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Article

Tin Removal from Tin-Bearing Iron Concentrate with a Roasting in an Atmosphere of SO2 and CO

1
Faculty of Metallurgical and Energy Engineering, Kunming University of Science and Technology, Kunming 650093, China
2
College of Environmental Science and Engineering, Donghua University, Shanghai 201620, China
*
Author to whom correspondence should be addressed.
Metals 2022, 12(11), 1974; https://doi.org/10.3390/met12111974
Submission received: 12 October 2022 / Revised: 11 November 2022 / Accepted: 15 November 2022 / Published: 18 November 2022
(This article belongs to the Special Issue Metal Recovery and Separation from Wastes)

Abstract

:
The tin could be volatilized and removed effectively from the tin-bearing iron concentrate while roasted in an atmosphere of SO2 and CO. The reduction of SO2 by CO occurred in preference to the SnO2 and Fe3O4, and the generated S2 could sulfurize the SnO2 to an evaporable SnS, which resulted in the tin volatilization. However, the Fe3O4 could be sulfurized simultaneously, and a phase of iron sulfide was formed, retaining in the roasted iron concentrate. It decreased the quality of the iron concentrate. In addition, the formation of Sn-Fe alloy was accelerated as the roasting temperature exceeded 1100 °C, which decreased the Sn removal ratio. An appropriate SO2 partial pressure and roasting temperature should be controlled. Under the condition of the roasting temperature of 1050 °C, SO2 partial pressure of 0.003, CO partial pressure of 0.85, and residence time of 60 min, the tin content in the roasted iron concentrate was decreased to 0.032 wt.% and the sulfur residual content was only 0.062 wt.%, which meets the standard of iron concentrate for BF ironmaking.

1. Introduction

The Sn-bearing iron ore is a typically complex iron ore resource, with the reserve exceeding 0.5 billion tons in China [1,2,3]. After it is treated by traditional mineral processing technology, a Sn-bearing iron concentrate could be obtained. However, this concentrate cannot be used as a raw material for ironmaking due to the overly high tin content in it (0.3–0.8 wt %) [4]. This content exceeds the content standard of tin in the iron concentrate (<0.08 wt.%) [3,4]. To use it as a resource, much research has been carried out to remove tin from the Sn-bearing iron concentrate. Because most of the Sn phases are embedded in the iron phase at a fine-grained size, the tin could not be removed effectively through mineral processing methods [4,5]. Considering the difference between the volatility of SnO, SnS, and other phases in the Sn-bearing iron concentrate, a reduction or sulfurization roasting process has been used to remove tin from this iron concentrate [4,5,6,7,8,9]. An Fe-Sn spinel or Fe-Sn alloy was easily formed in a reduction roasting process, causing the tin removal rate to be only 80%, as reported in previous research [9,10]. By a sulfurization roasting process, the tin removal rate reached over 90% with FeS2 [4], high-sulfur coal [6], waste tire rubber [5], or CaSO4 [11] used as curing agents. The sulfurization roasting process might be suitable for treating the Sn-bearing iron concentrate.
In the phosphate rock processing, fuel and coal combustion, and non-ferrous and ferrous metals smelting [12,13,14], massive SO2-containing gas was generated and would cause a serious pollution with an emission into the air. The treatment of SO2 gas has received increasing attention worldwide. Processes, including the wet method [15,16], semi-dry method [17,18], dry method [19,20], and activated carbon adsorptive method [21,22], have been used to remove SO2 from the flue gas. Among them, the CaCO3/CaO-CaSO4 wet method was mainly used in which the CaCO3/CaO was firstly ground into powder, then fully mixed with water and stirred to form slurry, and at last passed into the absorption tower together with air [16]. A high desulfurization efficiency could be obtained in this wet method; however, the generated waste gypsum residue leads a secondary pollution [15,23]. A wide variety technology is required to recycle SO2 from flue gases, especially for the gas containing low concentration SO2.
The SO2 could be reduced to elemental S2 by CO, which could then sulfurize SnO2 to SnS at a proper temperature [4,6,8]. Considering this, we proposed an innovative approach to remove Sn from the Sn-bearing iron concentrate using the SO2 as the curing agent in a reducing atmosphere (CO) in this research. This research supplied a new thought for treating and reusing the low concentration SO2 off-gas. Thermodynamic analysis and laboratory tests were carried out to study the feasibility of this approach. Furthermore, the reaction mechanism was elucidated through X-ray diffraction (XRD) and scanning electron microscopy coupled with energy dispersive spectrometry (SEM-EDS).

2. Materials and Methods

2.1. Materials

The tin-bearing iron concentrate used in this study was collected from an ironmaking plant in Yunnan province of China. The element analysis result shows that it contains 65.52 wt. % Fe and 0.39 wt.% Sn (Table 1). A pre-removal of Sn should be carried out before it used as an ironmaking raw material. Figure 1a shows that the main phase in this iron concentrate is Fe3O4, and the Sn-containing phase of cassiterite (SnO2) is embedded in this Fe3O4 phase as demonstrated in the electron probe microanalysis techniques (EPMA) analysis result (Figure 1b).
The N2 with purity of 99.99 vol.%, CO with purity of 99.99 vol.%, and mixed gas of 2 vol.% SO2+ 98 vol.% N2 used in this research, were supplied by the local suppliers.

2.2. Methods

The experiments were carried out in a horizontal tube furnace (GSL-1500X, Hefei Kejing Materials Technology Co. Ltd., Hefei, China), as shown in Figure 2, the temperature of which was measured by a KSY intelligent temperature controller connected to a Pt-Rh thermocouple. For the experimental procedure, the tin-bearing iron concentrate was firstly grounded to minus 0.075 mm, placed in a crucible, transferred to the horizontal tube furnace, and heated to a proper temperature under a high-purity N2 atmosphere with a flow rate of 40 mL/min. According to previous studies, the surface area of solid particles increased as the particle size decreased, which was beneficial to improving the gas-solid reaction area. The tin-bearing iron concentrate with particle size of 0.075μm was selected for experiment [8]. After that, the high-purity N2 was changed into the mixed gas of (2 vol.% SO2 + 98 vol.% N2) and high-purity CO at a proper volume ratio with a total flow rate of 100 mL/min, and held for a certain time. After the roasting process completed and the residue cooled down to room temperature in a high-purity N2 atmosphere at a flow rate of 40 mL/min, the roasted residue was removed and prepared for analysis.

2.3. Characterization

Elemental composition of the samples was obtained by chemistry analytical method, all of the measurements were conducted three times and the average value was taken as the final result. The phase composition and distribution in the samples were characterized via an X-ray diffraction and EPMA techniques (JEOL, Kyoto, Japan). The XRD patterns were obtained using Cu-Kα radiation in a 2θ range of 10° to 80° with a scan step of 8°/min (Rigaku, Kyoto, Japan). In addition, FactSage 7.2 software (7.2, GTT-Technologies, Herzogenrath, Germany) was used to calculate the equilibrium phase composition during the roasting process.
Mathematical expression of the Sn volatilization ratio in this paper was defined as:
R= M 0 × W 0 -M r × W r M 0 × W 0 × 100 %
where M0 and Mr stand for the mass of original tin-bearing iron concentrate and roasted residue, respectively, and W0 and Wr for the Sn mass content in the original tin-bearing iron concentrate and roasted residue, respectively.

3. Thermodynamic Analysis

To investigate the effect of SO2 (g) on the Sn volatilization rate from the tin-bearing iron concentrate under CO-SO2 mixed atmosphere, 1 mol Fe3O4 and 1 mol SnO2 were selected as the reactants to calculate the equilibrium phase composition while roasted with 2 mol CO and different amounts of SO2 at 1100 °C using FactSage 7.2 software. Without the addition of SO2 (g), the results in Figure 3a show that CO2 (g), FeO, Fe2O3 and SnO appear, which was due to the occurrence of reactions (1)–(3). Though the decomposition of Fe3O4 is difficult to be carried out due to the positive value of the standard Gibbs free energy of reaction (2) at 1100 °C (Figure 3b), the occurrence of reaction (3) promoted this decomposition to happen, considering the chemical equilibrium. With the increase of the SO2 amount from 0 to 0.4 mol, the amounts of CO (g), FeO, SnO, and Fe2O3 decrease, and the amounts of CO2 (g), S2 (g), SnS (g), SnO2 and Fe3O4 increase. In Figure 3b, the Gibbs free energy for the reduction of SO2 (g) by CO (g) (reaction (4)) at 1100 °C is minimum, causing the CO (g) amount used to reduce SnO2, Fe2O3 to be decreased in the presence of SO2 (g) and the equilibrium amount of SnO2 and Fe3O4 increased. The CO (g) first reduces SO2 (g) to form S2 (g) by reaction (4), and then S2 (g) reacts with SnO (s) and SnO2 (s) through reactions (5) and (6) to form SnS (g). The SnS (g) increases in this range of SO2 (g) amount. With the SO2 (g) amount exceeding 0.6 mol, an excessive SO2 (g) exists in the equilibrium composition in Figure 3a. Consequently, the reduction of SnO2 and Fe2O3 was further restrained, as a result of which the formation of SnS (g) decreased and the decomposition of Fe3O4 occurred little.
Under the condition of the Fe3O4 amount of 1 mol, SnO2 amount of 1 mol, and SO2 amount of 1.5 mol, the effect of CO (g) amount on the Sn transformation was then calculated at 1100 °C. Figure 3c,d show that with the increase of CO amount from 0 to 5 mol, the amounts of SO2 (g) and SnO2 decrease accompanied with the increase of SnS (g) and S2 (g) amounts, which might be due to the occurrence of reactions (4) to (6). As the amount of CO increases over 4 mol, the amounts of Fe3O4 (s) and S2 (g) decrease while the amounts of FeO (l) and FeS (l) increase, probably due to the occurrence of reactions (4) and (7).
In summary, under the CO-SO2 mixed atmosphere, the SnO2 can be sulfurized and volatilized in the form of SnS (g) from the tin-bearing iron concentrate. However, some sulfur might retain in the roasted iron concentrate in form of FeS at a high CO amount, which decreases the iron concentrate quality for ironmaking. A suitable SO2 and CO partial pressures should be controlled during the roasting process.
CO(g) + SnO2(s) = SnO(s) + CO2(g)
Fe3O4(s) = Fe2O3(s) + FeO(s)
CO(g) + Fe2O3(s) = 2FeO(s)+ CO2(g)
4CO(g) + 2SO2(g) = S2(g) + 4CO2(g)
3S2(g) + 4SnO = 4SnS(g) + 2SO2(g)
4CO(g) + S2(g) + 2SnO2 = 2SnS(g) + 4CO2(g)
S2(g) + Fe3O4 = FeS(l) + SO2(g) + 2FeO(l)

4. Results and Discussion

4.1. Effects of the SO2 Partial Pressure

Under the condition of the roasting temperature of 1000 °C, residence time of 40 min, tin-bearing iron concentrate particle size below 0.075 mm, and total flow rate of mixed gases of (2 vol.% SO2+ 98 vol.% N2) and high-purity CO of 100 mL/min, the effects of SO2 partial pressure on the Sn volatilization ratio from the tin-bearing iron concentrate and S content in the roasted residue were focused firstly. The SO2 partial pressure (PSO2) was assumed as PSO2= VSO2/(VSO2+ VN2+ VCO), and the CO partial pressure (PCO) was assumed as PCO= VCO/(VSO2+ VN2+ VCO). The VSO2, VN2, and VCO corresponds to the volume fraction of SO2, N2, and CO in the mixed gas respectively.
Figure 4a shows the changes of CO partial pressure (PCO) with the increase of SO2 partial pressure (PSO2) in this research. Based on it, the Fe3O4 and SnO2 both could be sulfurized during the roasting process in this process, as presented the predominance area diagram of Fe-Sn-S-O at 1000 °C in Figure 4b. More S2 (g) could be produced from the reduction of SO2 (g) at a higher SO2 partial pressure (PSO2) through Equation (4), which in turn could sulfurize more cassiterite (SnO2) to SnS (g) by Equation (6). As a result, the Sn volatilization ratio increased from 60.1% to 72.4% with the PSO2 from 0.001 to 0.005 as presented in Figure 4c. Furthermore, according to Figure 3c,d, the Fe3O4 could be sulfurized accompanied with the sulfurization of SnO2 thermodynamically, causing the sulfur content in the roasted residue to increase with the increase of PSO2 as shown in Figure 4d. Figure 5a shows the phase compositions of the roasted residues under different SO2 partial pressures. It indicated that after the roasting treatment, the Fe3O4 in the raw Sn-bearing iron concentrate could be reduced into FeO at the PSO2 of 0.003 and further reduced to metallic Fe as the PSO2 decreased to 0.001. The CO partial pressure increased from 0.85 to 0.95 with the decrease of PSO2 from 0.003 to 0.001 (Figure 4a), which promoted the further reduction of FeO to Fe. The phase of iron sulfide could not be detected in the XRD patterns of the roasted residues due to its little content. Then, an SEM-EDS analysis on the roasted residue was carried out and the result is shown in Figure 5b. In Figure 5b, the element composition of point “1” is Fe and S, which confirmed the existence of iron sulfide in the roasted residue. To increase the Sn volatilization ratio and decrease the S content in the roasted iron concentrate, the SO2 partial pressure should be controlled at 0.003.

4.2. Effects of Roasting Temperature

Under the condition of the SO2 partial pressure of 0.003, residence time of 40 min, particle size of the tin-bearing iron concentrate below 0.075 mm, and total flow rate of mixed gases of (2 vol.% SO2+ 98 vol.% N2) and high-purity CO of 100 mL/min, the effects of roasting temperature on the Sn volatilization ratio from the tin-bearing iron concentrate and S content in the roasted residue were researched.
The sulfurization of SnO2 through Equations (4) and (6) was accelerated at higher temperatures, and the vapor pressure of SnS (g) also increased with the increase of temperature [24]. These resulted in an increased the Sn volatilization ratio from 27.0% to 80.6% with the roasting temperature from 900 °C to 1050 °C seen in Figure 6a. However, with the roasting temperature further increased to 1100 °C, the Sn volatilization ratio decreased to 74.8%. This might be due to more generation of Fe-Sn alloy at 1100 °C, which limited the tin sulfurization and volatilization [9,10]. Comparing Figure 7a to Figure 7b, a metallic Fe phase could be detected in the roasted residue as the temperature increased from 1050 °C to 1100 °C, indicating a deeper reduction of Fe3O4 could be carried out and as a result more metallic Fe would be produced at a higher temperature. The generated metallic Fe might be combined with the reduced Sn to form an Fe-Sn alloy through Equation (8) [5], and more importantly the Fe content in the generated Fe-Sn alloy increased with the increase of the roasting temperature as presented in Figure 7c,d. Comparing Figure 7c to Figure 7d, the Sn content in the formed Sn-Fe alloy decreased from 97.01 wt% to 1.13 wt% as the roasting temperature increased from 900 °C to 1100 °C. The Sn activity in the Fe-Sn alloy decreased with the decrease of Sn content in it according to Raoult’s law, causing the Sn sulfurization from the Fe-Sn alloy by Equation (9) to be restricted. As a result, the Sn volatilization decreased to 74.8% at 1100 °C, as shown in Figure 6a.
[Fe] + [Sn] = Sn-Fe alloy
S2 + Sn-Fe alloy SnS + Fe
Similar to the sulfurization of SnO2 through Equations (4) and (6), the transfer of ‘S’ from SO2 to iron sulfide using Equation (7) was promoted with the increase of roasting temperature, causing the S content in the roasted residue increased with the temperature from 900 °C to 1000 °C (Figure 6b). However, as the temperature exceeded 1000 °C, the sulfur content in the roasted residue decreased. The reason might be that less S2 (g) would be generated at higher temperatures deduced from Figure 3b, which in turn led to less ‘S’ fixed in the roasted residue in form of iron sulfide. In Figure 3b, the Gibbs free energy for reaction (4) increased with the temperature increase. Based on the results in Figure 6a,b, the optimum roasting temperature should be 1050 °C in order to maximize the removal of tin from the tin-bearing iron concentrate and to ensure a low sulfur content in the roasted residue.

4.3. Effects of the Residence Time

Under the condition of roasting temperature of 1050 °C, SO2 partial pressure of 0.003, tin-bearing iron concentrate particle size below 0.075 mm and total flow rate of mixed gases of (2 vol.% SO2+ 98 vol.% N2) and high-purity CO of 100 mL/min, the effects of residence time on the Sn volatilization ratio from the tin-bearing iron concentrate and S content in the roasted residue are shown in Figure 8a,b respectively.
Based on Equations (4) and (6), the sulfurization reaction of Sn from the tin-bearing iron concentrate could be summarized as Equation (10) in this research. An unreacted core shrinking model was chosen to describe the sulfurization kinetics of SnO2. The reaction process could be divided into three main steps: outer diffusion of the CO and SO2 through the gas phase boundary layer to the reactant particle surface, internal diffusion of CO and SO2 through gaps in the reactant particle to the gas-solid reaction interface, and interfacial chemical reaction with the SnO2 at the reaction interface. Generally, the first step of the outer diffusion is not the rate controlling step when the gas flow exceeds 60 mL/min [25,26]. The sulfurization of SnO2 was likely controlled by the internal diffusion, interfacial chemical reaction, or the combination of them. As reported in previous research [27,28,29], the kinetic equations controlled by different reaction steps could be summarized in Table 2. In Table 2, the t was the reduction time, min; the X was the Sn volatilized ratio, %; and the a, b, a1, and b1 were constants. With the 1 1     X 1 / 3 used as Y-axis and t used as X-axis, the reaction would be controlled by the interfacial chemical reaction if there is a linear relationship between X and Y. Similarly, if there is a linear relationship between the 1 2 X / 3 1   X 2 / 3   (Y-axis) and t (X-axis), the reaction would be controlled by the gas internal diffusion control; if there is a linear relationship between the 1 + 1 X 1 / 3 2 1 X 2 / 3 (Y-axis) and t / 1 1 X 1 / 3 (X-axis), the reaction would be controlled by the combination of the internal diffusion and interfacial chemical reaction.
4CO(g) + SO2(g) + SnO2 = SnS + 4CO2(g)
The equations listed in Table 2 were used to treat the experimental data in Figure 8a, and the results are shown in Figure 9. In comparison with Figure 9a–c, a better linear dependence between the 1 2 X / 3 1   X 2 / 3   (Y-axis) and t (X-axis) could be seen with the residence time from 10 min to 60 min in Figure 9a. It indicated the reaction was controlled by the gas internal diffusion control. Consequently, as the residence time increased, the CO and SO2 gas concentration at the reaction interface gradually approached the CO and SO2 concentration in the main gas phase, causing more of the SnO2 to be sulfurized and volatilized. With the residence time prolonged from 20 min to 60 min, the Sn volatilization rate increased from 19.9% to 92.1%. While the residence time increased further; the Sn volatilization rate increased little. The trend in sulfur content in the roasted residue is similar with that of Sn volatilization ratio as presented in Figure 8a, which raised rapidly from 20 min to 60 min and then increased slowly as the residence time continued to increase. Considering the results in Figure 8a,b, the residence time was chosen at 60 min.
Under the condition of the roasting temperature of 1050 °C, SO2 partial pressure of 0.003, CO partial pressure of 0.85, and residence time of 60 min, the tin removal rate from the tin-bearing iron concentrate achieved 92.1% and the Sn content in the roasted iron concentrate was decreased to 0.032 wt.%. In addition, the sulfur content in the iron concentrate is only 0.062 wt.%, which meets the standard of BF ironmaking.

5. Conclusions

The tin from the tin-bearing iron concentrate could be efficiently removed using a roasting in the mixed atmosphere of CO and SO2 at 1050 °C. With the partial pressure of SO2 increased from 0.001 to 0.005, more S2 was produced from the reduction of SO2, which in turn promoted the sulfidation and SnO2 volatilization, resulting in the increased volatilization ratio of Sn from 60.1% to 72.4%. However, the Fe3O4 sulfidation also occurred simultaneously at a higher SO2 partial pressure and an iron sulfide phase was formed, retaining in the roasted iron concentrate, due to which the residual sulfur content increased. The Sn volatilization ratio increased from 27.0% to 80.6% with the increase of roasting temperature from 900 °C to 1050 °C, but it decreased to 74.8% as the roasting temperature was further increased to 1100 °C. It was due to the more formation of a Sn-Fe alloy. The kinetics study showed that the sulfurization of SnO2 from the concentrated tin-bearing iron was controlled by the internal gas diffusion reaction step. Under the condition of roasting temperature of 1050 °C, SO2 partial pressure of 0.003, CO partial pressure of 0.003, and residence time of 60 min, the Sn content in the roasted iron concentration was decreased to 0.032 wt%, and the residual sulfur content was only 0.062 wt%, which meets the BF ironmaking.

Author Contributions

L.L.: Conceptualization, funding acquisition, investigation, methodology, project administration, resources, supervision, writing—original draft, writing—review and editing. Z.X.: Data curation, investigation, validation, writing—original draft. S.W.: Methodology, investigation, validation, writing—original draft. All authors have read and agreed to the published version of the manuscript.

Funding

This study is supported by the National Natural Science Foundation of China (51874153).

Data Availability Statement

All data are available in this study.

Acknowledgments

The authors wish to express their thanks to the National Natural Science Foundation of China (51874153) for their financial support of this research.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. XRD pattern (a) and EPMA analysis (b) of the Sn-bearing iron concentrate.
Figure 1. XRD pattern (a) and EPMA analysis (b) of the Sn-bearing iron concentrate.
Metals 12 01974 g001
Figure 2. Schematic illustration of the experimental apparatus. (1-Mass flow meter; 2-Gas mixer; 3-Pressure gauge; 4-Filter; 5-Resistive heater; 6-Corundum reactor; 7-Temperature controller).
Figure 2. Schematic illustration of the experimental apparatus. (1-Mass flow meter; 2-Gas mixer; 3-Pressure gauge; 4-Filter; 5-Resistive heater; 6-Corundum reactor; 7-Temperature controller).
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Figure 3. (a) Equilibrium phase composition of 2 mol CO+ 1 mol Fe3O4 + 1 mol SnO2 roasted with different amounts of SO2 at 1100 °C; (b) Gibbs free energy changes for reaction (1)–(5) at 500–1100 °C; (c,d) Equilibrium phase composition of 1.5 mol SO2+ 1 mol Fe3O4 + 1 mol SnO2 roasted with different amounts of CO at 1100 °C.
Figure 3. (a) Equilibrium phase composition of 2 mol CO+ 1 mol Fe3O4 + 1 mol SnO2 roasted with different amounts of SO2 at 1100 °C; (b) Gibbs free energy changes for reaction (1)–(5) at 500–1100 °C; (c,d) Equilibrium phase composition of 1.5 mol SO2+ 1 mol Fe3O4 + 1 mol SnO2 roasted with different amounts of CO at 1100 °C.
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Figure 4. (a) The changes of CO partial pressure (PCO) with the increase of SO2 partial pressure (PSO2); (b) The predominance area diagram of Fe−Sn−S−O at 1000 °C ; (c) Effects of SO2 partial pressure on the Sn volatilization ratio from the tin-bearing iron concentrate; (d) The S content in the roasted iron concentrate under different SO2 partial pressure.
Figure 4. (a) The changes of CO partial pressure (PCO) with the increase of SO2 partial pressure (PSO2); (b) The predominance area diagram of Fe−Sn−S−O at 1000 °C ; (c) Effects of SO2 partial pressure on the Sn volatilization ratio from the tin-bearing iron concentrate; (d) The S content in the roasted iron concentrate under different SO2 partial pressure.
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Figure 5. (a) XRD patterns of the roasted residue at the SO2 partial pressure of 0.001 and 0.003 respectively; (b) SEM-EDS result of the roasted residue at the SO2 partial pressure of 0.003.
Figure 5. (a) XRD patterns of the roasted residue at the SO2 partial pressure of 0.001 and 0.003 respectively; (b) SEM-EDS result of the roasted residue at the SO2 partial pressure of 0.003.
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Figure 6. Effects of roasting temperature on the Sn volatilization ratio (a) from the tin-bearing iron concentrate and S content in the roasted iron concentrate (b).
Figure 6. Effects of roasting temperature on the Sn volatilization ratio (a) from the tin-bearing iron concentrate and S content in the roasted iron concentrate (b).
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Figure 7. XRD results of the roasted residues at 1050 °C (a) and 1100 °C (b), respectively, for 40 min with the PSO2 of 0.003; SEM-EDS results of the roasted residues at 1050 °C (c) and 1100 °C (d), respectively, for 40 min with the PSO2 of 0.003.
Figure 7. XRD results of the roasted residues at 1050 °C (a) and 1100 °C (b), respectively, for 40 min with the PSO2 of 0.003; SEM-EDS results of the roasted residues at 1050 °C (c) and 1100 °C (d), respectively, for 40 min with the PSO2 of 0.003.
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Figure 8. Effect of residence time on Sn volatilization ratio from the tin-bearing iron concentrate (a) and S content in the roasted residue (b).
Figure 8. Effect of residence time on Sn volatilization ratio from the tin-bearing iron concentrate (a) and S content in the roasted residue (b).
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Figure 9. (a) Relationship between [1 − 2X/3 − (1 − X) 2/3] and different residence time; (b) Relationship between [1 − (1 − X)1/3] and different residence time; (c) Relationship between [1 + (1 − X)1/3 2 (1 − X)2/3] and t/ [1 − (1 − X)1/3].
Figure 9. (a) Relationship between [1 − 2X/3 − (1 − X) 2/3] and different residence time; (b) Relationship between [1 − (1 − X)1/3] and different residence time; (c) Relationship between [1 + (1 − X)1/3 2 (1 − X)2/3] and t/ [1 − (1 − X)1/3].
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Table 1. Chemical composition of the Sn-bearing iron concentrate.
Table 1. Chemical composition of the Sn-bearing iron concentrate.
ElementFeSiO2SnZnCaOAl2O3PbOthers
Content65.520.910.390.042.300.870.129.87
Table 2. Kinetic equations for different controlling steps.
Table 2. Kinetic equations for different controlling steps.
Controlling StepKinetic Equation [26]
Interfacial chemical reactiont = a [1 − (1 − X)1/3]
Gas internal diffusiont = b [1 − 2X/3 − (1 − X)2/3]
Combination of interfacial chemical reaction and gas internal diffusiont = a1 [1 − (1 − X)1/3] + b1 [1 − 2X/3 − (1 − X)2/3]
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Li, L.; Xu, Z.; Wang, S. Tin Removal from Tin-Bearing Iron Concentrate with a Roasting in an Atmosphere of SO2 and CO. Metals 2022, 12, 1974. https://doi.org/10.3390/met12111974

AMA Style

Li L, Xu Z, Wang S. Tin Removal from Tin-Bearing Iron Concentrate with a Roasting in an Atmosphere of SO2 and CO. Metals. 2022; 12(11):1974. https://doi.org/10.3390/met12111974

Chicago/Turabian Style

Li, Lei, Zhipeng Xu, and Shiding Wang. 2022. "Tin Removal from Tin-Bearing Iron Concentrate with a Roasting in an Atmosphere of SO2 and CO" Metals 12, no. 11: 1974. https://doi.org/10.3390/met12111974

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