1. Introduction
Antimony is a vital strategic metal and has a wide range of uses in industry [1,2]. China is rich in antimony resources, with proven reserves of 640,000 tons of antimony in 2024, accounting for more than 30% of the global total [3]. At the same time, in 2023, the annual consumption of antimony resources in China reached approximately 150,000 tons, ranking it among the top in the world [4]. Antimony sulfide concentrate is one of the main raw materials for the production of metal antimony [5]; however, with increasing demands for antimony resources and the continuous shortage of single antimony ore resources, the extraction of antimony from complex resources containing antimony is the only means possible to sustainably develop the antimony industry [6,7]. Currently, more than 10 types of antimony-containing complex resources can meet the requirements of industrial production, including stibnite (Sb2S3), jamesonite (Pb4FeSb6S14), valentinite (Sb2O3, Sb 83.3%), senarmontite (Sb2O3, Sb 83.54%), and antimony–gold ore (Sb2S3, Sb 59.92%) [8,9,10]. Among these resources, antimony–gold symbiotic ore is a compound antimony ore with more economic value than single antimony ore [11]. As a result, this symbiotic ore is gradually replacing antimony sulfide concentrate and becoming one of the important raw materials for the production of metal antimony [12].
Currently, the treatment methods of antimony–gold symbiotic concentrate include the hydrometallurgical process and the pyrometallurgical process, with the latter method primarily used in enterprise production [13,14]. Volatilization smelting in a blast furnace is a typical pyrometallurgical process used for antimony-containing concentrates [15,16]. It faces issues, however, such as high energy consumption, difficulty in controlling environmental pollution, high production costs, and challenges in recovering precious metals [9]. The hydrometallurgical processes include the alkaline sulfide leach process [17,18], the acidic chloride leach process [19,20], and the pulp electrolysis process [21,22]. Although these processes do not produce sulfur dioxide (SO2) and have low energy consumption, they do encounter issues such as high consumption of water, large wastewater volumes, chlorine corrosion, and power consumption [23]. The oxygen-rich side-blown smelting process [24,25,26] has emerged as a novel technology in antimony smelting, characterized by its robust adaptability to raw materials, environmentally friendly approach, long furnace body life, high comprehensive metal recovery rate, and cost-effectiveness [27]. To address the issues of low metal recovery, high energy consumption, and high pollution associated with the existing treatment of antimony–gold concentrate, some scholars have proposed the adoption of a new synergistic oxygen-rich side-blown smelting process for lead concentrate and antimony–gold concentrate based on similar properties and its easy association with antimony and lead [28]. These scholars have initiated production practices. Zhang et al. [29] used the thermodynamic software FactSage 7.3 to calculate the reaction trend of various metal sulfides, the dominant region map of Me-S-O diagrams, and the distribution rule of phase equilibrium in the antimony–gold concentrate and lead concentrate synergistic smelting process and a verification test was carried out. However, the results were not quantitatively described in this research, and the yield of each product and the distribution behavior of each element in the product were not clear.
As advancements in computer hardware and software have been achieved, the quantitative analysis of the pyrometallurgical process has been performed using the multiphase equilibrium model [30] and leveraging computer-aided simulation techniques, which offer such benefits as high research efficiency, good reproducibility, low cost, and good security. Currently, scholars have performed thermodynamic simulation analysis and have conducted research on metallurgical processes, such as flash smelting [31,32], bottom-blown smelting [33,34], and side-blown smelting [35,36] of copper, lead, and other raw materials. These processes can better calculate and predict production output and reveal the distribution law of elements, providing theoretical guidance to optimize the production process.
Given these findings, in this study, we adopted the multiphase chemical equilibrium constant method [37,38], which was grounded in the mechanism of process and production practice of the antimony–lead synergistic side-blown oxidation smelting process and was based on the MetCal software platform (MetCal v7.81) [39]. We also researched and established a multiphase thermodynamic simulation model for the synergistic oxidation smelting of antimony and lead. Under typical production conditions, we conducted a thermodynamic simulation calculation for the antimony–lead synergistic side-blown oxidation smelting process while establishing a solid numerical modeling foundation for subsequent quantitative control and optimization of process parameters in this synergistic smelting process.
2. Process Mechanism and Model Establishment
2.1. Process Mechanism
The antimony–lead synergistic side-blown smelting process is based on a three-furnace segmented reaction design, including three stages of oxidation smelting, reduction smelting, and slag smelting [24]. In this study, we focused on the antimony–lead synergistic side-blown oxidation smelting process, which was completed in a side-blown oxidation furnace, as shown in Figure 1.
We added lead concentrate, antimony–gold concentrate, quartz sand, limestone, and other materials produced by belt ingredient mixing and granulation to a side-blown oxidation furnace. We added rich oxygen from both sides of the furnace body drum to the slag layer while strongly stirring the furnace high-temperature melt (1100–1300 °C). The antimony-containing and lead-containing materials oxidized rapidly, melted, and generated the primary antimony-rich crude lead, smelting slag, flue gas, and flue dust as well as other products in the furnace. The distribution rate of antimony and lead in the flue gas was low, while the distribution rate in the primary antimony-rich crude lead, smelting slag, and flue dust was high. Antimony and lead in the primary antimony-rich crude lead existed primarily in the form of monomers, and antimony and lead in the smelting slag and flue dust existed primarily in the form of oxides. Because of the large phase boundary area, the gas gave the molten pool a high stirring kinetic energy, the mass and heat transfer rate in the furnace was fast, and the phase composition of each product tended toward thermodynamic equilibrium quickly.
The products were precipitated and separated in the cylinder area of the furnace, the antimony-rich crude lead was discharged into the refining furnace from the siphon, and the smelting slag (containing approximately 30 wt% Pb, as analyzed using X-ray fluorescence (XRF)) was sent to the side-blown reduction furnace through the chute for further reduction smelting, which produced the secondary antimony-rich crude lead, reduction slag, flue gas, and flue dust. The gas generated during the oxidation and reduction smelting process was cooled in a waste heat boiler, and the flue dust was collected in an electric precipitator and then sent to the sulfuric acid system for acid production.
2.2. Model Assumption
In keeping with the mechanism of the antimony–lead synergistic side-blown oxidation smelting process, the products of this oxidative smelting process included antimony-rich crude lead, smelting slag, flue gas, and flue dust. In modeling the multiphase equilibrium model for this process, we assume that the equilibrium product phases encompassed three distinct phases: antimony-rich crude lead, smelting slag, and flue gas. The flue dust was composed of mixed mineral dust and product dust. Based on the reaction mechanism of the antimony–lead synergistic side-blown oxidation smelting process and literature reports, the composition of each equilibrium product is assumed to be as follows: (1). antimony-rich crude lead (ALd): Pb, PbS, Bi, Sb, Zn, Cu2S, FeS, As, Ag, and Other1; (2). smelting slag (Sl): PbO, PbSO4, PbS, ZnO, Cu2O, Cu2S, As2O3, Bi2O3, Sb2O3, Sb2O5, FeO, Fe3O4, FeS, CaO, Al2O3, MgO, SiO2, Ag, and Other2; (3). flue gas (gas): O2, Sb2O3, Sb2S3, Pb, PbO, PbS, As2O3, As2S3, Zn, ZnO, ZnS, SO2, S2, CO, CO2, N2, and H2O; (4). flue dust (Dt): Bi2S3, Sb2S3, As2S3, FeS, SiO2, Ag, Al2O3, H2O, FeS2, PbS, ZnS, Cu2S, Fe2O3, CaCO3, MgO, CaO, Pb, Bi, Zn, As, Sb, PbO, PbSO4, ZnO, Cu2O, Bi2O3, Sb2O3, Sb2O5, FeO, Fe3O4, As2O3, and Other3.
Among these products, “Other” denoted impurity elements that were not involved in the reactions but had the potential to influence the modeling of mass balance relationships.
2.3. Modeling Principles
We characterized the antimony–lead collaborative side-blown oxidation smelting process as a multiphase and multicomponent reactive system. The mathematical model for this process was developed using the chemical equilibrium constant method. In this method, at a constant temperature and pressure, we established a mathematical model based on the total moles of each element present and the independent chemical reactions occurring within the system when the system was at equilibrium. This model was expressed as a set of matrix nonlinear equations. By solving the mathematical model, we calculated the molar number of each phase and component in the system.
The multiphase multicomponent reaction system featured a set of linear independent molecular equation vectors, which were defined as independent components, and the rest were defined as subordinate components. Assuming that and , respectively, denoted the number of elements and the chemical composition in the antimony–lead synergistic side-blown oxidation smelting process, we determined the number of all components in the system by the reaction between the components, with the count of independent reactions denoted as , which was equal to . These independent reactions were represented by the following matrix equation:
(1)
where denotes the matrix of stoichiometric coefficients, denotes the molecular equation matrix of independent components, denotes the molecular equation matrix of subordinate components, and denote, respectively, the independent component number, subordinate component number, and element type number.According to the rules of matrix operation, can be calculated by the following equation:
(2)
where is the computable inverse matrix of .For the antimony–lead synergistic side-blown oxidation smelting process, we assumed that 0.2% of the inert constituent “Other” was allocated to the antimony-rich crude lead, while 99.8% was directed toward the smelting slag. On the basis of product assumptions and the principle of phase equilibrium, the composition of the multiphase equilibrium products included 17 elements and 46 compounds. The 17 elements included 15 individual elements (Pb, Zn, Cu, Fe, S, As, Sb, Ag, Bi, Al, Mg, O, H, N, and C) and 2 pseudo-elements (SiO2 and CaO). The total number of compound types corresponded to the sum of the types of compounds present in the antimony-rich crude lead, smelting slag, and flue gas. Therefore, in Equations (1) and (2), i and k ranged from 1 to 17, and j ranged from 1 to 27. There were 17 independent components and 27 subordinate components, excluding “Other,” which were represented by the stoichiometric coefficient matrices shown in Table A1 and Table A2 of Appendix A, respectively.
Table 1 shows the equilibrium reactions of 27 subordinate components and their equilibrium constant . The equilibrium constant of the independent reaction can be expressed by the following equation:
(3)
where R denotes the gas constant, T denotes the equilibrium temperature of the system, denotes the standard Gibbs free energy of formation of i independent components, and denotes the standard Gibbs free energy of formation of j subordinate components.When the multiphase reaction system of antimony–lead synergistic side-blown oxidation smelting reached the chemistry balance state, we determined the connection between 17 independent components and 27 subordinate components as shown in the following equation:
(4)
where denotes the molar number of i independent components, denotes the activity coefficient of i independent components, denotes the molar number of subordinate components, denotes the activity coefficient of subordinate components, denotes the molar number of i independent components, denotes the molar number of i subordinate components, and denotes the product phase.The total molar number of each component in the product phase in Equation (4) can be calculated by the following equation:
(5)
where i(m) denotes that the sum is obtained only when the i independent component belongs to the product phase, and j(m) denotes that the sum is obtained only when the subordinate component pertains to the product phase.According to the law of conservation of mass, the mass of each element can be calculated by the following equation:
(6)
where denotes the molar number of the element.For a closed pyrometallurgical system, we assumed that the number of product phases was defined as when the temperature, pressure, and number of elements of the system were given and had reached equilibrium. From Equations (3), (4) and (6), we observed that there were equations in the multiphase reaction system and that the number of variables to be solved was . The equations were matched in quantity to the variables that had to be resolved. The amount of each species in each phase at the equilibrium of this system can be obtained by solving the system of nonlinear equations consisting of Equations (4)–(6) according to the Newton–Raphson algorithm.
2.4. Mathematical Models and Computing Systems
On the basis of the mechanism of the antimony–lead synergistic side-blown oxidation smelting process and the modeling principle described in Section 2.3, we constructed the multiphase equilibrium model for this process using the chemical equilibrium constant method. The model can be solved by the calculation flowchart shown in Figure 2. After considering the heat balance connection between the input material and the output material within the smelting system, we developed the multiphase equilibrium calculation system in Figure 3 using the following equation, which was based on the MetCal software development platform (MetCal v7.81):
(7)
where Ai denotes the reactant; Ti denotes the initial temperature of the reactant Ai; Bj denotes the product; Tj denotes the temperature of the product Bj; nA denotes the number of reactants; nB denotes the number of products; H denotes the enthalpy value; Cp denotes the heat capacity; and QLoss denotes the amount of heat loss.3. Materials and Methods
3.1. Raw Material Composition
The raw materials for the side-blowing oxidation smelting process of an antimony and lead smelting enterprise in China included lead concentrate, antimony–gold concentrate, quartz sand, limestone, air, and industrial oxygen (oxygen volume concentration of 95%). We conducted XRF analysis, and the technical parameters of the equipment were as follows: in the linear range of less than 1%, the streaming gas detector counted 3000 kcps per second, and the scintillation detector counted 1500 kcps per second; the angular positioning accuracy of the scanning channel was less than 0.0001 degrees; and the range of analyzed elemental concentration was xppm—100%. We also used a spectrometer to analyze its elemental composition. According to the XRF analysis, we obtained the average value of the elemental composition of the raw materials used by the enterprise in December 2023, as shown in Table 2, Table 3, Table 4 and Table 5.
3.2. Calculation Condition and Mixed Ore Composition
Based on typical production data from a domestic antimony–lead smelting enterprise’s side-blown oxidative smelting process, the total raw material input was 50 t/h, with lead concentrate being 85.2%, antimony–gold concentrate 10.6%, quartz 0.2%, and limestone 4%. The oxygen–material ratio was set at 130 Nm3/t, and the oxygen enrichment concentration was 90%. We calculated the melting temperature according to the heat balance. We assumed that the temperature of the antimony-rich crude lead was 300 °C lower than that of the smelting slag and that the temperature of the flue gas and dust was 20 °C higher than that of the smelting slag. The elemental composition of each raw material is detailed in Table 2, Table 3, Table 4 and Table 5. The outer wall area was 400 m2, the furnace mouth area was 8 m2, and the furnace lining thickness was 1 m. The ambient temperature was 30 °C, and the liner material was made of magnesio-chrome tiles with a coefficient of blackness of 0.8 and a convective heat transfer coefficient of 3.5 W/(m2·K).
The mixed ore is obtained by batching and physical mixing of lead concentrate, antimony–gold concentrate, quartz, and lime melt, and its physical phase composition is shown in Table 6. The physical phase composition of the mixed ore was obtained by summing the physical phase compositions of the four solid raw materials. Among them, the physical phase compositions of antimony–gold concentrate and lead concentrate were obtained from the elemental analysis results obtained from XRF analysis of samples taken under typical working conditions and, based on the characteristics of the two types of concentrates belonging to sulfide ores and the principle of the minimum free energy [42], they were calculated by the constructed physical phase computation model assuming their physical phase types (i.e., compound compositions).
3.3. Thermodynamic Data
By combining Equation (8), the Kirchhoff formula, with Equation (9), which details the connection between the temperature and the standard molar entropy change in reactions, we computed the Gibbs free energy of the components in the antimony–lead synergistic side-blown oxidation smelting process using Equation (10):
(8)
(9)
(10)
We extracted the standard thermodynamic data for the products from the MetCal software (MetCal v7.81)’s database, as shown in Appendix A, Table A3. To negate the effects of reaction kinetics, we considered both production analysis and literature references [43,44,45,46] and adjusted the activity coefficients for certain products, as noted in Appendix A, Table A4. MQC indicates that the activity of the component is determined using MetCal v7.81’s modified quasi-chemical solution model for activity calculations. We treated the flue gas as an ideal gas, which suggested that its component activity coefficient should be set to 1.
4. Result and Discussion
4.1. Calculated Result
According to the calculation conditions and the phase composition of mixed ore of Section 3.2, we used the constructed multiphase equilibrium calculation system for the antimony–lead synergistic side-blown oxidation smelting process to calculate the composition and yield of equilibrium products. Table 7 and Table 8, respectively, show the main technical indices and heat balance calculation results of the antimony–lead synergistic oxidation smelting process. And the allocation behavior of the accessory elements in the products is illustrated in Figure 4.
4.2. Results Comparison
On the basis of production report data from a domestic antimony–lead smelting enterprise’s side-blown oxidation smelting section released in mid-December 2023, we compared the average analysis results of samples of the antimony-rich crude lead and smelting slag with the values calculated using our model, as shown in Table 9.
4.3. Discussion
From the results of the data presented in Figure 3, it is evident that elements such as Pb, Sb, Zn, As, Cu, and Fe were mainly enriched in the smelting slag during the antimony–lead synergistic side-blown oxidation smelting process, whereas Ag and Bi were mainly distributed in the antimony-rich crude lead. With the exception of S, the distribution rate of the other associated elements in the flue gas was not significant. The results show that the elements Pb, Sb, Zn, As, Cu, and Fe are more easily oxidized into slag, while Ag and Bi are less easily oxidized, so they are more distributed in antimony-rich crude lead.
Reviewing the data presented in Table 9, we observed that the calculated values for most elements in the products closely matched the average production measurements, except for certain elements that were not detected during production. Specifically, the relative errors for Pb, Sb, Cu, As, Bi, and Ag in the antimony-rich crude lead were 4.83%, 3.92%, 0.08%, 0.36%, 1.88%, and 1.23%, respectively. For the smelting slag, the relative errors for Pb, Sb, Zn, Cu, Fe, CaO, SiO2, S, As, Bi, and Ag were 1.43%, 9.29%, 7.96%, 8.29%, 2.64%, 0.55%, 2.03%, 4.57%, 0.10%, 0%, and 5.17%, respectively. Notably, the discrepancies between simulated and measured values for Zn, Cu, Sb, and As in the smelting slag were substantial, which we attributed to detection errors associated with the quantification of trace elements in the production analysis, as well as inherent errors in the model itself.
In order to further improve the accuracy and reliability, it is necessary to continue to optimize the model and to carry out more precise detection in the future. Although there are certain discrepancies between the production data and the calculated values of the model, these errors are currently in a controllable range, with relative errors remaining below 10%. These comparison results demonstrated that the model developed in this research was able to capture the multiphase reaction characteristics of the antimony–lead synergistic side-blown oxidation smelting process. This process had the capacity to precisely forecast the smelting production process and to refine process parameters, thus serving as an effective instrument for the subsequent systematic thermodynamic analysis of the process.
5. Conclusions
On the basis of the multiphase reaction mechanism and features of the antimony–lead synergistic side-blown oxidation smelting process, we constructed a thermodynamic simulation model and calculation system of the antimony–lead synergistic side-blown oxidation smelting process using the chemical equilibrium constant approach and MetCal software platform (MetCal v7.81), which provided a software-based tool for the thermodynamic calculation and analysis of the smelting process. The model is based on the MetCal platform (MetCal v7.81), which has high accuracy, low error predictions and fast computation speed.
Using the established calculation system, we conducted an instance validation under the typical production conditions of a domestic enterprise. The outcomes from the product composition closely matched the actual manufacturing outcomes, demonstrating that the constructed model effectively embodied the multiphase reaction features of the antimony–lead synergistic side-blown oxidation smelting process and possessed the ability to accurately forecast the output of this process.
Through verification and contrast experiments, we found that the calculated values of the main technical index for the antimony–lead synergistic side-blown oxidation smelting process had a small relative error compared with the average measured values from industrial production during the same period. The relative errors of the calculated mass fractions of Pb, Sb, Zn, Cu, Fe, CaO, SiO2, S, As, Bi, and Ag in antimony-rich crude lead and smelting slag are less than 10%. Although there is an error margin, it is acceptable. In the future, the constructed model and calculation system can be used to carry out conditional experiments to optimize and regulate different process parameters, so as to provide a model basis for the subsequent on-line optimization and regulation of the antimony and lead synergistic side-blowing oxidation smelting process.
Conceptualization, M.L. and B.M.; Formal analysis, Z.Z. (Zhenquan Zhong) and M.L.; Investigation, Y.F. and X.C.; Resources, Z.Z. (Zhenquan Zhong) and Z.Z. (Zhongtang Zhang); Visualization, Z.Z. (Zhenquan Zhong) and M.L.; Writing—original draft, Z.Z. (Zhenquan Zhong), M.L. and Y.F.; and Writing—review and editing, Z.Z. (Zhenquan Zhong) and M.L. All authors have read and agreed to the published version of the manuscript.
The original contributions presented in this study are included in the article material. Further inquiries can be directed to the corresponding author.
We would like to thank Huang Jindi for his suggestions on this article. Thanks to Tong Changren for his guidance and support in obtaining the license to use MetCal v7.81. Special thanks to Guangxi Nandan Nanfang Metal Co., Ltd. for providing the production data for this study.
The authors declare no conflicts of interest.
Footnotes
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.
Figure 1 Oxygen-enriched side-blown furnace [
Figure 2 Calculation flowchart of thermodynamic model [
Figure 3 Multiphase equilibrium calculation system for the antimony–lead synergistic side-blown oxidation smelting process.
Figure 4 Distribution rate of accessory elements in the product: (a) Pb, (b) Sb, (c) Zn, (d) As, (e) Cu, (f) Fe, (g) Ag, (h) S, and (i) Bi.
Equilibrium reactions and equilibrium constants of the antimony–lead synergistic side-blown oxidation melting system.
Equilibrium Reaction | Kj | Equilibrium Reaction | Kj |
---|---|---|---|
2Pb(ALd) + O2(Gas) = 2PbO(Sl) | K 1 | As2O3(Sl) = As2O3(Gas) | K 15 |
PbS(ALd) + O2(Gas) = Pb(Sl) + SO2(Gas) | K 2 | Sb2O3(Sl) = Sb2O3(Gas) | K 16 |
2Zn(ALd) + O2(Gas) = 2ZnO(Sl) | K 3 | 6FeO(Sl) + O2(Gas) = 2Fe3O4(Sl) | K 17 |
4Sb(ALd) + 3O2(Gas) = 2Sb2O3(Sl) | K 4 | 2FeS(Sl) + 3O2(Gas) = 2FeO(Sl) + 2SO2(Gas) | K 18 |
4As(ALd) + 3O2(Gas) = 2As2O3(Sl) | K 5 | 2Cu2S(Sl) + 3O2(Gas) = 2Cu2O(Sl) + 2SO2(Gas) | K 19 |
Pb(ALd) = Pb(Gas) | K 6 | 2PbO(Sl) + O2(Gas) + 2SO2(Gas) = 2PbSO4(Sl) | K 20 |
Ag(ALd) = Ag(Sl) | K 7 | 2ZnS(Gas) + 3O2(Gas) = 2ZnO(Gas) + 2SO2(Gas) | K 21 |
2Cu2S(Sl) + 3O2(Gas) = 2Cu2O(Sl) + 2SO2(Gas) | K 8 | 2Zn(Gas) + O2(Gas) = 2ZnO(Gas) | K 22 |
2FeS(ALd) + 3O2(Gas) = 2FeO(Sl) + 2SO2(Gas) | K 9 | 2As2S3(Gas) + 9O2(Gas) = 2As2O3(Gas) + 6SO2(Gas) | K 23 |
2Pb(Gas) + O2(Gas) = 2PbO(Gas) | K 10 | 2Sb2S3(Gas) + 9O2(Gas) = 2Sb2O3(Gas) + 6SO2(Gas) | K 24 |
PbS(Sl) + 2PbO(Sl) = 3Pb(ALd) + SO2(Gas) | K 11 | S2(Gas) + 2O2(Gas) = 2SO2(Gas) | K 25 |
PbS(Sl) = PbS(Gas) | K 12 | 2CO(Gas) + O2(Gas) = 2CO2(Gas) | K 26 |
ZnO(Sl) = ZnO(Gas) | K 13 | 4Sb(ALd) + 5O2(Gas) = 2Sb2O5(Sl) | K 27 |
4Bi(ALd) + 3O2(Gas) = 2Bi2O3(Sl) | K 14 |
Chemical composition of lead concentrate (wt.%).
Pb | Zn | Bi | Cu | Fe | Ca | SiO2 |
40.76 | 5.90 | 0.54 | 0.65 | 14.80 | 2.1 | 8.58 |
S | Mg | Al | C | O | Other | |
16.30 | 1.14 | 0.26 | 0.63 | 7.31 | 1.03 |
Chemical composition of antimony–gold concentrate (wt.%).
Sb | Fe | S | SiO2 | As | Al | Ag | O | Other |
---|---|---|---|---|---|---|---|---|
40.55 | 3.50 | 27.00 | 12.34 | 13.82 | 0.36 | 1.22 | 0.32 | 0.90 |
Chemical composition of quartz (wt.%).
SiO2 | CaO | FeO | O | Other |
---|---|---|---|---|
85.00 | 5.00 | 2.64 | 0.29 | 7.07 |
Chemical composition of limestone (wt.%).
FeO | CaO | SiO2 | O | Other |
---|---|---|---|---|
0.49 | 53.00 | 1.04 | 0.43 | 45.04 |
Phase composition of mixed ore (wt.%).
PbS | ZnS | Cu2S | Fe2O3 | FeS | CaCO3 | SiO2 | Ag | Al2O3 |
37.23 | 6.96 | 0.64 | 10.05 | 0.53 | 4.15 | 8.18 | 0.12 | 0.46 |
As2S3 | Sb2S3 | Bi2S3 | MgO | H2O | FeS2 | CaO | Other | |
2.30 | 5.73 | 0.53 | 4.15 | 6.95 | 10.12 | 1.98 | 2.60 |
Calculation results of the main technical index.
Name | Unit | Value | Name | Unit | Value |
---|---|---|---|---|---|
Pb content of ALd | % | 89.29 | Pb content of dust | % | 38.03 |
Sb content of ALd | % | 3.24 | Sb content of dust | % | 5.05 |
Direct yield of Pb | % | 20.62 | Temperature of ALd | °C | 829 |
Direct yield of Sb | % | 5.87 | Temperature of slag | °C | 1129 |
FeO/SiO2 in slag | 2.30 | Temperature of gas | °C | 1149 | |
CaO/SiO2 in slag | 0.53 | Yield of dust | % | 13.88 | |
CaO/FeO in slag | 0.28 | Yield of ALd | % | 6.18 | |
Pb content of slag | % | 32.88 | Yield of slag | % | 48.60 |
Sb content of slag | % | 5.34 | Yield of gas | % | 33.69 |
Calculation results of heat balance.
Type | Heat Type | Material Name | Temperature (°C) | Heat Quantity (MJ/h) | Ratio of Heat |
---|---|---|---|---|---|
Heat income | Physical heat | Mixed ore | 25 | 0.00 | 0.00 |
Industrial oxygen | 25 | 0.00 | 0.00 | ||
Air | 25 | 0.00 | 0.00 | ||
Chemical heat | 25 | 59,250.37 | 100.00 | ||
Exchange heat | Cooling inlet water | 37 | |||
Total | 55,250.37 | 100.00 | |||
Heat outcome | Physical heat | Antimony-rich crude lead | 829 | 480.12 | 0.81 |
Smelting slag | 1129 | 23,199.92 | 39.16 | ||
Flue gas | 1149 | 24,207.03 | 40.86 | ||
Dust | 1149 | 5186.27 | 8.75 | ||
Exchange heat | Cooling outlet water | 38 | 836.39 | 1.41 | |
Natural heat | 60 | 5340.64 | 9.01 | ||
Total | 59,250.37 | 100.00 |
Calculation results and industrial data (wt.%).
Value | Phase | Pb | Sb | Zn | Cu | Fe | CaO | SiO2 | S | As | Bi | Ag |
---|---|---|---|---|---|---|---|---|---|---|---|---|
Calculated | ALd | 89.292 | 3.238 | 0.002 | 1.319 | 0 | - | - | 0.348 | 0.555 | 4.284 | 0.903 |
Measured | 85.176 | 3.370 | - | 1.318 | - | - | - | - | 0.553 | 4.366 | 0.892 | |
Calculated | Sl | 32.875 | 5.275 | 6.590 | 0.562 | 17.062 | 6.083 | 11.558 | 1.282 | 2.06 | 0.07 | 0.061 |
Measured | 33.351 | 5.815 | 7.160 | 0.519 | 17.525 | 6.050 | 11.797 | 1.226 | 2.064 | 0.070 | 0.058 |
Appendix A
Stoichiometry matrix for 17 independent species.
Component | Phase | Pb | Zn | Cu | Fe | S | As | Sb | Mg | Al | Bi | Ag | SiO2 | CaO | O | C | H | N |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Pb | Ld | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
PbS | Ld | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Zn | Ld | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Cu2S | Ld | 0 | 0 | 2 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
FeS | Ld | 0 | 0 | 0 | 1 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
As | Ld | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sb | Ld | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Bi | Ld | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Ag | Ld | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 |
Al2O3 | Sl | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 0 |
MgO | Sl | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 |
SiO2 | Sl | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 |
CaO | Sl | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 |
O2 | Gas | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 |
CO | Gas | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 1 | 0 | 0 |
H2O | Gas | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 2 | 0 |
N2 | Gas | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 |
Stoichiometry matrix for 27 subordinate species.
Component | Phase | Pb | Zn | Cu | Fe | S | As | Sb | Bi | Ag | SiO2 | CaO | O | C | H | N |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
PbO | Sl | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 |
PbSO4 | Sl | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 0 | 0 | 0 |
PbS | Sl | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
ZnO | Sl | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 |
Cu2O | Sl | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 |
Cu2S | Sl | 0 | 0 | 2 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
FeO | Sl | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 |
Fe3O4 | Sl | 0 | 0 | 0 | 3 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 0 | 0 | 0 |
FeS | Sl | 0 | 0 | 0 | 1 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
As2O3 | Sl | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 0 |
Sb2O3 | Sl | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 0 |
Bi2O3 | Sl | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 3 | 0 | 0 | 0 |
Sb2O5 | Sl | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 5 | 0 | 0 | 0 |
Ag | Sl | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 |
Pb | Gas | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
PbO | Gas | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 |
PbS | Gas | 1 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Zn | Gas | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
ZnO | Gas | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 |
ZnS | Gas | 0 | 1 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
As2O3 | Gas | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 0 |
As2S3 | Gas | 0 | 0 | 0 | 0 | 3 | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sb2O3 | Gas | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 0 |
Sb2S3 | Gas | 0 | 0 | 0 | 0 | 3 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
SO2 | Gas | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 |
S2 | Gas | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
CO2 | Gas | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 1 | 0 | 0 |
Standard thermodynamic parameters of product components.
Component | State | cp = a + b × 10−3T + c × 105T−2 + d × 10−6T2 | |||||
---|---|---|---|---|---|---|---|
a | b | c | d | ||||
Pb | Liquid | 3.873 | 70.506 | 27.159 | 1.029 | 0 | 0 |
PbS | Liquid | −93.143 | 84.129 | 66.946 | 0 | 0 | 0 |
Bi | Liquid | 9.271 | 71.980 | 27.197 | 0 | 0 | 0 |
Sb | Liquid | 17.531 | 62.712 | 31.381 | 0 | 0 | 0 |
Zn | Liquid | 5.727 | 48.549 | 31.381 | 0 | 0 | 0 |
Cu2S | Liquid | −68.100 | 132.462 | 89.665 | 0 | 0 | 0 |
FeS | Liquid | −64.631 | 91.208 | 62.552 | 0 | 0 | 0 |
As | Liquid | 21.568 | 53.284 | 28.833 | 0 | 0 | 0 |
Ag | Liquid | 6.393 | 43.220 | 33.473 | 0 | 0 | 0 |
PbO | Liquid | −202.249 | 73.379 | 65.000 | 0 | 0 | 0 |
PbSO4 | Liquid | −923.159 | 148.494 | 186.004 | 0 | 0 | 0 |
ZnO | Liquid | −309.542 | 47.920 | 60.669 | 0 | 0 | 0 |
Cu2O | Liquid | −130.224 | 96.402 | 99.916 | 0 | 0 | 0 |
As2O3 | Liquid | −643.439 | 128.125 | 152.720 | 0 | 0 | 0 |
Sb2O3 | Liquid | −675.490 | 143.628 | 156.904 | 0 | 0 | 0 |
Sb2O5 | Liquid | −971.925 | 125.105 | 141.331 | −3.732 | −20.113 | 0 |
Bi2O3 | Liquid | −578.024 | 149.814 | 202.005 | 0 | 0 | 0 |
FeO | Liquid | −257.276 | 57.591 | 68.201 | 0 | 0 | 0 |
Fe3O4 | Liquid | −993.334 | 198.385 | 213.389 | 0 | 0 | 0 |
SiO2 | Liquid | −927.548 | 9.310 | 85.774 | 0.000 | 0.000 | 0.000 |
CaO | Liquid | −572.908 | 40.980 | 62.762 | 0.000 | 0.000 | 0.000 |
MgO | Liquid | −561.018 | 12.833 | 66.946 | 0.000 | 0.000 | 0.000 |
Al2O3 | Liquid | −595.568 | 45.145 | 144.866 | 0.000 | 0.000 | 0.000 |
Pb | Gas | 195.205 | 175.377 | 28.063 | −11.029 | −9.310 | 4.728 |
PbO | Gas | 68.139 | 240.048 | 41.612 | −3.526 | −20.136 | 1.014 |
PbS | Gas | 127.959 | 251.416 | 37.350 | 0.194 | −2.096 | 0.140 |
Zn | Gas | 130.403 | 16.992 | 20.898 | −0.133 | −0.067 | 0.034 |
ZnO | Gas | 136.518 | 242.811 | 37.671 | −0.286 | −1.985 | 0.735 |
ZnS | Gas | 204.322 | 236.404 | 166.350 | −85.742 | −166.125 | 21.952 |
As2O3 | Gas | −322.845 | 371.925 | 82.134 | 6.444 | −5.356 | 0 |
As2S3 | Gas | 27.042 | 314.289 | 96.201 | 1.071 | −8.213 | 0 |
Sb2O3 | Gas | −708.564 | 129.903 | 180.004 | 0 | 0 | 0 |
Sb2S3 | Gas | 119.661 | 409.820 | 107.636 | 0.209 | −7.255 | 0 |
O2 | Gas | 0 | 205.154 | 34.860 | 1.312 | −14.141 | 0.163 |
SO2 | Gas | −296.820 | 248.226 | 54.781 | 3.350 | −24.745 | −0.241 |
S2 | Gas | 128.603 | 228.169 | 34.672 | 3.286 | −2.816 | −0.312 |
CO | Gas | −110.544 | 197.665 | 29.932 | 5.415 | −10.814 | −1.054 |
CO2 | Gas | −393.515 | 213.774 | 54.437 | 5.116 | −43.579 | −0.806 |
N2 | Gas | 0 | 191.615 | 23.529 | 12.117 | 1.210 | −3.076 |
H2O | Gas | −241.832 | 188.837 | 31.438 | 14.106 | −24.952 | −1.832 |
Activity coefficients of product components.
Component | Phase | Activity Coefficient |
---|---|---|
PbO | Sl | 1 |
PbSO4 | Sl | 0.8 |
PbS | Sl | 0.5 |
ZnO | Sl | 0.1 |
Cu2O | Sl | 0.002 |
Cu2S | Sl | 50 |
FeO | Sl | 0.0001 |
Fe3O4 | Sl | 0.1 |
FeS | Sl | 0.0001 |
As2O3 | Sl | 0.003 |
Sb2O3 | Sl | 0.002 |
Sb2O5 | Sl | MQC |
Bi2O3 | Sl | 1.64 |
CaO | Sl | 0.1 |
MgO | Sl | 1 |
Al2O3 | Sl | 1 |
SiO2 | Sl | 0.1 |
Ag | Sl | 1.351 |
Pb | ALd | 0.35 |
PbS | ALd | 20 |
Sb | ALd | 0.0078 |
CuS | ALd | 0.028 |
FeS | ALd | 100 |
Zn | ALd | 0.066 |
As | ALd | 0.058 |
Bi | ALd | 18 |
Ag | ALd | 0.045 |
1. Li, J.; Xu, D.; Zhu, Y. Global antimony supply risk assessment through the industry chain. Front. Energy Res.; 2022; 10, 1007260. [DOI: https://dx.doi.org/10.3389/fenrg.2022.1007260]
2. Zhao, G.; Li, W.; Geng, Y.; Bleischwitz, R. Uncovering the features of global antimony resource trade network. Resour. Policy; 2023; 85, 103815. [DOI: https://dx.doi.org/10.1016/j.resourpol.2023.103815]
3. U.S. Geological Survey. Mineral Commodity Summaries 2024; U.S. Geological Survey: Reston, VA, USA, 2024; 212p.
4. Tang, M.T.; Tang, C.B.; Yang, J.M.; Chen, Y.M.; Yang, S.H. Development Trend of Antimony Industry in China under Dual Carbon Strategy. Nonferrous Met.; 2024; 11, pp. 110-116.
5. Multani, R.S.; Feldmann, T.; Demopoulos, G.P. Antimony in the metallurgical industry: A review of its chemistry and environmental stabilization options. Hydrometallurgy; 2016; 164, pp. 141-153. [DOI: https://dx.doi.org/10.1016/j.hydromet.2016.06.014]
6. Wu, Q.J.; Lv, Z.; Cao, J.C. Distribution and supply of antimony resources in China and abroad and development status of antimony industry Chain. Multipurp. Util. Miner. Resour.; 2022; 43, pp. 77-82.
7. Zhong, D.P.; Li, L.; Tan, C. Recovery of antimony from antimony-bearing dusts through reduction roasting process under CO—CO2 mixture gas atmosphere after firstly oxidation roasted. J. Cent. South Univ.; 2018; 25, pp. 1904-1913. [DOI: https://dx.doi.org/10.1007/s11771-018-3880-y]
8. Dembele, S.; Akcil, A.; Panda, S. Technological trends, emerging applications and metallurgical strategies in antimony recovery from stibnite. Miner. Eng.; 2022; 175, 107304. [DOI: https://dx.doi.org/10.1016/j.mineng.2021.107304]
9. Ding, J.; Zhang, Y.; Ma, Y.; Wang, Y.; Zhang, J.; Zhang, T. Metallogenic characteristics and resource potential of antimony in China. J. Geochem. Explor.; 2021; 230, 106834. [DOI: https://dx.doi.org/10.1016/j.gexplo.2021.106834]
10. Kanellopoulos, C.; Sboras, S.; Voudouris, P.; Soukis, K.; Moritz, R. Antimony’s Significance as a Critical Metal: The Global Perspective and the Greek Deposits. Minerals; 2024; 14, 121. [DOI: https://dx.doi.org/10.3390/min14020121]
11. Huang, M.; Li, Z.; Wang, Q.; Guo, X.; Li, W. Antimony and gold substance flows analysis of pyrometallurgical process for antimony-gold concentrates. J. Clean. Prod.; 2023; 420, 138385. [DOI: https://dx.doi.org/10.1016/j.jclepro.2023.138385]
12. Ding, L.F.; Liu, Y.C.; Fu, J.G.; Zhang, Y.R.; Lin, Y.; Zhao, Y.C.; Hua, X.Y. Sulfur Reduction and Upgrading of High-Sulfur Antimony-Gold Bulk Concentrate from Russia. Min. Metall. Eng.; 2023; 43, pp. 77-79.
13. Ma, D.; Li, D.B.; Chen, X.G.; Pei, Z.Y. Research progress of antimony concentrate smelting technology. China Nonferrous Metall.; 2020; 49, pp. 49-54.
14. Zhu, Q.; Yang, J.G.; Tang, S.Y.; Man, T.X.; Liu, J.; Ye, W.L.; Tang, C.B. Current Development Status of Clean Metallurgical Technologiesfor Antimony. Nonferrous Met. (Extr. Metall.); 2025; 04, pp. 30-38.
15. Yu, Z.; Wang, L.; Zheng, Q.; Che, X.; Cui, X.; Wei, S.; Li, H.; Shi, X. Present Situation and Research Progress of Comprehensive Utilization of Antimony Tailings and Smelting Slag. Sustainable; 2023; 15, 13947. [DOI: https://dx.doi.org/10.3390/su151813947]
16. Wang, K.; Wang, Q.M.; Chen, Y.L.; Li, Z.C.; Guo, X.Y. Antimony and arsenic substance flow analysis in antimony pyrometallurgical process. Trans. Nonferrous Met. Soc. China; 2023; 33, pp. 2216-2230. [DOI: https://dx.doi.org/10.1016/S1003-6326(23)66254-5]
17. Ling, H.; Malfliet, A.; Blanpain, B.; Guo, M. A review of the technologies for antimony recovery from refractory ores and metallurgical residues. Miner. Process. Extr. Metall. Rev.; 2024; 45, pp. 200-224. [DOI: https://dx.doi.org/10.1080/08827508.2022.2132946]
18. Celep, O.; Alp, İ.; Deveci, H. Improved gold and silver extraction from a refractory antimony ore by pretreatment with alkaline sulphide leach. Hydrometallurgy; 2011; 105, pp. 234-239. [DOI: https://dx.doi.org/10.1016/j.hydromet.2010.10.005]
19. Krenev, V.; Dergacheva, N.; Fomichev, S. Hydrometallurgical processes of antimony extraction from ores and concentrates. Theor. Found. Chem. Eng.; 2016; 50, pp. 613-619. [DOI: https://dx.doi.org/10.1134/S0040579516040151]
20. Yang, T.; Rao, S.; Liu, W.; Zhang, D.; Chen, L. A selective process for extracting antimony from refractory gold ore. Hydrometallurgy; 2017; 169, pp. 571-575. [DOI: https://dx.doi.org/10.1016/j.hydromet.2017.03.014]
21. Solozhenkin, P.M.; Alekseev, A.N. Innovative Processing and Hydrometallurgical Treatment Methods for Complex Antimony Ores and Concentrates. Part II: Hydrometallurgy of Complex Antimony Ores. J. Min. Sci.; 2010; 46, pp. 446-452. [DOI: https://dx.doi.org/10.1007/s10913-010-0056-z]
22. Zhang, Y.; Wang, C.; Ma, B.; Jie, X.; Xing, P. Extracting antimony from high arsenic and gold-containing stibnite ore using slurry electrolysis. Hydrometallurgy; 2019; 186, pp. 284-291. [DOI: https://dx.doi.org/10.1016/j.hydromet.2019.04.026]
23. Wang, Y.; Liu, C.; Li, Y.; Ye, Y.; Xu, F.; Li, Y. Metallic antimony preparation by carbothermic reduction of stibnite concentrates: Strategies, mechanisms, and comparison of microwave and conventional roasting. Miner. Eng.; 2024; 208, 108584. [DOI: https://dx.doi.org/10.1016/j.mineng.2024.108584]
24. Zhou, A.; Zhang, L.; Zhou, Y.; Li, Y.; Wu, X.; Xia, L.; Liu, Z. Co-Smelting Process of Pb Concentrate and Zn Leaching Residues with Oxygen-Rich Side Blowing Furnaces: Industrial Application and Material Balance. JOM; 2023; 75, pp. 5833-5846. [DOI: https://dx.doi.org/10.1007/s11837-023-06192-9]
25. Mao, Q.H.; Gang, Y.; Chong, Y.; Long, H. Dynamic soft sensor modeling of matte grade in copper oxygen-rich side blow bath smelting process. Measurement; 2023; 223, 113792.
26. Bian, Z.; Chen, D.; Sun, L.; Wang, L.; Zhao, H.; Zhen, Y.; Qi, T. Numerical Simulation and Experimental Investigation of Multiphase Flow in an Oxygen-Rich Side-Blown Bath Smelting Furnace. JOM; 2023; 75, pp. 3962-3974. [DOI: https://dx.doi.org/10.1007/s11837-023-06009-9]
27. Jiang, X.; Cui, Z.; Chen, M.; Zhao, B. Mixing behaviors in the horizontal bath smelting furnaces. Metall. Mater. Trans. B; 2019; 50, pp. 173-180. [DOI: https://dx.doi.org/10.1007/s11663-018-1433-2]
28. Boyle, R.; Jonasson, I. The geochemistry of antimony and its use as an indicator element in geochemical prospecting. J. Geochem. Explor.; 1984; 20, pp. 223-302. [DOI: https://dx.doi.org/10.1016/0375-6742(84)90071-2]
29. Zhang, Z.T.; Liu, L.J.; Li, Y.H.; Nie, H.P.; Wang, R.X.; Xu, Z.F. Thermodynamic Study on Synergistic Smelting Process of Complex Antimony Gold Concentrate and Lead Concentrate. Nonferrous Met. (Extr. Metall.); 2023; 12, pp. 9-17.
30. Leal, A.M.M.; Kulik, D.A.; Kosakowski, G. Computational methods for reactive transport modeling: A Gibbs energy minimization approach for multiphase equilibrium calculations. Adv. Water Resour.; 2016; 88, pp. 231-240. [DOI: https://dx.doi.org/10.1016/j.advwatres.2015.11.021]
31. Wang, J.; Chen, Y.; Zhang, W.; Zhang, C. Furnace structure analysis for copper flash continuous smelting based on numerical simulation. Trans. Nonferrous Met. Soc. China; 2013; 23, pp. 3799-3807. [DOI: https://dx.doi.org/10.1016/S1003-6326(13)62932-5]
32. Feng, Y.C.; Li, M.Z.; Dao, Y.Q.; Huang, J.D.; Xie, J.C.; Li, J.B. Thermodynamic Simulation Analysis of Copper Flash Smelting Process with Oxidized Ore Addition. Nonferrous Met. (Extr. Metall.); 2025; 3, pp. 10-20.
33. Zhang, Z.K.; Li, M.; LLiu, K.; LI, X.X. Analysis on the Influence Law of Key Parameters for Double Bottom Blowing Continuous Copper Smelting Process Based on MetCal Calculation Model. Sci. Technol. Eng.; 2022; 22, pp. 8652-8659.
34. Wang, B.R.; Yang, H.Y.; Jin, Z.N.; Tong, L.L.; Ma, Z.Y. Arsenic distribution and phase structure in oxygen-enriched bottom blown copper smelting process. Chin. J. Nonferrous Met.; 2024; 34, pp. 908-922.
35. Wang, J.S.; Qin, J.; Tao, J.; Huang, T.; Shi, X.X.; Cao, Z.M. Thermodynamic simulation and optimization of lead side blowing oxidation smelting process. Nonferrous Met. Sci. Eng.; 2020; 11, pp. 7-15.
36. Wu, X.Y.; Chen, F.Y.; Chen, Z.H.; He, E.; Zhang, X.X.; Hou, Y.Q.; Xie, G. Optimization of copper slag type in double-furnace continuous smelting with top and side blowing. Chin. J. Nonferrous Met.; 2024; 34, pp. 3476-3489.
37. Shen, Z.; Li, Y.; Xu, N.; Sun, B.; Du, W.; Xu, M.; Chang, L. Investigation on the chemical equilibrium products for CnHmOlNk type fuels using equilibrium constants database. Fuel; 2022; 310, 122325. [DOI: https://dx.doi.org/10.1016/j.fuel.2021.122325]
38. Crerar, D.A. A method for computing multicomponent chemical equilibria based on equilibrium constants. Geochim. Cosmochim. Acta; 1975; 39, pp. 1375-1384. [DOI: https://dx.doi.org/10.1016/0016-7037(75)90116-7]
39. Li, M.Z.; Zhou, J.M.; Tong, C.R.; Zhang, W.H.; Chen, Z.; Wang, J.L. Thermodynamic Modeling and Optimization of the Copper Flash Converting Process Using the Equilibrium Constant Method. Metall. Mater. Trans. B-Process Metall. Mater. Process. Sci.; 2018; 49, pp. 1794-1807. [DOI: https://dx.doi.org/10.1007/s11663-018-1277-9]
40. Li, M.; Feng, Y.; Chen, X. Thermodynamic Simulation Model of Copper Side-Blown Smelting Process. Metals; 2024; 14, 840. [DOI: https://dx.doi.org/10.3390/met14080840]
41. Chen, X.Z.; Li, M.Z.; Liu, F.P.; Huang, J.D.; Yang, M.H. Multi-Phase Equilibrium Model of Oxygen-Enriched Lead Oxidation Smelting Process Based on Chemical Equilibrium Constant Method. Processes; 2023; 11, 3043. [DOI: https://dx.doi.org/10.3390/pr11103043]
42. Chen, S.; Zhang, J.; Wang, Y.; Wang, T.; Li, Y.; Liu, Z. Thermodynamic Study of H2-FeO Based on the Principle of Minimum Gibbs Free Energy. Metals; 2023; 13, 225. [DOI: https://dx.doi.org/10.3390/met13020225]
43. Wang, J.; Wen, X.; Zhang, C. Thermodynamic model of lead oxide activity in PbO–CaO–SiO2–FeO–Fe2O3 slag system. Trans. Nonferrous Met. Soc. China; 2015; 25, pp. 1633-1639. [DOI: https://dx.doi.org/10.1016/S1003-6326(15)63768-2]
44. Maruoka, N.; Ueda, S.; Shibata, H.; Yamaguchi, K.; Kitamura, S.-y. Thermodynamic properties of lead oxide in a mixture of stainless steelmaking and nonferrous smelting slags. High Temp. Mater. Process.; 2012; 31, pp. 273-279. [DOI: https://dx.doi.org/10.1515/htmp-2011-0139]
45. Tan, P.; Zhang, C.; Zhang, R. Computer model of QSL lead smelting process. J. Cent. South Univ. Technol.; 1996; 27, pp. 543-546.
46. Wang, J.; Zhang, C.; Zhang, W. Multi-phase equilibrium model of lead flash smelting process. J. Cent. South Univ. Sci. Technol; 2012; 43, pp. 429-434.
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer
© 2025 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/). Notwithstanding the ProQuest Terms and Conditions, you may use this content in accordance with the terms of the License.
Abstract
On the basis of the theory of polyphase equilibrium and the utilization of the MetCal software platform (MetCal v7.81), we adopted the chemical equilibrium constant method and successfully constructed a multiphase equilibrium model and simulation system for the antimony–lead synergistic side-blown oxidation smelting process. In typical production conditions, which encompass factors such as the composition of raw material, the ratio of oxygen to material, and oxygen-enriched concentration, the equilibrium product composition and pivotal technical indices are modeled and computed. Calculation results indicated that, other than the trace elements in the smelting slag, the relative errors of the calculated values for the content of major elements in the antimony-rich crude lead and smelting slag were less than 10% of the measured value after average treatment in production. Therefore, our results showed that the developed model and system preferably embodied the practical production condition of the antimony–lead synergistic side-blown oxidation smelting process, which is capable of precisely forecasting the smelting outcomes and optimizing the process parameters, thereby offering effective guidance for the practical execution of the antimony–lead synergistic side-blown oxidation smelting process.
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer
Details


1 School of Metallurgical Engineering, Jiangxi University of Science and Technology, Ganzhou 341000, China; [email protected] (Z.Z.); [email protected] (Y.F.); [email protected] (X.C.); [email protected] (Z.Z.)
2 School of Metallurgical and Ecological Engineering, University of Science and Technology Beijing, Beijing 100083, China; [email protected]