; Xiao, H.; Sun, Y.; Gao, P.; Zhang, Y. Exploration of hydrogen-based suspension magnetization roasting for refractory iron ore towards a carbon-neutral future: A pilot-scale study. Int. J. Hydrogen Energy 2022, 47, 15074–15083. [Google Scholar] [CrossRef]
  16. Liu, X.; Gao, P.; Yuan, S.; Lv, Y.; Han, Y. Clean utilization of high-iron red mud by suspension magnetization roasting. Miner. Eng. 2020, 157, 106553. [Google Scholar] [CrossRef]
  17. Yuan, S.; Liu, X.; Gao, P.; Han, Y. A semi-industrial experiment of suspension magnetization roasting technology for separation of iron minerals from red mud. J. Hazard. Mater. 2020, 394, 122579. [Google Scholar] [CrossRef]
  18. Zinoveev, D.; Grudinsky, P.; Zakunov, A.; Semenov, A.; Panova, M.; Valeev, D.; Kondratiev, A.; Dyubanov, V.; Petelin, A. Influence of Na2CO3 and K2CO3 Addition on Iron Grain Growth during Carbothermic Reduction of Red Mud. Metals 2019, 9, 1313. [Google Scholar] [CrossRef]
  19. Xie, R.; Zhu, Y.; Liu, J.; Wang, X.; Li, Y. Differential collecting performance of a new complex of decyloxy-propyl-amine and α-bromododecanoic acid on flotation of spodumene and feldspar. Miner. Eng. 2020, 153, 106377. [Google Scholar] [CrossRef]
  20. Wang, X.; Gao, P.; Liu, J.; Gu, X.; Han, Y. Adsorption performance and mechanism of eco-friendly and efficient depressant galactomannan in flotation separation of chalcopyrite and molybdenite. J. Mol. Liq. 2021, 326, 115257. [Google Scholar] [CrossRef]
  21. Liu, J.; Xie, R.; Zhu, Y.; Li, Y.; Liu, C. Flotation behavior and mechanism of styrene phosphonic acid as collector on the flotation separation of fluorite from calcite. J. Mol. Liq. 2021, 326, 115261. [Google Scholar] [CrossRef]
  22. Yuan, S.; Zhang, Q.; Yin, H.; Li, Y. Efficient iron recovery from iron tailings using advanced suspension reduction technology: A study of reaction kinetics, phase transformation, and structure evolution. J. Hazard. Mater. 2021, 404, 124067. [Google Scholar] [CrossRef] [PubMed]
  23. Chen, J.; Zhang, R.; Simmonds, T.; Hayes, P.C. Microstructural Changes and Kinetics of Reduction of Hematite to Magnetite in CO/CO2 Gas Atmospheres. Metall. Mater. Trans. B 2019, 50, 2612–2622. [Google Scholar] [CrossRef]
  24. Chithiraputhiran, S.; Neithalath, N. Isothermal reaction kinetics and temperature dependence of alkali activation of slag, fly ash and their blends. Constr. Build. Mater. 2013, 45, 233–242. [Google Scholar] [CrossRef]
  25. Mozammel, M.; Sadrnezhaad, S.K.; Khoshnevisan, A.; Youzbashizadeh, H. Kinetics and reaction mechanism of isothermal oxidation of Iranian ilmenite concentrate powder. J. Therm. Anal. Calorim. 2013, 112, 781–789. [Google Scholar] [CrossRef]
  26. Gong, D.; Zhou, K.; Li, J.; Peng, C.; Chen, W. Kinetics of Roasting Reaction Between Synthetic Scheelite and Magnesium Chloride. JOM 2019, 71, 2827–2833. [Google Scholar] [CrossRef]
  27. Fiúza, A.; Silva, A.; Carvalho, G.; de la Fuente, A.V.; Delerue-Matos, C. Heterogeneous kinetics of the reduction of chromium (VI) by elemental iron. J. Hazard. Mater. 2010, 175, 1042–1047. [Google Scholar] [CrossRef] [Green Version]
  28. Xiang, J.; Huang, Q.; Lv, W.; Lv, X.; Bai, C. Effects of Pre-Oxidation on the Kinetics of Iron Leaching from Ilmenite in Hydro-chloric Acid Solution. In Rare Metal Technology 2018; Kim, H., Wesstrom, B., Alam, S., Ouchi, T., Azimi, G., Neelameggham, N.R., Wang, S., Guan, X., Eds.; Springer International Publishing: Cham, Switzerland, 2018; pp. 301–307. [Google Scholar]
Figure 1. X-ray diffraction pattern of hematite.
Figure 1. X-ray diffraction pattern of hematite.
Minerals 12 01107 g001
Figure 2. The schematic diagram of the experiment equipment.
Figure 2. The schematic diagram of the experiment equipment.
Minerals 12 01107 g002
Figure 3. Conversion degrees of hematite under different conditions ((a) 0% NaOH, (b) 1% NaOH, (c) 2% NaOH).
Figure 3. Conversion degrees of hematite under different conditions ((a) 0% NaOH, (b) 1% NaOH, (c) 2% NaOH).
Minerals 12 01107 g003
Figure 4. XRD patterns of reduction products with different NaOH content at 560 °C.
Figure 4. XRD patterns of reduction products with different NaOH content at 560 °C.
Minerals 12 01107 g004
Figure 5. Magnetic intensity (a) and magnetic susceptibility (b) of reduction products with different NaOH contents at 560 °C.
Figure 5. Magnetic intensity (a) and magnetic susceptibility (b) of reduction products with different NaOH contents at 560 °C.
Minerals 12 01107 g005
Figure 6. Linear regression analysis curves between mechanism function G(α) of A3 model and experimental data ((a) 0% NaOH, (b) 1% NaOH, (c) 2% NaOH).
Figure 6. Linear regression analysis curves between mechanism function G(α) of A3 model and experimental data ((a) 0% NaOH, (b) 1% NaOH, (c) 2% NaOH).
Minerals 12 01107 g006
Figure 7. Arrhenius plot for the evaluation of the activation energy of the process (a) 0% NaOH, (b) 1% NaOH, (c) 2% NaOH.
Figure 7. Arrhenius plot for the evaluation of the activation energy of the process (a) 0% NaOH, (b) 1% NaOH, (c) 2% NaOH.
Minerals 12 01107 g007aMinerals 12 01107 g007b
Figure 8. Thermodynamic analysis of suspension reduction of hematite after addition of NaOH.
Figure 8. Thermodynamic analysis of suspension reduction of hematite after addition of NaOH.
Minerals 12 01107 g008
Figure 9. SEM images and EDS element map of the reduction product (2.0% NaOH).
Figure 9. SEM images and EDS element map of the reduction product (2.0% NaOH).
Minerals 12 01107 g009
Table 1. Chemical composition of hematite sample (mass, %).
Table 1. Chemical composition of hematite sample (mass, %).
CompositionTFeFeOSiO2Al2O3CaOMgOPS
Content68.750.450.480.0810.280.220.0250.004
Table 2. Description of the thirty kinetic models used in this study.
Table 2. Description of the thirty kinetic models used in this study.
Mechanism Functionsf(α)G(α)
Nucleation modelA11 − α−ln(1 − α)
A22(1 − α)[−ln(1 − α)]1/2[−ln(1 − α)]1/2
A33(1 − α)[−ln(1 − α)]2/3[−ln(1 − α)]1/3
A44(1 − α)[−ln(1 − α)]3/4[−ln(1 − α)]1/4
A3/23/2(1 − α)[−ln(1 − α)]1/3[−ln(1 − α)]2/3
A1/41/4(1 − α)[−ln(1 − α)]−3[−ln(1 − α)]4
A1/31/3(1 − α)[−ln(1 − α)]−2[−ln(1 − α)]3
A1/21/2(1 − α)[−ln(1 − α)]−1[−ln(1 − α)]2
Geometrical contraction modelsR1/21/2(1 − α)−11 − (1 − α)2
R1/31/3(1 − α)−21 − (1 − α)3
R1/41/4(1 − α)−31 − (1 − α)4
R22(1 − α)1/21 − (1 − α)1/2
R33(1 − α)2/31 − (1 − α)1/3
R44(1 − α)3/41 − (1 − α)1/4
Diffusion modelsD11/2α−1α2
D2[−ln(1 − α)]−1A + (1 − α)ln(1 − α)
D3(1 − α)1/2[1 − (1 − α)1/2] −1[1 − (1 − α)]1/2]2
D43/2(1+α)2/3[(1+α)1/3 − 1] −1[(1+α)]1/3 − 1]2
D53/2(1 − α)4/3[(1 − α)−1/3 − 1] −1[(1 − α)]−1/3 − 1]2
D63/2(1 − α)2/3[1 − (1 − α)−1/3]−1[1 − (1 − α)]1/3]2
D76(1 − α)2/3[1 − (1 − α)−1/3]1/2[1 − (1 − α)]1/3]1/2
D83/2[(1 − α)−1/3 − 1] − 11 − 2/3α − (1 − α)2/3
Power lawsP43/4α1/4
P32/3α1/3
P21/2α1/2
P11α
P3/22/3α−1/2α3/2
Reaction-order modelsF11 − α−ln(1 − α)
F2(1 − α)2(1 − α)−1 − 1
F31/2(1 − α)3(1 − α)−2
Table 3. Reaction rate constant and linear correlation coefficient of reduction at different temperatures.
Table 3. Reaction rate constant and linear correlation coefficient of reduction at different temperatures.
NaOH AdditiveG(α)Temperature (k)1/TReaction Rate (k/min−1)lnkR2
0%G(α) = [−ln(1 − α)]1/37930.0009380.06435−2.743420.99834
8330.0009040.07337−2.612240.99359
8730.0008730.09599−2.343510.99597
9130.0008430.10640−2.240550.99541
1%G(α) = [−ln(1 − α)]1/37930.0009380.02330−3.75930.98532
8330.0009040.04508−3.099320.98583
8730.0008730.08082−2.515530.98907
9130.0008430.10429−2.169020.98568
2%G(α) = [−ln(1 − α)]1/37930.0009380.02052−3.886360.98552
8330.0009040.04275−3.152390.99224
8730.0008730.08178−2.503720.99611
9130.0008430.10369−2.266350.97408
Table 4. Thermodynamic equations of suspension reduction of hematite after addition of NaOH.
Table 4. Thermodynamic equations of suspension reduction of hematite after addition of NaOH.
NumberEquation
(9)3Fe2O3(s) + CO(g) = 2Fe3O4(s) + CO2(g)
(10)Fe3O4(s) + CO(g) = 3FeO(s) + CO2(g)
(11)Fe3O4(s) + 4CO(g) = 3Fe(s) + 4CO2(g)
(12)FeO(s) + CO(g) = Fe(s) + CO2(g)
(13)2NaOH(s) + Fe2O3(s) = Na2O·Fe2O3(s) + H2O(g)
(14)3Na2O·Fe2O3(s) + CO(g) = 2Fe3O4(s) + 3Na2O(s) + CO2(g)
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Yuan, S.; Li, X.; Wang, X.; Zhang, H.; Li, Y. Effects of NaOH Content on the Reduction Kinetics of Hematite by Using Suspension Magnetization Roasting Technology. Minerals 2022, 12, 1107. https://doi.org/10.3390/min12091107

AMA Style

Yuan S, Li X, Wang X, Zhang H, Li Y. Effects of NaOH Content on the Reduction Kinetics of Hematite by Using Suspension Magnetization Roasting Technology. Minerals. 2022; 12(9):1107. https://doi.org/10.3390/min12091107

Chicago/Turabian Style

Yuan, Shuai, Xinyu Li, Xun Wang, Hao Zhang, and Yanjun Li. 2022. "Effects of NaOH Content on the Reduction Kinetics of Hematite by Using Suspension Magnetization Roasting Technology" Minerals 12, no. 9: 1107. https://doi.org/10.3390/min12091107

APA Style

Yuan, S., Li, X., Wang, X., Zhang, H., & Li, Y. (2022). Effects of NaOH Content on the Reduction Kinetics of Hematite by Using Suspension Magnetization Roasting Technology. Minerals, 12(9), 1107. https://doi.org/10.3390/min12091107

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop