Recovery of Metal Values from Bauxite Residue/Red Mud: A Review
Suchita Rai1*, Prachiprava Pradhan1, Amar Padole1, Anupam Agnihotri1
Jawaharlal Nehru Aluminium Research Development and Design Centre, Nagpur, Maharashtra, 440023, India.
*Corresponding Author E-mail: suchitarai@jnarddc.gov.in, suchitarai1968@gmail.com
ABSTRACT:
Red mud/bauxite residue is an industrial waste product of Bayer's process and because of its alkalinity poses a significant environmental problem. However, it is a potential source from which valuable metals such as iron, alumina, titanium, caustic soda, gallium and rare earth elements (REEs) especially scandium can be extracted. The aim of this article is to systematically review, research on metal and rare earth extraction from red mud from the year 2000 to 2024. Extraction methods by hydrometallurgy, pyrometallurgy and bioleaching have been reviewed in the paper. It is seen that in any extraction process, the different operational parameters, such as reagent concentrations, temperature and pH influence the extraction efficiency of metals and rare earths. The recovery challenges and limitations presented in this document highlights, above all, the underlying complexities. The paper also discusses the problems associated with the recovery processes, particularly because of the complex composition of the red mud.
KEYWORDS: Red Mud/ Bauxite Residue, Metal Extraction, Recovery, Rare Earth Elements, Hydrometallurgy, Pyrometallurgy, Acid Leaching, Bioleaching, Sustainability.
INTRODUCTION:
Bauxite residue/ Red mud (RM)is a highly alkaline by- product produced during the extraction of purified aluminum hydroxide from bauxite ore. Depending upon the bauxite processed and the technology employed, production of one tonne of aluminum oxide generates 1–2.25 tonnes of RM (Paramguru, Rath, and Misra 2004). The large volume of red mud produced annually poses significant environmental risks, including soil and water pollution (Li et al. 2024). However, it also presents an opportunity for metal recovery, and is an alternative source of valuable metals (Kong et al. 2022). Red mud is a promising alternative for metal extraction such as alumina, caustic soda, iron, titanium, including rare earth elements (REEs) such as scandium and gallium, making it a strong contender for metal extraction. Red mud primarily consists of 30-60% iron oxide (Fe2O3) and 10-20% alumina (Al2O3). It also contains silica (SiO2) at 3-50%, titanium oxide (TiO2) in trace amounts up to 25%, sodium oxide (Na2O) at 2-10%, and calcium oxide (CaO) ranging from 2-8% (Paramguru R.K 2004).
The red mud produced by Indian alumina refineries has the chemical composition of Iron Oxide (Fe2O3) 40-62%, Alumina (Al2O3) 16-23%, Silica (SiO2) 4-9%, Titanium Oxide (TiO2) 4-16%, Sodium Oxide (Na2O) 3-6.5%, Calcium Oxide (CaO) 0.5-3% (Rai et al. 2020).
Extracting valuable metals from red mud presents a solution to multiple challenges, such as lowering waste disposal expenses, preserving natural resources, and reducing environmental pollution. Moreover, the properties of rare earth elements are of great interest because of their fundamental applications in a number of advanced technological processes. Several techniques for metals extraction from red mud include carbothermal reduction, smelting reduction, acid leaching, magnetic separation, and hydrothermal techniques (Khanna et al. 2022). These methods have shown promise in recovering iron, REEs, and other valuable metals from red mud.
This review paper aims to examine the present status of metal recovery from red mud, with a focus on the technical, environmental, and economic aspects of this processes. We will examine the challenges and opportunities that are linked to metal recovery from red mud and discuss the potential applications of these technologies. This paper reviews and discusses the research conducted from the year 2000 to the present.
RECOVERY OF METAL:
Recovery of Iron from Red Mud:
Various methods have been developed by researchers for recovery of iron from Bayer red mud such as physical sorting by magnetic separation, hydrometallurgical recovery, pyrometallurgical recovery. Physical sorting method such as magnetic separation generally carried out with high iron content red mud does not involve chemical reaction. (X. F. Li et al. 2023). Iron in red mud mainly consists of two phases, namely hematite (Fe2O3) and goethite (FeOOH) (Klauber, Gräfe, and Power 2011).
In one of the studies, (Liu and Naidu 2014) concluded that, a combined process was much preferred over the single process method which can achieve multiple additional values from red mud. Table 1 reviews the works carried out for recovery of iron from red mud.
Table 1: Iron recovery from red mud (national and international context)
|
Constituents used |
Experimental conditions (optimal condition) |
Observations |
Method used for extraction |
Key findings |
Country |
Reference |
|
Red Mud, sulphuric acid |
RM calcined at 873 K, 6M H₂SO₄ |
Follows first-order kinetics |
Acid leaching |
97.46% Fe, 64.40% Al recovered |
Turkey |
(Uzun and Gülfen 2007) |
|
Red mud |
Reduction roasting, magnetic separation |
Original Fe₂O₃ content in red mud: 27.93% |
Magnetic separation |
89.05% Fe in magnetised separated part, 97.69% metallization |
China |
(Liu, Yang, and Xiao 2008). |
|
Red mud, carbon, soda ash, lime |
Preheated at 800°C for 20 min and then sinter at 600°C, 20 min |
Ferric oxide can completely reduce with increase in amount of carbon added |
Pyrometallurgy |
Alumina recovery rate: 89.71%, and Fe recovery rate: 60.67% |
China |
(LI et al. 2009) |
|
Red mud, carbon, lime, calcium, calcium carbonate, magnesium carbonate |
Additive to red mud ratio: 6:100, carbon powder to red mud ratio :18:100, temp. 1300°C, 110 min. |
Building materials were prepared from silicate residues after successful Fe recovery |
Direct reduction roasting and magnetic Separation |
88.77% Fe in concentrate and 81.40% recovery ratio |
China |
(W. Liu, Yang, and Xiao 2009) |
|
Red mud, sulphuric acid |
383 K (110°C), H₂SO₄ leaching |
Kinetic study carried out. Controlled by intra-particle diffusion |
Acid leaching |
maximum Fe (III) leaching from bauxite residue at 383 K |
China |
(Z. R. Liu et al. 2009) |
|
Red mud, sodium carbonate, calcium fluoride |
1150°C, coal-based reduction, 180 min, 3% Na₂CO₃ and 3% CaF₂ added |
Na2CO3 and CaF2 increases reducing reaction activity of FeO |
Pyrometallurgy |
grade of concentrate to 89.57%. metallization increases to 91.2% grade with addition of Na2CO3, CaF2. |
China |
(Huang et al. 2010) |
|
Red mud |
High gradient superconducting magnetic separation (HGSMS) for fine particles (<100 μm and <10 μm) |
Fe-element intergrowth observed |
Magnetic Separation |
58% Fe2O3 increased to 65% oxide in <100 μm red mud, 29 to 45% Fe2O3 in <10 μm red mud |
China |
(Li et al. 2011) |
|
Red mud, magnesium chloride, sodium acetate |
Sintering at 800°C-1000°C in a resistance type vertical tube furnace, 1-4 days |
Varied effects on metal extractability |
Pyrometallurgy |
Increased Fe and Al leachability
|
India |
(Ghosh et al. 2011) |
|
Red mud, graphite (99 % Cfix) Red mud of NALCO and Vedanta |
Smelting in 35 kW DC extended arc plasma reactor, reduction time 15 min, reductant 11% (graphite powder), limestone, dolomite, fluorspar and CaCO3 used as fluxes |
Study of recovery of pig iron from dry red mud, Reductant concentration effect studied |
Pyrometallurgy, plasma smelting |
Fe recovery of 65-70% with NALCO red mud and 79% with Vedanta red mud, reduction rate follows first-order kinetics |
India |
(Rath et al. 2011) (Rath et al. 2013) (Jayasankar et al. 2012) |
|
Red mud, sodium carbonate, soft coal |
8% Na₂CO₃, 1050°C, 80 min, magnetic separation |
overall iron recovery rate is 95.76%. |
Pyrometallurgy |
90.87% Fe in final product |
China |
(Zhu et al. 2012) |
|
Red mud, anthracite, lime stone |
Reduction at 1400°C, 30 min., molar ratio of 1.6, and basicity of 1.0. |
Temperature is identified as the strongest factor influencing the metallization rate |
Reduction roasting |
Chemical analysis showed that the total iron content in the nuggets is higher than in pig iron |
China |
(Guo et al. 2013) |
|
Red mud, lignite (30.15% Cfix) |
Microwave reductive roasting using lignite, followed by wet magnetic separation |
Hematite to magnetite to iron transformation |
Pyrometallurgy |
Fe2O3 % increased from original 43% to 50% with 69.3 % metallization, 35.15 wt.% total Fe in magnetic concentrate |
Greece |
(Samouhos et al. 2013) |
|
Red mud, sodium sulphate and CaO added as additives, bituminous coal as reductant |
9% sodium sulphate, 9.46 % lime and 16 % coal, 1423 K (1150°C), 80 min |
Na₂SO₄ improved Fe grain growth |
Pyrometallurgy |
Original Fe2O3 is 36%, 90.28 % Fe, 94.87 % metallization and 92.14% of iron recovery |
China |
(Chun et al. 2014) |
|
Pyrite, red mud |
30 g red mud-containing 9.24% of iron (13.2% Fe2O3) was mixed with 0.74 g pyrite, 600°C, 30 min, N₂ atmosphere |
Hematite reduced to magnetite |
Pyrometallurgy |
4.5 g with 36.9% magnetically separated, Efficient Fe transformation and separation |
China |
(Liu et al. 2014)
|
|
Red mud, iron scraps, oxalic acid, H2SO4, HCl, HNO3, acetic acid, sodium acetate, potassium permanganate |
Selective leach with oxalic acid, red mud/oxalic acid/H₂SO₄ is 3:3:2, 95 °C,90 min at L/S ratio: 16:1 mL/g |
High Fe recovery rate |
Hydrometallurgy |
Leaching with oxalic acid, reduction of iron in the leached solution using iron scraps, precipitation of FeC2O4.2H2O, separation of oxalic acid and iron using H2SO4. |
China |
(Yang et al. 2015) |
|
Red mud, reducing agent |
Reduction roasting, magnetic separation |
Nanotechnology enhanced Fe enrichment |
Pyrometallurgy |
Over 70% Fe recovery |
India |
(Biswal 2018) |
|
Basic oxygen furnace (BOF) slag, red mud, lignite coke, Lime
|
Combined carbothermic reduction, 1500°C, 1h, BOF slag, lignite coke |
Low residual Fe in slag |
Pyrometallurgy |
High Fe extraction, dilution slags with high Al₂O₃ content with enrichment of Ti |
Red mud (Greece) and BOF slag (Germany) |
(Xakalashe and Friedrich 2018) |
|
Red mud, CO, CO2, N2 |
Reduction at 540±10°C, PCO/PCO2=1(0.070 atm (bar) ±0.001 atm (bar), 30min |
Approximately 98% magnetite could be recovered |
Reduction followed by magnetic separation |
~60% grade of the magnetite achieved |
America |
(Gostu 2018) |
|
Red mud, laterite nickel ore |
Reduction roasting followed by magnetic separation |
When Ni added up to 0.6% white microstructure turn into grey |
Carbothermic reduction followed my magnetic separation |
Red mud grey cast iron provides better strength and corrosion resistance |
China |
(Zeng 2018) |
|
Red Mud, reductants such as coal dust, sugarcane bagasse, spent pot lining
|
Magnetic separation, carbon-containing wastes as reducing agent |
Comprehensive study on % recovery |
Magnetic separation |
80% recovery with hydro-cyclone and iron (Fe2O3) enrichment from 52% to 70% by physical separation technique |
India |
(Rai et al. 2019) |
|
Red mud, Sichuan coke (Cfix:84.4%), chlorinating agent (sodium chloride) |
Roasting at 1100°C for 60 min, mass ratio: 100:15:15:10 (red mud/sodium chloride/ coke/sodium sulfate) |
Improved Fe recovery from red mud |
Pyrometallurgy |
92.78% Fe recovery rate, magnetic concentrate sorting index with TFe 82.13% |
China |
(Ding et al. 2020) |
|
Red Mud, Zn (NO3)2·6H2O, H2O2, Na2CO3, Al (NO3)3·9H2O, NaOH |
Zn (NO3)2·6H2O to RM is 2:1, 6h dry milling, water dosage 2 mL, 250 rpm. |
Created Fe₂O₃/Zn-Al layered double hydroxide (LDH) |
Mechano- chemical synthesis |
Successfully synthesized Fe2O3/Zn-Al layered double hydroxide |
China |
(Li et al. 2020) |
|
Red mud, coke, sodium sulphate, potassium chloride
|
Ratio of Red mud: potassium chloride: coke: sodium sulfate is 100:13:10:8 and roasted at 1100°C, 65 min |
Enhanced Fe extraction |
Pyrometallurgy |
85.43% Fe recovery with total iron grade of 79.32% |
China |
(Wei et al. 2021) |
|
Red mud, lime milk |
Red mud treated with 90°C for 180 min to liberate sodium. carbothermic reduction with coal at 1000-1200°C, magnetic separation |
Effective extraction process |
Reduction of iron and magnetic Separation |
Successful Fe extraction from red mud |
Russia |
(Zinoveev et al. 2021) |
|
Red mud, CaF2, calcified slag, coking coal
|
1550°C, alkalinity 1.1, carbon ratio 1.1, 30 min, 3% CaF₂ |
High efficiency in Fe recovery. Calcified iron tailings extracted from red mud can be used for making aluminate cement. |
Pyrometallurgy |
90.06% Fe recovery and 93.76% mass fraction of Fe in the metal. |
China |
(Yang et al. 2022) |
|
Red mud, magnesium oxide, carbon dioxide, calcium sulfate, sodium carbonate, calcium oxide
|
MgO mixed with red mud at 1100°C to form MgFe2O4. NaAlO2 leached out. ATH precipitated. Separated. Magnetic separation carried out. MgO/(Fe₂O₃ + MgO) ratio of 14.89% at 1100°C with Ca/ (Si + Ti): 1.8 |
Efficient and environment friendly extraction |
Magnetization sintering process |
67.54% and 73.01% of recovery rate of Fe and Al |
China |
(Chen et al. 2023) |
Various techniques are used to recover iron from Bayer red mud, including acid leaching, pyrometallurgy, hydrometallurgy and magnetic separation, with pyrometallurgy being the predominant method. Iron recovery rates are generally impressive, often achieving 70-90% or higher under optimal circumstances, highlighting the application of red mud as a significant secondary source of iron. Research on iron recovery from red mud is being pursued worldwide, with notable contributions from countries like China, India, and Turkey, reflecting a broad interest in this area.
Recovery of Alumina and Caustic Soda:
Red mud also contains valuables such as Al2O3 (14-17%) and caustic soda (5-6%) which can be partially recovered. Studies show that Bayer process modifies the aluminum minerals, so using weak acids most of the Al can be separately extracted from mud while the mobilization of iron is not significant (Zsolt and Lakatos 2009). Table 2 reviews the work carried out for recovery of alumina and caustic soda from red mud in India and abroad.
Table 2. Recovery of Alumina and caustic soda from red mud (national and international context)
|
Constituents used |
Observations |
Method of Extraction |
Key Findings |
Country |
Reference |
|
|
Red mud, sodium hydroxide, lime |
45% NaOH solution, CaO: red mud ratio is 0.25, 200°C, 3.5h for Al2O3 extraction. 7% NaOH solution at 170°C for 2 hrs for Na2O extraction |
Sodium aluminate hydrate crystallized |
Mild Hydro- chemical method |
87.8% Al2O3, 96.4% Na2O extracted |
China |
(Zhong, Zhang, and Zhang 2009) |
|
Red mud, fungi (A. Niger and P. Simplicissimum) |
Biological leaching with fungi
|
Indigenous specimen fungi most efficient |
Biological leaching |
2082 mg Al2O3/L solubilized at 15% pulp density of red mud |
Iran |
(Ghorbani, Oliazadeh, and Shahverdi 2009) |
|
Red mud, CaCO3, Na2CO3 |
Ratio of red mud: CaCO3: Na2CO3 in mole ratio of 1:0.20:0.25. 1100°C, 4h; leaching with 80 g/L 1h, 105°C |
Na2CaSiO4, Ca2SiO4, CaTiO3 and Ca2Fe2O5 formation enhance the alumina extraction efficiency |
Hydrometallurgy |
97.64% alumina extraction efficiency |
India |
(Shib and Meher 2016) |
|
Red mud, NaOH, CaO, CO2 gas |
Calcification-carbonation method |
High recovery rate of alkali and alumina |
Calcification-carbonation method |
75% alumina extraction with 95.2% Na2O recovered |
China |
(Zhu et al. 2016) |
|
Red mud |
The effect of cooling methods of furnace, air, water, liquid N2 studied on roasted red mud |
Specific surface area increases from 1.898 to 2.177 m2 ·cm-3 |
Hydrometallurgy |
Nearly 25% total sodium recovery |
China |
(Liu et al. 2017) |
|
Red mud, citric acid, |
Leaching with citric acid dosage 15%, liquid-to-solid ratio 7 mL/g, 100°C, 300 rpm, 120 min. |
Internal diffusion controlled dealkalization process |
Acid leaching |
The dealkalization rate was > 95% |
China |
(Li, Zhu, and Tang 2017) |
|
Red mud, lime, CO2 gas |
Calcification-carbonisation process |
After Al2O3 and Na2O extraction, residue can be used in cement. It also meets the requirement of soil in terms of alkalinity salinity and other soil properties |
calcification-carbonisation process |
Alkali content reduced to less than 0.3%and 46.5% alumina extraction |
China |
(Wang et al. 2018) |
|
Red mud, sodium carbonate, coal, hydrochloric acid, |
Magnetic separation roasting (1050 °C, 2 h) leaching of non-magnetic phase with 6M HCl, 90°C, 2h |
High purity alumina extracted |
Magnetic Separation |
20.66% alumina extracted |
Indonesia |
(Suprapto et al. 2018) |
|
Red mud and calcified slag |
Wet grinding of calcified slag |
Milling condition established. Effect of wet grinding studied. |
Calcification-Carbonization |
The process improved carbonisation efficiency and alumina extraction. |
China |
(Liu et al. 2020) |
|
Red mud, sodium hydroxide |
Mechanical activation, Calcification-carbonization with phase transformation |
Milling conditions of calcified slag studied. Alumina extraction ratio increased |
Calcification-carbonization |
Alumina extraction increased from 32.9% to 43.1% |
China |
(Liu, Liu, and Zhang 2019) |
|
Red mud, H2SO4, waste ammonia, iron powder |
Hydrothermal reaction 40% H2SO4, 110°C, 5h fractional precipitation |
Effective separation of Fe and Al with lower leaching of Ti and Si |
Fractional precipitation process |
>90% Al and Fe extraction with 45% and 95% purity resp. |
China |
(Yu et al. 2020) |
The above table outlines techniques for the extraction of alumina (Al2O3) and caustic soda (Na2O) from various sources, highlighting hydrometallurgy, calcification-carbonation, and bioleaching as prevalent methods. The efficiency of extraction for both alumina and caustic soda shows significant variation, with certain techniques reporting high recovery rates, such as a study from China that achieved 96.4% alumina extraction, and 95.2 % alkali recovered. Many of these methods aim to recover alumina and caustic soda concurrently, underscoring the significance of effectively extracting both substances. Global research efforts are underway regarding the extraction of alumina and caustic soda, mainly in China.
Recovery of Titanium Dioxide:
Titanium in bauxite primarily occurs in the forms of anatase or rutile (TiO2). The titanium compounds are predominantly insoluble, leading to their accumulation in red mud, where the titanium content ranges from trace amounts up to 25% by weight. Titanium is extracted with iron, alumina which has been explained in the earlier section. Very few works have been conducted on selective extraction of titanium from red mud. Table 3 reviews the very recent work on extraction of Titanium from red mud.
Table 3. Recovery of Titanium from red mud
|
Constituent used |
Experimental Conditions |
Observations |
Method used for extraction |
Key Findings |
Country |
Reference |
|
Red mud, H2SO4 |
Acid leaching with 6N H2SO4, 60°C and solid to liquid ratio: 5%. |
At optimum conditions, iron leaching was 46%, and aluminum did not exceed 37% |
Acid leaching |
Titanium recovery efficiency was 64.5% |
Greece |
(Agatzini-Leonardou et al. 2008) |
|
Red mud, H2SO4, HCl |
H2SO4 as leaching agent, 70°C, 120 min, Solid/liquid ratio: 1:50 |
Hydrometallurgical treatment of red mud. Interference of Fe in Ti leaching observed. |
Acid leaching |
H2SO4 leaching most effective. Maximum titanium leaching efficiency 67%. |
Grecce |
(Alkan, Schier, et al. 2017) |
|
Red mud, hydrochloric acid, sulphuric acid, extractant Cyanex923, Heptane
|
Sulfuric acid leaching (6mol/L), 85 ◦C, L/S = 20 Organic/aqueous phase ratio: 1. Cynax concentration was 2.59 gL-1 |
The maximum leach rate of Ti (IV), Fe (III) and Al (III) were 64.53%, 34.01% and 47.09% in H2SO4. The extraction efficiency was 42.07%, 2.27%, 0.49% for Ti (IV) Fe (III) and Al (III) resp. with addition of Cynax923 to the H2SO4 leach liquor |
Acid Leaching |
High extraction efficiency for titanium (IV). Exothermic process with efficiency decreasing at higher temperatures. |
China |
(Zou, Chen, and Li 2021) |
|
Red mud, leaching reagent (HNO3, H2SO4, HCl, EDTA and aqua regia, Cyanex 301), precipitating agents (oxalic acid, ace tic acid, sulphuric acid, tartaric acid, thiosulfate, iodide, ammonia) |
HCl leaching (12 mol/L), 25ۦ°C, 24 hours, Solid/liquid ratio: 1:10, agitator speed: 150 rpm, oxalic acid, acetic acid, sulphuric acid, tartaric acid, thiosulfate, iodide and ammonia used to precipitate |
The method effectively removed impurities such as iron and aluminum, enhancing titanium recovery |
Acid Leaching |
Maximum titanium leaching efficiency of 95% with HCl. |
Italy |
(Pietrantonio et al. 2021) |
|
Red mud, smelting separation slag, additives (NaOH, Ca(OH)2) |
Roasting (1200°C, 60 min) NaOH leaching to remove alumina bearing phases followed by HCl leaching to get titanium enriched slag. |
Mineral phase reconstruction process can enable a higher metal leaching rate. |
Acid Leaching |
Overall TiO2 recovery was 95.46%. |
China |
(S. Li et al. 2023) |
Different studies report efficiencies from 67% up to 95.46% for titanium extraction from red mud by acid leaching. Sulfuric and hydrochloric acid have been used as leaching agents. Generally, titanium extraction efficiencies using hydrochloric acid can be as high as 95.46%, compared to with sulfuric acid. Although processes with the optimal conditions for titanium extraction depend on the specific process, they generally involve a high acid concentration, controlled temperature, and solid-liquid ratios.
Recovery of Gallium:
Gallium is trace element present in the bauxite and enters the red mud during its processing. Red mud generally consists of 0.002 %–0.008% of gallium (Ga) (Lu et al. 2018). Table 4 reviews the work carried out for recovery of gallium from red mud. Solvent extraction and electrolysis are mainly the two methods used for recovery of Gallium from red mud
Table 4. Recovery of Gallium from red mud
|
Constituents used |
Observations |
Method used for extraction |
Key Finding |
Country |
Reference |
|
|
Red mud, HCl, NaOH |
Acid leaching with HCl from red mud; 8 mol/L HCl, L/S=4.0, 5 hours, 109 °C |
Leaching rate of gallium was 95.4%. |
Acid Leaching |
Max. extraction rate of gallium reached 98% with 50% TBP+50% kerosene |
China |
(Wang et al. 2012). |
|
Red mud, oxalic acid, sulphuric acid, nitric acid, hydrochloric acid |
Selective acid leaching with oxalic acid (H2C2O4) (2.5 M H2C2O4, 21.7 h, 80°C,10g/L slurry conc.) |
Highest extraction efficiency of Ga achieved using oxalic acid leaching. |
Acid Leaching |
gallium extraction 80%. |
Hungary |
(Ujaczki et al. 2017).
|
|
Red mud, sodium hydroxide |
20 % NaOH, 120 °C, 12 hours, solid/liquid ratio 1:5 |
Fe is not detected in leaching solution |
Hydrothermal alkaline leaching method |
Maximum gallium leaching efficiency of 91.4%. |
China |
(Xue et al. 2019) |
|
Red mud, sulphuric acid, D2EHPADi (2-ethylhexyl) phosphoric acid |
Extraction of gallium (III) and vanadium (IV) using D2EHPA; pH 1.4-1.8, 0.3 M D2EHPA |
. Yield of vanadium increases from 18.1 to 95.8%, yield of gallium nearly 98.2% at pH 1-2 |
Hydrometallurgy |
Optimized conditions for selective separation of gallium and vanadium from aluminum. |
China |
(Tagiyeva L.T 2021) |
Acid leaching is highly effective for gallium extraction, achieving over 95% recovery under optimized conditions. Very recently, phosphoric acid has been proposed to be used for leaching instead of H2SO4 (Yimin Zhu 2024). Research focuses on improving the selectivity and efficiency of gallium extraction, particularly in separating it from elements like vanadium and aluminium in complex matrices such as red mud.
Recovery of Rare Earth Elements (REEs):
The REEs comprises of the fifteen metallic elements of the lanthanide series, along with yttrium and scandium (Krishnamurthy and Gupta 2004). They are further classified into light rare earth elements, LREEs, which include lanthanum to europium, and the heavy rare-earth elements, HREEs, that contain the other remaining lanthanides from gadolinium to lutetium plus yttrium (Trifonov 1963). Rare earth elements and is composition from one of the studies of Chenna Borra is given in the Table 5 (Borra et al. 2015). Table 6 show the utilization of red mud for REEs recovery in a national and international context.
Table 5: Rare earth elements composition in red mud in g/tonne
|
Elements |
Sc |
Y |
La |
Ce |
Pr |
Nd |
Sm |
Eu |
Gd |
Tb |
Dy |
Ho |
Er |
Tm |
Yb |
Lu |
|
Composition (g/tonne) |
121 |
76 |
114 |
368 |
28 |
99 |
21 |
5 |
22 |
3 |
17 |
4 |
13 |
2 |
14 |
2 |
Table 6. Utilization of red mud for rare earth elements recovery in National and international context
|
Study |
Observation |
Rare earth recovered |
Ref. |
|
Acid leaching with HCl and H2SO4 at two leaching conditions. |
80% scandium recovery and 1% titanium recovery in HCl leaching and 96.5% titanium recovery in H2SO4 leaching |
Scandium and Titanium |
(Zhang, Deng, and Xu 2005) |
|
Biological leaching Penicillium tricolor fungi |
Two-step bioleaching process at 10% (w/v) pulp density achieved maximum extraction yield |
REE |
(Qu and Lian 2013) |
|
Studied possibilities to REEs from residues such as pyrometallurgical slags, bauxite residue (red mud), phosphogypsum, mine tailings and wastewater. |
Author reviewed the recovery of REEs from industrial waste |
REE |
(Binnemans et al. 2013) (Binnemans et al. 2015) |
|
Sulfuric acid leaching followed by liquid-liquid extraction with various organic extractants. |
99.9 % Lanthanum and cerium recovery achieved |
Lanthanum and Cerium |
(Abhilash et al. 2014) |
|
Leaching experiments on Greek bauxite residue |
70-80% REEs could be recover using 6 N HCl leaching for 24 h at 25°C. |
REE |
(Borra et al. 2015) |
|
Author reviewed various extraction method |
Can be recovered by direct leaching or by smelting followed by leaching. |
REE |
(Borra, Blanpain, et al. 2016a) |
|
A combined sulfation–roasting–leaching process to selectively leach the REEs while leaving iron undissolved in the residue. |
Higher acid concentrations enhanced REE extraction |
REE |
(Borra, Mermans, et al. 2016) |
|
Reduction smelting process using wollastonite as a flux and graphite as a reducing agent. |
high-temperature leaching at 90°C yielded > 95% scandium, >70% of REEs, and about 70% titanium |
Fe, REE |
(Borra, Blanpain, et al. 2016b) |
|
Used functionalized ionic liquid titanium bis(trifluoromethylsulfonyl)imide (HbetTf2N) directly on leaching |
70-85% REEs extraction yield with <3% Fe extraction yeild |
REE |
(Davris et al. 2016) |
|
Recovery of Titanium and scandium using combine pyrometallurgical and hydrometallurgical methods |
To overcome limitations of direct leaching, a new process combining pyrometallurgical and hydrometallurgical methods was proposed |
REE |
(Alkan, Xakalashe, et al. 2017) |
|
Used sequential extraction method |
60% yttrium was extracted from high iron diasporic red mud |
yttrium |
(Gu, Wang, and Hargreaves 2018) |
|
Study comprises of Overview of the methods to extract rare earth elements (REEs) |
Author reviewed method for extraction of REEs |
REEs |
(Akcil et al. 2018) |
|
Dry digestion method followed by water leaching |
Multi-stage leaching, particularly with HCl is more effective than single-stage dry digestion-water leaching |
REE |
(Rivera et al. 2018) |
|
Technical feasibility of simultaneous metal extraction and separation was investigated using HCl medium and various organic extractant in liquid-liquid extraction. |
88.5% of La and 99.9% of Ce recovery at 95 °C, 1 M HCl, S/L 1/100, 1 hour, 200 rpm agitation |
Lanthanum and Cerium |
(Abhilash et al. 2019) |
|
An acid producing bacteria Acetobacter sp. was used. Two-step processes were used with 2-10% pulp density. |
Leaching ratios of Al, Lu, Y, Sc, and Th were 55%, 53%, 61%, 52% and 53% respectively with one step process at 2% pulp density |
Aluminium, Lanthanum, Yttrium, Scandium, Thorium |
(Qu et al. 2019) |
Recovery of Scandium:
The recent advancements in the distribution characteristics of scandium in red mud, along with the techniques for extracting scandium from red mud and the associated processing conditions, have been reviewed both domestically and internationally. (Si, Deng, and Xu 2003). The authors summarized techniques for extracting scandium from red mud, outlining key technologies for recovery from leaching solutions, solvent extraction, and refining processes, ultimately suggesting a more viable approach for comprehensive red mud utilization (Wang et al. 2008). Table 7 reviews the work carried out for extraction of scandium.
Table 7. Recovery of Scandium from red mud
|
Constituent used |
Observations |
Method of Extraction |
Key Findings |
Country |
Reference |
|
|
Red mud, Hydrochloric acid, P_507 and kerosene |
HCl leaching followed by solvent extraction |
Processing conditions studied |
Hydrometallurgy |
The scandium had 66.09% purity. |
China |
(Zhang, Deng, and Xu 2006) |
|
Modified Activated Carbon, HCl, red mud
|
Adsorbent dosage: 6.25 g/L,308 K, Adsorption time: 40 min
|
Adsorption capacity to Sc increases with time, reaching equilibrium after 40 min
|
Adsorption
|
Adsorption capacity to Sc increases with time, reaching equilibrium after 40 min
|
China |
(ZHOU et al. 2008) |
|
Red mud, NaOH, Na2CO3, ZnO |
Carbonisation of red mud with CO2 |
Ga, Al also co-precipitate |
Carbonisation. |
Zinc hydroxide was the most effective co-precipitant for scandium |
Russia |
(Yatsenko and Pyagai 2010) |
|
Red mud, diluted sulphuric acid, Cyanex 272, D2EHPA |
Leaching with 0.5 H2SO4 followed by solvent extraction |
DE2HPA is best extract among remaining extract used in the study |
solvent ex‐ traction |
99% scandium could extract |
Australia |
(Wang, Pranolo, and Cheng 2013) |
|
Red mud, HCl, H2SO4, lignite coke, lime |
High-pressure acid leaching with HCl at 120°C and H2SO4 at 150°C |
High selectivity for scandium extraction |
Hydro-metallurgy |
Approx. 80% scandium recovery (HCl leaching) and more than 95% extraction (H2SO4 leaching) |
Greece |
(Rivera et al. 2019) |
|
Red mud, sulphuric acid, CaF2, solvent extractant P507
|
Acid leaching with CaF₂ and H₂SO₄, 90°C, solvent extraction 10% P507, pH: 0.1 for 4 min |
Effective combination of acid leaching and solvent extraction |
Acid leaching |
over 98% scandium extraction |
China |
(Zhu et al. 2020) |
|
Red mud, ammonium chloride, sulfuric acid scandium sulfate, ethanol |
5-6 M H2SO4 and 0.5 M NH4Cl |
High scandium recovery rate achieved. |
Hydro-metallurgy |
99% of scandium in the form of NH4Sc (SO4)2 |
Russia |
(Pasechnik et al. 2021) |
|
Red mud, H2SO4, MgSO4, NaOH, and Al(OH)3, sodium carbonate and lime |
Acid leaching with MgSO₄ at pH 2, CMgSO4 of 24 g L−1 ,80 °C, 60 min |
significant extraction even at pH 4 |
Acid leaching |
scandium extraction efficiency of over 80% at pH 2 |
Russia |
(Shoppert et al. 2022) |
|
Red mud, nitric acid |
Diluted nitric acid leaching at pH 2, L:S ratio 10,80 °C, 90 min |
Significant effect of pH |
Acid leaching |
71.2% scandium extraction with Fe extraction less than 3%. |
Russia |
(Shoppert et al. 2022) |
|
Red mud, hydrochloric acid |
Hydrochloric acid leaching at 20% in solution, 200 rpm, 80°C, 3h, S/L:1:10(g/mL), −74 µm sample particle size |
leaching efficiency is controlled by chemical reaction step. |
Acid leaching |
Maximum scandium leaching efficiency of 83.94% |
China |
(Wei et al. 2022) |
|
Red mud, sulfuric acid |
Roasting at 1023 K, 60 min H2SO4 leaching (H2SO4/RM :0.9 mL/g, 323K, 200 rpm, 2h, L:S:5mL/g) |
low acid consumption, high scandium leaching rate |
sulfation-roasting-water leaching method |
Leaching efficiency of scandium is 91.98% |
China |
(Ding et al. 2022) |
Various acids like hydrochloric acid, sulfuric acid, and nitric acid have been commonly used for leaching of scandium from red mud. Under optimized conditions, which generally include elevated temperatures ranging from 80 to 120°C and carefully regulated pH levels, high recovery rates for scandium can be attained, often exceeding 80% and reaching as high as 99%. The experiments were carried out in several countries, including Greece, China, and Russia, with studies being carried out in India too.
CONCLUSION:
The processes for metal extraction from red mud have been several studied and have been reviewed. Red mud consists of metals which makes their recovery an important aspect both in as far as industry is concerned and in relation to the environment. Reduction roasting is the most used method for extraction of iron from red mud. In reduction roasting, the red mud is treated at very high temperatures together with a reductant that allows the iron oxides to be converted to iron. After this roasting, it is common to get rid of iron by means of magnetic separation in which only the magnetic iron is separated. In addition to reduction roasting, acid leaching is another important method of iron extraction. Using this method, red mud is treated with acids that dissolve iron. Most of the time, researchers rely on hydro metallurgical techniques to separate alumina and caustic soda from red mud. In these processes, aqueous solutions are utilized for the removal of the targeted components from red mud. One of the most effective processes is the calcification-carbonation method, in which aluminium-containing compounds are converted into more soluble forms and then extracted. For the extraction of alumina and caustic soda both hydrometallurgy and calcium carbonation have demonstrated high extraction efficiency. For titanium recovery, strong acid leaching methods have shown more leaching efficiency. For selectively recovery of gallium from red mud there is not much literature available. Acid and alkali leaching methods are being utilized by researchers to extract gallium. The exploration of gallium recovery remains an area of ongoing research, as the demand for this metal continues to grow in various high-tech applications. There is an increasing demand on extraction of rare earth elements from red mud like cerium, scandium and lanthanum due to their applications in specialised materials.
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Received on 27.01.2025 Revised on 24.02.2025 Accepted on 20.03.2025 Published on 27.03.2025 Available online from March 27, 2025 Research J. Engineering and Tech. 2025; 16(1):31-43. DOI: 10.52711/2321-581X.2025.00004 ©A and V Publications All right reserved
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