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Article

Sodium-Oxide Fluxed Aluminothermic Reduction of Manganese Ore for a Circular Economy: Cr Collector Metal Application

by
Theresa Coetsee
1,* and
Frederik De Bruin
2
1
Department of Materials Science and Metallurgical Engineering, University of Pretoria, Pretoria 0002, South Africa
2
Independent Metallurgical Consultant, Pretoria 0002, South Africa
*
Author to whom correspondence should be addressed.
Sustain. Chem. 2025, 6(3), 30; https://doi.org/10.3390/suschem6030030
Submission received: 9 August 2025 / Revised: 15 September 2025 / Accepted: 16 September 2025 / Published: 18 September 2025

Abstract

Aluminothermic reduction is gaining renewed interest as an alternative processing route for the circular economy. Aluminium is produced electrochemically in the Hall–Héroult process with minimal CO2 emissions if electricity is sourced from non-fossil fuel energy sources. The Al2O3 product from the aluminothermic reduction process can be recycled via hydrometallurgy, with leaching as the first step. NaAlO2 is a water-leachable compound that forms a pathway for recycling Al2O3 with hydrometallurgy. In this work, a suitable slag formulation is applied in the aluminothermic reduction of manganese ore to form a Na2O-based slag of high Al2O3 solubility to effect good alloy–slag separation. The synergistic effect of added chromium metal as a collector metal is illustrated with an increased alloy yield at 68%, from 43% without added Cr. The addition of small amounts of carbon reductant to MnO2-containing ore ensures rapid pre-reduction to MnO. This approach negates the need for a pre-roasting step. The alloy and slag chemical analyses are compared to the thermochemistry-predicted phase chemistry. The alloy consists of 57% Mn, 18% Cr, 18% Fe, 3.4% Si, 1.5% Al, and 2.2% C. The formulated slag exhibits high Al2O3 solubility, enabling effective alloy–slag separation, even at an Al2O3 content of 55%.

1. Introduction

Thermic reduction of oxides with Al or Si as reductant is a well-established method for producing low-carbon ferroalloys. Both ferromanganese and ferrochromium of low carbon content can be produced in this way [1]. In the production of low-carbon ferrochromium (LCFeCr) and medium-carbon ferrochromium (MCFeCr) via silicothermic reduction, the Si reductant is applied in the form of ferrosilicon or ferrosilicochromium (45% Si, 40% Cr, 0.02% C) [1]. Typical ferrochromium grades are summarised in Table 1 to indicate the %C ranges per category of ferrochromium [1,2,3]. There are also sub-categories with lower %Cr; for example, as low as 45% Cr is deemed acceptable [1]. MCFeCr can be produced by silicothermic reduction or by refining high-carbon ferrochromium (HCFeCr) in the oxygen-blown converter process [1]. The slag used as a reactant feed in the silicothermic production process is prepared by melting a lime–chromite ore mixture in an electric furnace [1,3]. Similarly, to produce the Si reductant from quartz as ferrosilicon or ferrosilicochromium, an electric furnace is used. Consequently, the overall energy requirement for MCFeCr and LCFeCr production is high, at 8000–9000 kWh/t product [1].
Aluminothermic reduction can also be used to produce low-carbon ferrochromium; however, it is historically considered too expensive [1]. A recent new interest has developed in sourcing Al reductant from industrial waste streams of ferroaluminosilicalcium (FeAlSiCa) and ferrosilicochrome (FeSiCr) dust to produce carbon-free ferrochrome [4,5]. Beketov pioneered the aluminothermic reduction process in 1859 [6]. In the 19th century, the cost of aluminium decreased sufficiently for the practical industrial application of aluminothermic reduction, via the work of Beketov and Goldschmidt, respectively [6]. Despite a long history of development of aluminothermic reduction, different research approaches are used to improve process understanding and optimise reactant utilisation. For example, some studies applied reactants under a protective gas atmosphere to study specific reactions [7,8,9,10,11], while others performed aluminothermy in air to study the real-life process with ignition in air [12,13,14,15,16]. Process simulation experiments should be performed in air to assess the feasibility of the process in terms of reactant consumption, temperature attainment, and slag–metal separation.
As described by Gasik, the complex ferroalloy of FeCrAl is useful since the Al serves as a deoxidiser element whilst the liquid steel is alloyed with Cr, resulting in limited oxidation loss of Cr [3]. Aluminothermic reduction in chromium oxide materials with an excess of Al added can be used to produce this alloy. Carbothermic reduction of fused alumina in the presence of ferrochrome or ferrosilicochrome in a ferroalloy furnace can also produce this alloy [3]. Similarly, complex alloys such as ferrochrome-manganese alloy (FeCrMn) and ferrochrome-siliconmanganese alloy (FeCrMnSi) may be produced by reducing chromium and manganese oxide-containing melts with silicon and/or carbon reductant [3]. The motivation for using FeCrMn alloy as an alloying source addition to liquid steel is that the melting temperature is low (1400–1500 °C) in 30% Mn-35% Mn alloy, compared to the high melting temperature of LCFeCr (1640–1680 °C), and so facilitating fast dissolution into liquid steel [3]. A complex alloy for alloying high-carbon and tool steels is produced by high-temperature (1600–1700 °C) carbothermic reduction of low-grade manganese ore and chrome ore in an electric furnace. The reported average alloy composition is 19% Fe, 14% Si, 8% Mn, 58% Cr, 6% C [17]. The compositions of high manganese chromium-containing complex alloys are summarised in Table 1. From the above discussion, it is clear that a FeCrMnSiAl complex alloy may find similar application in liquid steel alloying.
Considering the shift in process requirements to reduce CO2 emissions and apply circular economy principles in metals production, the application of Al is a possible alternative processing route because Al is produced electrochemically in the Hall–Héroult process. This processing approach limits CO2 emissions if the electricity input is sourced from non-fossil fuel energy sources. This approach is attracting increased research attention in the aluminothermic production of manganese and silicon alloys, as well as in the recycling of waste streams, such as end-of-life lithium-ion batteries and waste iron oxides, including mill scale [7,8,9,10,12,13]. Furthermore, the Al2O3 product may be recycled as feed to the Hall–Héroult process after hydrometallurgical treatment [18,19]. Aluminothermic reduction of manganese ore is already applied to produce low-carbon ferro-manganese alloy. The MnO2 ore is pre-roasted to convert the MnO2 to lower oxidation state oxides of Mn2O3 and Mn3O4 to prevent violent heat release from aluminothermic reduction of MnO2 [15]. The ore feed requirement is a minimum of 46% Mn and a Mn/Fe ratio of 9, with a P content below 0.12%, and CaF2 is added as a flux. The product alloy composition ranged from 70 to 84% Mn, 13–16% Fe, 1–10% Si, <0.03% Al, and <0.24% P, and the metal yield was 58–64% [15].
An essential aspect of aluminothermic reduction is the optimal separation of the produced alloy from the slag. Since Al2O3 has a high melting point, the slag chemistry must be designed to flux most of the Al2O3. Thus, slag volume can be excessive, and the phase chemistry of the slag will likely influence the ease of subsequent processing for Al(OH)3 formation via hydrometallurgy. Since CaO and Al2O3 form low liquidus compounds and CaO in the slag increases the activity of MnO in the slag to promote the aluminothermic reduction of MnO, the aim slag of CaO-Al2O3 chemistry was applied [7,8]. Most of the Al was leached from CaO-Al2O3 slag in a 10% Na2CO3 solution, reacted at 30–45 °C [18]. A different approach is to use a Na2O-Al2O3-based slag since the NaAlO2 compound can be leached in water at 60 °C [19]. Adequate leaching conditions were identified at a solid–liquid ratio of 1:10 with a leaching time of 60 min at 60 °C. The leachate contained Na+:Al3+ at 1.43:1. Carbonation with CO2 gas bubbled through the solution at 80 °C and resulted in a pH of 12.5–10.5 for 96.5% Al recovery as α-Al(OH)3 (Bayerite) particles of 90% +44 μm and 98.8% alumina grade, suitable as feed to the Hall–Héroult process after calcination to α-Al2O3 [19].
The objective of this work is to produce a medium-carbon Mn-Cr-Fe alloy with a Na2O-fluxed formulation for the circular aluminothermic reduction of manganese ore with chromium metal as the collector metal. A successful slag formulation must achieve high Al2O3 solubility to facilitate adequate alloy–slag separation. It must allow the Al2O3 product to be recovered via hydrometallurgy by forming the desired water-soluble compound, NaAlO2.

2. Materials and Methods

The experimental details in this work are the same as in our previously reported work. In this work, Cr metal is applied as collector metal instead of the Si metal addition applied previously [16]. The addition of Si metal resulted in a high uptake of Si in the alloy, forming a bulk alloy of 1.4% Al, 8.7% Si, 65.8% Mn, 21.8% Fe, 2.2% C at 56% alloy yield.

2.1. Materials

The reaction mixture consisted of manganese ore, coal, metal powders of aluminium and chromium, and lime and sodium silicate as flux. The chemically pure metal powders were sourced as follows: Al (99.7% Al, −1 mm) supplied by Sigma-Aldrich (Johannesburg, South Africa), and Cr (99.0% Cr, −44 µm) provided by Alfa Aesar (Johannesburg, South Africa). The chemically pure sodium silicate is supplied by Sigma-Aldrich (Johannesburg, South Africa), and CaO is provided by Associated Chemical Enterprises (Johannesburg, South Africa). The manganese ore is a pyrolusite (MnO2)-based ore sourced from a small-scale ore body complex in South Africa, and the medium-volatile coal is also sourced from South Africa. The coal contains 22.5% volatile matter, 12% ash, 62.2% fixed carbon, and 3.3% moisture. Table 2 presents the analyses of ore and coal ash. The mixture, based on 100 g of ore, was placed in a graphite crucible and sealed with a graphite lid. The crucible dimensions were 50 mm inner diameter, 70 mm in height, and 7 mm in wall thickness. The lid was recessed by 7 mm to fit the crucible’s inner diameter. The reaction mixtures are summarised in Table 3.

2.2. Methods

2.2.1. Experimental Procedure

The masses of the reaction mixture were weighed and mixed thoroughly in a mixing container. The mixture was transferred into the graphite crucible, and the graphite lid was placed onto the crucible rim. The muffle furnace was pre-heated and soaked for 12 h at the set-point temperature of 1350 °C. The proportional-integral-derivative (PID) controller was used to control the muffle furnace temperature. The aluminothermic reaction consists of placing the graphite crucible and contents into the muffle furnace. From prior experimentation, it was noted that the crucible must be removed from the furnace 2 min after ignition, marked by a flash flame exiting the muffle furnace’s top side-panel joint gaps. Therefore, the reaction mixture was not entirely heated by the muffle furnace, but rather via the exothermic aluminium (aluminothermic) reactions. The ignition time was 6 min after placing the crucible in the furnace. Following a total reaction time of 8 min, the crucible and its contents were removed from the furnace. The lid was then removed, and the molten metal and slag were poured into a cast-iron mould. Upon cooling to room temperature, the poured contents were returned to the graphite crucible for manual separation of metal and slag.

2.2.2. Materials Analyses

The large slag and alloy blobs were sectioned for chemical analysis of the alloy and slag phases using a scanning electron microscope (SEM). The cross-section faces were coated with gold for analysis by the SEM via a Zeiss 540 Ultra FEG (field emission gun) SEM (Zeiss, Oberkochen, Germany) with energy dispersive X-ray spectroscopy (EDX) probe operated at 20 kV. Inductively coupled plasma optical emission spectroscopy (ICP-OES) method using a Perkin Elmer Optima 5300 instrument (Perkin Elmer, Springfield, IL, USA) was used in ore, bulk alloy, and slag analyses. The alloy carbon and sulphur content was analysed by the combustion method using a LECO CS 744 instrument (LECO, St Joseph, MO, USA). A proximate analysis of the coal was conducted in accordance with the South African National Standard (SANS 1726:2011) [20]. The coal ash was analysed by X-ray fluorescence (XRF) spectrometer using an ARL Advant’X Series Sequential IntellipowerTM XRF instrument (Thermo Fisher Scientific, Waltham, MA, USA).

2.2.3. Thermochemical Calculations

The alloy equilibrium phase chemistries were calculated in Thermo-Calc 2023b software, using the SGTE Alloy 4.9 database [21]. The equilibrium phase chemistry of the target slag and the sample D slag was calculated in FactSage, as well as the gas–slag–metal equilibrium for the sample D inputs. The Equlib module in FactSage 7.3 was used with selecting the FToxid database and SGTE alloy database [22].

3. Results

Although the results of sample A with carbon and aluminium added have been shown elsewhere, for comparison, the sample A results are also presented here [16]. Similarly, a photograph of the base case (BC) sample is shown in Figure 1a to confirm that no significant slag or alloy formed at the low initial temperature in the muffle furnace (1350 °C). The magnetic fraction of this sample is shown in Figure 1a, with only sintered material formed and no slag or alloy mass formation. This effect is due to the absence of exothermic heat and fast reduction reactions from aluminothermic reduction. Carbothermic reduction is slower than aluminothermic reduction and is highly endothermic due to the endothermic Boudouard reaction, requiring non-chemical heating from the furnace. Therefore, a much longer dwell time in the furnace would be required to achieve noticeable alloy formation via carbothermic reduction. In contrast, large alloy blobs were effectively separated from the slag in samples A and D, along with some smaller metal droplets, as seen in Figure 1b,c. The alloy composition of the fractured surfaces of the large alloy volumes was analysed by SEM-EDX. A typical analysis area consisted of 0.5 mm × 0.5 mm. Figure 2 and Figure 3 display the EDX element maps and SEM images of example areas comprising the field of view (FOV) from the regions analysed in samples A and D. The sample A alloy in Figure 2 appears to be a homogenous Mn-Fe-Si single-phase alloy. The sample D alloy contains small slivers of Cr in a homogeneous single-phase alloy of Mn-Fe-Si-Cr.
The analyses of the areas are summarised in Table 4 and Table 5. The analyses per area in each sample are closely matched. The maximum variance (σ) of the SEM-EDX analyses for each element is also indicated. The bulk chemistry of each alloy is also displayed in Table 4 and Table 5, specifically, because the SEM-EDX does not accurately analyse for carbon, whilst the LECO combustion analysis of the bulk alloy provides quantitative %C. It is observed that the carbon in Figure 2 and Figure 3 appears as specs on the surface of the sample and does not form part of the bulk alloy. The carbon specs were most likely formed from the decomposition of CO in the product gas as the material cooled down. Significant quantities of CO gas may form as shown in the gas–slag–metal equilibrium calculations in Section 4.3. However, most of the carbon is present in the bulk alloys, with the %C in the bulk sample A alloy as 3.5%, and in the sample D alloy it is 2.2%. Similarly, the Al appears as specs in Figure 2 and Figure 3, although the analyses are at a level of approximately 1% in both samples.

4. Discussion

Although aluminothermic reduction is not considered an equilibrium process, the application of equilibrium phase calculations is useful in investigating the effects of different melting points and chemistries of the target and realised slag and alloy compositions [7,8,9,11]. In the following section, the thermochemical software FactSage 7.3 and Thermo-Calc 2023b are utilised to calculate equilibrium compositions for comparison with the experimental results presented in this work [21,22]. The main reason for not attaining chemical equilibrium in aluminothermic reduction is the high release rate of heat, resulting in short reaction times and thus limited time for process control. In various studies on the application of aluminothermic reduction for different feed materials, it has been demonstrated that the chemical composition and particle size of the feed material significantly influence the aluminothermic reaction rate and extent, thereby determining the maximum attained temperature and the final product proportions and chemistries [11,12,13,14,23,24].
In addition, laboratory studies vary in the reaction atmosphere applied. In some studies, the mixture is reacted under a protective gas atmosphere, such as Argon gas, to eliminate oxygen in the air from reacting with the feed mixture [7,8,9,10,11]. However, it has been shown that some air is required to initiate the reaction in MnO2–Al mixtures since this mixture did not react under Argon gas [14]. In some studies, oxidants other than air may be added deliberately as an additive, or the oxides targeted for the reduction reaction may form the dual purpose of oxidant and metal/alloy product former. Thus, calculating the feed recipe to limit the %Al in the alloy product is not as simple as in most large-scale furnace-based processes since Al is highly reactive to all oxygen sources.

4.1. Alloy Composition

The sample D Cr-Mn-Fe-Si complex alloy has a relatively low %C at 2.2, similar to a MCFeCr alloy in Table 1. In comparison, the sample A alloy contains 3.5% C. Although both ferrochromium and ferromanganese have a high carbon solubility capacity, the presence of silicon in the alloys decreases the solubility limit of carbon [1]. This effect appears to be at play in both alloys A and D at 1.4 and 3.4% Si, respectively. The carbon saturation level for sample A alloy at 1550 °C is 6.5% C, and for the chromium-containing sample D alloy with a higher %Si, the carbon saturation level is 6.9% C. This is compared to the %C shown in Table 4 and Table 5, at 3.5% C in sample A alloy and 2.2% C in sample D alloy.
The equilibrium phase chemistry of the bulk alloy compositions in Table 4 and Table 5 is shown in Figure 4. In Figure 4a, the sample A alloy has a solidus temperature of 1093 °C and a liquidus temperature of 1171 °C. The closeness of these two temperatures results in a narrow solidification temperature range, leading to a rapid setting of the alloy composition. The low liquidus and solidus temperatures, relative to the high temperatures attained in aluminothermic reduction, which can easily reach 3000 °C, allow for an extensive alloy separation time [24]. The rapid incorporation of the added chromium metal powders indicates that the aluminothermic reaction temperature was sufficiently high to melt the chromium metal, which has a melting point of 1857 °C. As shown in Figure 4b, the solidus temperature of the sample D alloy is 1026 °C, and the liquidus temperature is 1373 °C. The higher liquidus temperature compared to the sample A liquidus temperature may work against effective bulk alloy separation in sample D.

4.2. Slag Composition

The aim slag composition was selected to maintain a low liquidus temperature in the slag, even as a high level of Al2O3 uptake occurs from aluminothermic reduction reactions, such as reaction (1):
3(MnO) + 2(Al) = <Al2O3> + 3(Mn)
< > = solid; ( ) = liquid
Comparison of the average SEM-EDX slag analyses and bulk slag analyses in Table 6 indicates some alloy entrapment because zero iron content is expected in the slag due to the highly reducing conditions in aluminothermic smelting. Especially for sample D, with added Cr metal, the Cr in the slag is likely metallic, as confirmed by the SEM-EDX analyses in which no Cr-oxide was detected. Mass balance calculations based on the input masses and the output masses of slag and alloy indicate that the alloy mass in the slag and the overall alloy recovery numbers are as shown in Table 7. A comparison of the numbers for sample A versus sample D, at 43% versus 68% alloy yield, indicates that the addition of Cr as a collector metal served its intended purpose, increasing alloy collection and separation. Element accounting percentages shown in Table 8 indicate a good accounting of Fe and Cr, with some loss of Mn, Si, and Al to the gas due to volatilisation of metals at the high reaction temperatures expected in thermic reduction. At an industrial scale, various typical gas- and particulate-capturing equipment options are available, such as a reaction chamber hood with a positive off-gas pressure to counter volatilisation and capture fumes for recycling [3].
Comparison of the SEM-EDX slag analyses with the target analysis in Table 6 reveals lower percentages of CaO and Na2O, and higher levels of Al2O3, in the experimental results. The effect of this higher Al2O3 content on the slag phase chemistry was investigated by comparing the slag phase chemistry of slag D to that of the target slag.
The cooling curve of the target slag is shown in Figure 5a. It is seen that the slag liquidus temperature is 1373 °C. The slag solidus is relatively low at 1002 °C, allowing ample time for the alloy to separate from the slag upon cooling. The cooling curve for the EDX analysis of slag D from Table 6 is shown in Figure 5b, indicating the formation of spinel and corundum precipitation phases upon cooling. The liquidus temperature is 1647 °C. Therefore, for good slag and alloy separation, the reaction mass temperature must be at least close to the liquidus temperature. As discussed in [16], the post-tap slag can be modified with additional Na2O-flux to attain the desired slag phase chemistry, with a high NaAlO2 phase content, since high residual heat content remains after the aluminothermic reaction.

4.3. Gas–Slag–Metal Equilibrium Thermochemistry

Chemical equilibrium is not expected in the aluminothermic reduction process because of the rapid heat release from aluminium oxidation. To test this expectation, a thermochemistry analysis was conducted. The gas–slag–metal equilibrium for the feed mixture inputs was calculated at temperatures of 1650 °C to 1900 °C. The calculated equilibrium end-point alloy and slag analyses are compared to the experimentally determined values as shown in Figure 6a–d. It is observed that the alloy compositions of %Mn, %Cr, and %Fe are close to equilibrium at 1900 °C. However, the reductant species of %Al, %Si, and %C differ significantly from their equilibrium values at 1900 °C. Especially, the %Al is predicted to be close to zero at equilibrium, whilst this is not the case in the produced alloy. Although a limited quantity of carbon is added to the feed mixture, it is seen in Figure 6a that the equilibrium alloy carbon content varies widely from 4.4% C at 1650 °C to 1.4% C at 1900 °C. Figure 6a also shows the inverse relationship between %C and %Si.
The slag analyses displayed in Figure 6c,d show larger differences between equilibrium-predicted values and the experimentally measured values, in large part due to the total oxidation of Al predicted in the equilibrium calculations, as well as the reduction of BaO into the alloy. In addition, the equilibrium calculations predicted a significant loss of Na to the gas phase, whilst the experimental loss appears to be much less. This is a crucial aspect to be able to retain sufficient Na2O in the slag for fluxing, enabling adequate alloy–slag separation. The main gas compounds are summarised in Figure 6e, which predicts gas-phase losses of Na and Mn. As already mentioned above, the process application on an industrial scale opens equipment possibilities such as the off-gas system and positive furnace pressure control to limit and capture volatiles. In addition, at an industrial scale, a semi-continuous loading procedure is possible, which lowers top temperatures and facilitates the capture of volatiles in the reaction mixture [3].
The gas–slag–metal equilibrium calculation results shown in Figure 6 correspond somewhat to the empirically determined results of alloy and slag chemistry. However, a crucial discrepancy arises from the 1.5% Al observed in the experiment alloy product, which was not predicted in the equilibrium calculations. The reason for this difference is most likely the dwindling chemical reaction driving force as the reaction completion is approached, according to Le Chatelier’s principle. The carbothermic reduction of MnO from slag does not reach equilibrium and depends on the activity differential between the MnO in the reactant phase and the equilibrium MnO activity value. The reaction interface area is the primary uncertain variable [25]. The ore contains limited fluxing compounds, and, therefore, the activity of MnO will be close to unity, as MnO has a high melting point of 1945 °C, and will require time to dissolve into the added flux compounds. To illustrate the likely activity ranges at the start and end of the aluminothermy process, the activity values are presented in Table 9 for a temperature of 1900 °C. The oxide melt was calculated as a mixture of ore and flux compounds forming a high-MnO slag with a liquidus temperature calculated as 1730 °C, resulting in the following composition: 58.9% MnO, 14.5% SiO2, 14.5% CaO, 2.5% Al2O3, 9.6% Na2O. It is observed that the chemical driving force for reaction (1) is high, as the initial activities of the reactants, Al and MnO, are significantly higher than their equilibrium activity values. The formation of Al2O3 diffusion barriers on the surface of aluminium particles, either solid or molten, is unlikely in this reaction system because the fluxing agents were explicitly selected to form a slag with high Al2O3 solubility. Even in the absence of a slag product, it was shown that a continuous Al2O3 product layer could not form in aluminothermy of granular materials [26].
Considering that the gas–slag–metal equilibrium calculations were made for a closed system with no air added as reactant, it is clear that the equilibrium calculation may provide, at best, a ballpark number for the required Al addition mass. To illustrate this effect, a gas–slag–metal equilibrium calculation was performed at 1900 °C for different Al reductant addition levels, ranging from ±20% to the experimental value of 30 g of Al, corresponding to 24 g and 36 g of Al addition. The equilibrium calculation results are summarised in Figure 7a,b as the equilibrium alloy and slag compositions.
Figure 7a indicates that, in the equilibrium calculation, all Al metal is reacted with MnO and SiO2, irrespective of the grams of Al added in the range considered here. This effect is clearly visible with 7% Si in the alloy when +20% Al is added. The attendant change in slag composition is drastic, as shown in Figure 7b, indicating an excessively increased Al2O3 content to 72% and a lowered SiO2 content to 6%, likely resulting in a slag of low fluidity. Therefore, the equilibrium calculation is only useful following experimental verification and may provide trends in chemical changes for estimated temperatures. Precise recipe calculation seems unlikely.
In summary, it is clear from this work that the applied sodium-fluxed slag is a practical approach to enable good alloy–slag separation from one-step aluminothermic reduction of manganese ore with chromium metal as collector metal. A medium-carbon complex alloy of Mn-Cr-Fe-Si can be produced through a reaction design, and the resulting suitable sodium-fluxed high-alumina slag can be used for circular processing to recover aluminium for the Hall–Héroult electrochemical process.

5. Conclusions

This work demonstrates the empirical application of a sodium-fluxed aluminothermic reduction system for MnO2-type ores in a single step. The addition of a small quantity of coal as a reductant facilitates rapid pre-reduction to the MnO level, thereby eliminating the need for an extra step of pre-roasting the MnO2 ore.
Chromium metal is used as a collector metal to increase the alloy yield to 68%, from 43% in the absence of the chromium collector metal. The chromium collector metal improved alloy–slag separation. The medium-carbon complex alloy product contains 57% Mn, 18%Cr, 18% Fe, 3.4% Si, 1.5% Al, and 2.2% C. This Mn-Cr containing complex alloy can be applied as an efficient alloying addition in steelmaking because it melts at a lower temperature than MCFeCr of the same carbon content (2.2%C).
The applied Na2O-fluxed feed mixture formulation enables the formation of the water-soluble NaAlO2 compound, allowing for the recycling of Al2O3 through hydrometallurgical processing via the Bayer process, to the Hall–Héroult electrochemical process, which is used to produce aluminium.
Gas–slag–metal equilibrium calculations show that precise recipe calculation is not achieved through such calculations because the Al reactant requirement does not precisely follow equilibrium. The equilibrium calculations provide temperature estimates and trends in chemical changes. Therefore, theoretical feed mixture formulations must be tested through empirical applications as shown in this work.

Author Contributions

F.D.B. conceptualised the work; F.D.B. and T.C. executed the experiments together, interpreted the data together, and prepared the manuscript together. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded in part by the University of Pretoria.

Data Availability Statement

The original contributions presented in this study are included in the article. Further inquiries can be directed to the corresponding author.

Acknowledgments

The authors are grateful to Coenraad Snyman at the Laboratory for Microscopy and Microanalysis at the University of Pretoria for his advice and assistance on the SEM imaging and analysis in this work.

Conflicts of Interest

The authors declare no conflicts of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.

Abbreviations

The following abbreviations are used in this manuscript:
HCFeCrHigh–carbon ferrochromium
MCFeCrMedium-carbon ferrochromium
LCFeCrLow-Carbon ferrochromium
FeCrMnFerrochrome-manganese
FeCrSiMnFerrochrome-siliconmanganese
PIDProportional-integral-derivative
SEM Scanning electron microscope
EDXEnergy dispersive X-ray spectroscopy
ICP-OESInductively coupled plasma optical emission spectroscopy
XRFX-ray fluorescence

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Figure 1. (a) Photographs of magnetic fraction from Sample BC; (b) easily separated alloy from Sample A; (c) easily separated alloy from Sample D.
Figure 1. (a) Photographs of magnetic fraction from Sample BC; (b) easily separated alloy from Sample A; (c) easily separated alloy from Sample D.
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Figure 2. (a): SEM image (×500) of analysed area (number 1) in Sample A; (b): EDX map of area in (a).
Figure 2. (a): SEM image (×500) of analysed area (number 1) in Sample A; (b): EDX map of area in (a).
Suschem 06 00030 g002
Figure 3. (a): SEM image (×500) of analysed area (number 6) in Sample D; (b): EDX map of area in (a).
Figure 3. (a): SEM image (×500) of analysed area (number 6) in Sample D; (b): EDX map of area in (a).
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Figure 4. Phase chemistry of alloy: (a) Sample A alloy; (b) Sample D alloy: Calculated in Thermo-Calc [21].
Figure 4. Phase chemistry of alloy: (a) Sample A alloy; (b) Sample D alloy: Calculated in Thermo-Calc [21].
Suschem 06 00030 g004
Figure 5. (a): Target slag phase chemistry calculated in FactSage [22]. (b): Slag D phase chemistry calculated in FactSage [22].
Figure 5. (a): Target slag phase chemistry calculated in FactSage [22]. (b): Slag D phase chemistry calculated in FactSage [22].
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Figure 6. (a): Sample D alloy composition vs. gas–slag–metal equilibrium. (b): Sample D alloy composition vs. gas–slag–metal equilibrium. (c): Sample D slag composition vs. gas–slag–metal equilibrium. (d): Sample D slag composition vs. gas–slag–metal equilibrium. (e): Sample D gas in gas–slag–metal equilibrium from FactSage [22].
Figure 6. (a): Sample D alloy composition vs. gas–slag–metal equilibrium. (b): Sample D alloy composition vs. gas–slag–metal equilibrium. (c): Sample D slag composition vs. gas–slag–metal equilibrium. (d): Sample D slag composition vs. gas–slag–metal equilibrium. (e): Sample D gas in gas–slag–metal equilibrium from FactSage [22].
Suschem 06 00030 g006aSuschem 06 00030 g006b
Figure 7. (a): Experimental vs. equilibrium alloy compositions at different Al levels (1900 °C). (b): Experimental vs. equilibrium slag compositions at different Al levels (1900 °C).
Figure 7. (a): Experimental vs. equilibrium alloy compositions at different Al levels (1900 °C). (b): Experimental vs. equilibrium slag compositions at different Al levels (1900 °C).
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Table 1. Ferromanganese alloy compositions (mass%): n.s. = not specified [1,2,3].
Table 1. Ferromanganese alloy compositions (mass%): n.s. = not specified [1,2,3].
%Cr%Si%C%S%P%Al%MnBalance
HCFeCr (C) [2]62–72<3.04.0–9.5<0.060<0.03000Fe
MCFeCr [1]65–75<1.50.5–4.0<0.050<0.03000Fe
LCFeCr (D) [2]67–75<1.0<0.75 <0.025<0.03000Fe
Charge chrome [1]53–586–35–8n.s.n.s.00Fe
FeCrAl [3]48–520.5–100018–220Fe
FeCrMn [3]31–39<1.6<0.0500036–44Fe
FeCrSiMn [3]20–2520–30<0.05<0.05<0.02030–35Fe
Table 2. Bulk chemical composition of manganese ore and coal ash (mass%).
Table 2. Bulk chemical composition of manganese ore and coal ash (mass%).
%FeO%MnO%Cr2O3%V2O5%TiO2%CaO%K2O%P2O5%SiO2%Al2O3%MgO%Na2O%BaO
Ore10.7061.590.030.040.050.230.210.015.432.610.110.001.85
Ash1.510.020.050.052.162.460.511.1951.4439.350.680.300.27
Table 3. Reaction mixtures (grams).
Table 3. Reaction mixtures (grams).
OreCoalNa2O·SiO2CaOAlCr
Base case (BC)10027201500
A100102015300
D1001020153010
Table 4. EDS analyses of Sample A alloy (mass%); n.a. = not available; n.d. = not detected.
Table 4. EDS analyses of Sample A alloy (mass%); n.a. = not available; n.d. = not detected.
Area%Al%Si%Mn%Fe%Ca%V%S%C
10.62.469.426.90.10.60.0n.a.
20.02.268.828.30.20.60.0n.a.
31.62.368.227.00.20.60.0n.a.
40.82.168.128.30.10.60.0n.a.
51.41.867.528.60.20.60.0n.a.
Average0.92.268.427.80.20.60.0n.a.
Maximum σ0.010.010.060.030.000.01n.d.
Bulk Alloy0.41.466.128.00.050.400.033.5
Table 5. EDS analyses of Sample D alloy (mass%); n.a. = not available; n.d. = not detected.
Table 5. EDS analyses of Sample D alloy (mass%); n.a. = not available; n.d. = not detected.
Area%Al%Si%Mn%Fe%Ca%Cr%S%C
61.22.356.518.20.121.70.0n.a.
71.12.257.118.40.121.10.0n.a.
81.12.257.318.50.120.70.0n.a.
91.12.357.118.70.120.70.0n.a.
101.12.057.418.00.021.30.0n.a.
111.42.756.418.50.020.90.0n.a.
Average1.22.357.018.40.121.10.0n.a.
Maximum σ0.010.010.060.030.010.03n.d.
Bulk Alloy1.53.456.818.20.0217.70.122.2
Table 6. Target vs. test slag analyses (SEM Average) and bulk chemistry.
Table 6. Target vs. test slag analyses (SEM Average) and bulk chemistry.
%Al2O3%SiO2%MnO%FeO%CaO%Na2O%BaO%CrOB2 =
%CaO/%SiO2
Target slag3917140.01711201.0
A: EDX54.59.120.00.08.05.52.800.9
A: bulk53.212.327.62.47.14.61.500.6
A: Corrected52.111.922.70.07.04.51.500.6
D: EDX59.39.012.60.010.56.02.701.2
D: bulk51.011.026.53.19.34.81.54.50.8
D: Corrected54.710.717.50.010.05.11.60.00.9
Table 7. Mass balance numbers (grams unless indicated differently).
Table 7. Mass balance numbers (grams unless indicated differently).
Alloy Mn in
Alloy
Fe in
Alloy
Slag Fe in
Slag
Alloy
in Slag
Mn in
Ore
Fe in
Ore
Mn+Fe
+Cr
%Alloy Yield
A18.712.45.379.11.55.347.78.356.043
D30.617.45.6106.82.513.947.78.366.068
Table 8. Mass accounting of primary elements (percent).
Table 8. Mass accounting of primary elements (percent).
%Fe %Mn%Si%Al%Cr
Sample A81675862none
Sample D9782788091
Table 9. Activities in slag and alloy at 1900 °C (liquid reference state).
Table 9. Activities in slag and alloy at 1900 °C (liquid reference state).
Al2O3 MnOSiO2AlMnSi
Oxide melt3.46 × 10−50.7487.62 × 10−41.0<<0.0001<<0.0001
Equilibrium0.3170.0848.90 × 10−31.12 × 10−30.4842.69 × 10−3
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Coetsee, T.; De Bruin, F. Sodium-Oxide Fluxed Aluminothermic Reduction of Manganese Ore for a Circular Economy: Cr Collector Metal Application. Sustain. Chem. 2025, 6, 30. https://doi.org/10.3390/suschem6030030

AMA Style

Coetsee T, De Bruin F. Sodium-Oxide Fluxed Aluminothermic Reduction of Manganese Ore for a Circular Economy: Cr Collector Metal Application. Sustainable Chemistry. 2025; 6(3):30. https://doi.org/10.3390/suschem6030030

Chicago/Turabian Style

Coetsee, Theresa, and Frederik De Bruin. 2025. "Sodium-Oxide Fluxed Aluminothermic Reduction of Manganese Ore for a Circular Economy: Cr Collector Metal Application" Sustainable Chemistry 6, no. 3: 30. https://doi.org/10.3390/suschem6030030

APA Style

Coetsee, T., & De Bruin, F. (2025). Sodium-Oxide Fluxed Aluminothermic Reduction of Manganese Ore for a Circular Economy: Cr Collector Metal Application. Sustainable Chemistry, 6(3), 30. https://doi.org/10.3390/suschem6030030

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