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Preparation of Magnesium Silicate Hydrate by Dissolving Magnesium Silicate Minerals with Waste Acid
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Qiang SONG1, Qian HE1, Jiao NIE1, Tiantian SONG1, Hong ZHOU2, Yaru HU1, Yanxin CHEN1, Yang DENG3, Fuan CHENG1
Journal of the Chinese Ceramic Society | 2025, 53(11) : 3168 - 3178
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Journal of the Chinese Ceramic Society | 2025, 53(11): 3168-3178
• Research Article •
Preparation of Magnesium Silicate Hydrate by Dissolving Magnesium Silicate Minerals with Waste Acid
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Qiang SONG1, Qian HE1, Jiao NIE1, Tiantian SONG1, Hong ZHOU2, Yaru HU1, Yanxin CHEN1, Yang DENG3, Fuan CHENG1
Affiliations
  • 1.College of Materials Science and Engineering Xi'an University of Architecture and Technology, Xi'an 710055, China
  • 2.Shaanxi Building Materials Technology Group Co., Ltd., Xi'an 710018, China
  • 3.Shaanxi Fuping Eco-Cement Co., Ltd., Weinan 711709, Shaanxi, China
  • SONG Qiang (1980-), male, Ph.D., Associate Professor. E-mail:

About Author:

SONG Qiang (1980-), male, Ph.D., Associate Professor. E-mail:

Published: 2025-11-20 doi: 10.14062/j.issn.0454-5648.20250134
Outline
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Introduction

Magnesium silicate hydrate (M-S-H) attracts significant attention as an alternative to traditional portland cement due to its unique properties, including reduced energy consumption during preparation. However, its synthesis typically requires MgO from calcined magnesite, which undermines the environmental benefits it provides. This study addresses these limitations by proposing a waste valorization strategy: recycling waste acid to dissolve naturally abundant magnesium silicate minerals (serpentine, olivine, and sepiolite) for M-S-H production. By combining acid waste management with mineral resource utilization, this approach not only avoids the energy-intensive MgO production process but also eases the ecological hazards caused by acid disposal.

Methods

The experimental involved three key stages: acid leaching, material preparation, and characterization. First, serpentine, olivine, and sepiolite were subjected to dissolution in a mixed waste acid solution (HCl: 6.20 mol/L, H2SO4: 7.77 mol/L) at 90 ℃ for 3 h under continuous mechanical agitation. The solid-to-liquid ratio was maintained at 1∶5 for acid leaching. After leaching, the insoluble residues (mainly amorphous silica) were separated with a centrifuge (Thermo Scientific ST 16R). The obtained residues were washed ultrasonically with deionized water 5 times to remove residual acid. Subsequently, the residue was dried in a vacuum drying oven at 50 ℃ for 24 h. The acid-leached filtrate was added into a 10 mol/L NaOH solution, with real-time pH monitoring until reaching pH 11.5. The obtained suspension was left to settle at room temperature for 24 h. The white flocculent precipitate was collected by vacuum filtration and dried at 100 ℃ for 24 h to obtain Mg(OH)2-rich powder. The dried residue was mixed with Mg(OH)2 powder at a ratio of n(SiO2) ∶ n(MgO)=1.0∶1.4, and blended with water with a water-to-solid ratio of 1 ∶ 2 to form a paste. The paste was sealed in glass tubes and cured in water baths at 20, 50 ℃, and 80 ℃ for 3, 7, 14 d, and 28 d, followed by vacuum drying at 50 ℃ for 24 h prior to characterization. Mortar samples with the same residue-Mg(OH)2 ratio were tested for compressive strength, fluidity, and drying shrinkage according to Chinese national standards.

Results and discussion

The residues contain 89%-96% amorphous SiO2, and Mg(OH)2 precipitates exhibit 96% purity. Promoting curing temperature significantly accelerates M-S-H formation. At the same age, the diffraction peak of Mg(OH)2 is lower in samples cured at higher temperature. TG curves reveal 3 distinct mass loss: 50-350 ℃ (loss of physically bound water, Δw1), 350-450 ℃ (Mg(OH)2 dehydroxylation, Δw2), and 450-750 ℃ (Si-OH dehydroxylation, Δw3). The Δm2 content decreases with age and elevated temperatures, indicating accelerated Mg(OH)2 reaction. A linear relationship between Δm2 and (Δw2+Δw3) is established. A decline is observed in the slopes of fitting line, from 0.96 (20 ℃) to 0.80 (50 ℃) and 0.76 (80 ℃), which indicates that the contribution from unreacted Mg(OH)2 decreases while the formation of M-S-H is promoted with increasing temperature. The broadening and intensification of the exothermic peak near 850 ℃ (M-S-H recrystallization) in the DSC curve indicate enhanced maturation of M-S-H with increasing curing temperature. 29Si NMR spectra indicate elevated curing temperatures reduced the relative content of Q1, confirming enhanced polymerization of silicon-oxygen tetrahedra in M-S-H phases, though infinite chain structures were not formed. The diminished Q3c signal (corresponding to talc-type 2∶1 layered structures) indicated a gradual decline in "transitional" M-S-H (Mg/Si = 0.9-1.1), while increased Q3a (serpentine-like 1∶1 layers) reflected accelerated alignment of Mg/Si ratios with the raw material's composition (1.4). M-S-H gels form via Mg2+/H3SiO4- polymerization into Q2/Q3 networks with minor Q1, accelerated by elevated temperatures to yield serpentine-like layer structure. The M-S-H mortars demonstrated remarkable early strength (12-18 MPa at 3 d). This was attributed to the high reactivity of amorphous SiO2 and the rapid dissolution of Mg(OH)2. After 28 d, compressive strength reached 40 MPa at 80 ℃. The mortar exhibited superior fluidity (157-181 mm flow diameter) without any superplasticizer, enabled by 28%-32% moisture in residues. However, excessive drying shrinkage was observed.

Conclusions

The mixed waste acid effectively dissolved serpentine, olivine, and sepiolite, yielding Mg(OH)2 (≥96% purity) and SiO2-rich residues (>89% SiO2). The polymerization degree of silicon-oxygen tetrahedra in the resulting M-S-H phases increased with rising curing temperature (from 20 ℃ to 80 ℃) and extended curing time (from 3 d to 28 d), leading to the formation of serpentine-like layered structures. The mortar exhibited high early strength (12-18 MPa at 3 d) and reached 40 MPa at 28 d, which is attributed to the high reactivity of silica residues and rapid dissolution of Mg(OH)2. Although the inherent moisture in the residues and the absence of water consumption by Mg(OH)2 contributed to excellent fluidity without adding superplasticizers, this combination still causes significant shrinkage.

magnesium silicate hydrate  /  magnesium silicate minerals  /  acid-leaching method  /  cementitious material
宋强, 何倩, 聂娇, 宋甜甜, 周红, 胡亚茹, 陈延信, 邓洋, 程福安. 利用废酸溶解硅酸镁矿物制备水化硅酸镁胶凝材料. 硅酸盐学报, 2025 , 53 (11) : 3168 -3178 . DOI: 10.14062/j.issn.0454-5648.20250134
Qiang SONG, Qian HE, Jiao NIE, Tiantian SONG, Hong ZHOU, Yaru HU, Yanxin CHEN, Yang DENG, Fuan CHENG. Preparation of Magnesium Silicate Hydrate by Dissolving Magnesium Silicate Minerals with Waste Acid[J]. Journal of the Chinese Ceramic Society, 2025 , 53 (11) : 3168 -3178 . DOI: 10.14062/j.issn.0454-5648.20250134
Year 2025 volume 53 Issue 11
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doi: 10.14062/j.issn.0454-5648.20250134
  • Receive Date:2025-03-03
  • Online Date:2026-10-21
  • Published:2025-11-20
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History
  • Received:2025-03-03
  • Revised:2025-03-27
Funding
Affiliations
    1.College of Materials Science and Engineering Xi'an University of Architecture and Technology, Xi'an 710055, China
    2.Shaanxi Building Materials Technology Group Co., Ltd., Xi'an 710018, China
    3.Shaanxi Fuping Eco-Cement Co., Ltd., Weinan 711709, Shaanxi, China

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CHEN Yanxin (1974-), male, Ph.D., Professor. E-mail:
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表12种不同金属材料的力学参数
科
Family
属数
Number of
genus
种数
Number of
species
占总种数比例
Percentage of
total species (%)
属
Genus
种数
Number of
species
占总种数比例
Percentage of total
species (%)
鹅膏菌科Amanitaceae 2 11 5.26 鹅膏菌属 Amanita 10 4.78
小菇科 Mycenaceae 2 12 5.74 丝盖伞属 Inocybe 5 2.39
多孔菌科 Polyporaceae 8 14 6.70 蜡蘑属 Laccaria 5 2.39
红菇科 Russulaceae 3 23 11.00 小皮伞属 Marasmius 6 2.87
小菇属 Mycena 11 5.26
光柄菇属 Pluteus 5 2.39
红菇属 Russula 17 8.13
栓菌属 Trametes 5 2.39
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