ISSN 1008-5548

CN 37-1316/TU

最新出版

以菱镁矿为原料制备大比表面积多孔羟基硅酸镁及其吸附性能

Preparation and adsorption performance of porous magnesium hydroxy silicate with high specific surface area prepared from magnesite


姜嘉存1 王余莲1,2赵 菁1 ,吕思龙1 刘珈伊3蒋宝泉1李克卿1于航欢1武小娟1孙浩然1 马瑞廷1 李 刚2

1. 沈阳理工大学 材料科学与工程学院,辽宁 沈阳 110159;2. 营口理工学院 辽宁省菱镁矿高值利用工程研究中心,辽宁 营口 115014;3. 东北大学 资源与土木工程学院,辽宁 沈阳 110819


引用格式:

姜嘉存,王余莲,赵菁,等 . 以菱镁矿为原料制备大比表面积多孔羟基硅酸镁及其吸附性能[J]. 中国粉体技术,2026,32(5):1-16.

JIANG Jiacun, WANG Yulian, ZHAO Jing, et al. Preparation and adsorption performance of porous magnesium hydroxy silicate with high specific surface area prepared from magnesite[J]. China Powder Science and Technology,2026,32(5):1−16.

DOI:10.13732/j.issn.1008-5548.2026.05.010

收稿日期:2026-01-05,修回日期:2026-02-20,上线日期:2026-04-14。

基金项目:国家自然科学基金项目,编号52374271;“兴辽英才计划”青年拔尖人才项目,编号XLYC2403010;辽宁省重点研发计划应用基础研究计划项目,编号2025JH2/101300041。

第一作者:姜嘉存(2000—),男,硕士生,研究方向为镁基矿物功能材料制备与应用。E-mail:J19818675956@163. com。

通信作者:

王余莲(1986—),女,教授,博士,博士生导师,中组部“万人计划”青年拔尖人才,研究方向为矿物材料制备及功能化。E-mail:ylwang0908@163. com。

李刚(1969—),男,教授,博士,博士生导师,研究方向为功能材料。E-mail:stars2387@vip. sina. com。


摘要:【目的】以菱镁矿为原料,制备具有良好吸附性能的大比表面积多孔羟基硅酸镁,推动菱镁矿资源高值化利用。【方法】通过煅烧-水化-碳化法将菱镁矿制成重镁水(Mg(HCO32)作为镁源,以正硅酸乙酯为硅源,采用水热法-煅烧法制备大比表面积多孔羟基硅酸镁;探究硅镁物质的量比、水热时间、水热温度及煅烧时间对产物显微结构、比表面积及孔径分布等的影响,采用X射线衍射仪、扫描电子显微镜、全自动比表面积分析仪、傅里叶变换红外光谱仪、X射线光电子能谱仪和电感耦合等离子体光谱仪对产物微观结构及吸附性能进行表征。【结果】当硅镁物质的量比为2:1、水热时间为8 h、水热温度为130 ℃,比表面积为630.36 m2/g,经过400 ℃、4 h煅烧后比表面积提高10.7 %,为706.28 m2/g,说明煅烧对比表面积提高有较大影响。多孔羟基硅酸镁的形成过程包括3个阶段:正硅酸乙酯水解生成富含硅羟基的环状多聚硅烷醇中间体;重镁水中镁离子与该中间体通过Si—O—Mg键交联组装为层状骨架;羟基占据层间与表面位点,稳定结构的同时并促进孔形成,煅烧活化使羟基硅酸镁内部脱水形成新的孔道。通过络合反应对重金属离子产生吸附作用,对Cu2+、Cr3+和Ni2+的最大吸附量分别为275、245、258 mg/g。【结论】以菱镁矿为原料制备多孔羟基硅酸镁,具有大的比表面积和良好的吸附性能,可应用于重金属离子吸附。

关键词:菱镁矿;羟基硅酸镁;多孔材料;比表面积;吸附

Abstract

Objective Using magnesite as the raw material, porous magnesium hydroxy silicate with excellent adsorption performance and large specific surface area is prepared to promote the high-value utilization of magnesite resources.

Methods Magnesite was converted into magnesium bicarbonate solution (Mg(HCO3)2) via calcination-hydration-carbonation process to serve as the magnesium source, while tetraethyl orthosilicate was used as the silicon source. Porous magnesium hydroxy silicate with a large specific surface area was then synthesized by combining the hydrothermal method with the calcination method. This study mainly investigated the effects of the molar ratio of silicon to magnesium, hydrothermal reaction time, hydrothermal temperature, and calcination time on the microstructure, specific surface area, and pore size distribution of the products. The microstructure and adsorption performance of the prepared products were characterized by means of XRD, SEM, BET, FTIR, XPS, and ICP-AES.

Results and Discussion Using magnesite as the raw material, magnesium bicarbonate solution prepared via the calcination-hydration-carbonation process was employed as the magnesium source, while tetraethyl orthosilicate served as the silicon source. Porous magnesium hydroxy silicate was synthesized using the hydrothermal method. When the molar ratio of silicon to magnesium was 2:1, the hydrothermal reaction time was 8 h, the hydrothermal temperature was 130 ℃, and magnesium hydroxy silicate product with a specific surface area of 630.36 m2/g was obtained. Among the synthesis parameters, the molar ratio of silicon to magnesium and the hydrothermal reaction time exerted the most significant effects on the specific surface area of the magnesium hydroxy silicate. During the reaction process, the magnesium silicate initially presented as bulk solids without obvious porous structures. With a gradual increase in the content of the silicon source, primary particles were observed to gradually emerge on the surface of the bulk magnesium silicate. As the hydrothermal time increased continuously, a highly developed porous network structure was finally formed. This phenomenon could be attributed to the more complete hydrolysis of tetraethyl orthosilicate resulting from the increased silicon source and extended hydrothermal time, which provided more silanol groups for the cross-linking reaction with magnesium ions and promoted the full assembly of the porous structure. In contrast, the hydrothermal temperature exerted a relatively significant influence on the product's aggregation state. When the hydrothermal temperature was appropriate, the product existed as bulk aggregates with well-defined pore channels and uniform particles. However, when the hydrothermal temperature was excessively high, the particles grew too fast, leading to their connection into sheet-like structures, the disappearance of pore channels, and a consequent decrease in specific surface area. The final product was identified as porous magnesium hydroxy silicate crystals with a granular accumulation structure. The calcination time also showed a notable impact on the specific surface area of the magnesium hydroxy silicate. The specific surface area reached a maximum value of 706.28 m2/g after 4 h of calcination, which was 10.7% higher than that of the uncalcined sample. Calcination could induce the removal of bound water molecules from the magnesium hydroxy silicate, thereby maintaining the pore channels while forming more mesoporous and microporous structures. However, excessively long calcination time might lead to pore channel collapse, resulting in structural damage and a subsequent decrease in specific surface area. Its formation process involved three stages: the hydrolysis of tetraethyl orthosilicate to generate cyclic polysilanol intermediates rich in silanol groups; the cross-linking assembly of ions from the magnesium bicarbonate solution with these intermediates into a layered framework via Si—O—Mg bonds; and the occupation of interlayer and surface sites by hydroxyl groups, which stabilized the structure and promoted pore formation, while subsequent calcination activation induced internal dehydration of the magnesium hydroxy silicate to form new pore channels. The product adsorbed heavy metal ions through complexation reactions, with the maximum adsorption capacities of 275, 245, and 258 mg/g for Cu2+, Cr3+, and Ni2+, respectively. The adsorption rate was fastest and the adsorption efficiency was highest within the first 5 min, after which the adsorption reached equilibrium. Meanwhile, the pseudo-first-order and pseudo-second-order kinetic models were employed to fit and analyze the adsorption data. The fitting results showed that the adsorption of the three heavy metal ions followed a chemical adsorption process, which was consistent with the previously proposed complexation reaction mechanism for heavy metal adsorption by porous magnesium hydroxy silicate.

Conclusion Porous magnesium hydroxy silicate prepared from magnesite possesses a high specific surface area and excellent adsorption performance, enabling its application in the field of heavy metal ion adsorption from polluted water. This study not only expands the methods for preparing magnesium silicate from mineral raw materials and supplements the specific reaction conditions, but also provides theoretical support and technical reference for the high-value utilization of magnesite resources and the development of efficient and low-cost heavy metal adsorption materials.

Keywords:magnesite; magnesium hydroxy silicate; porosint; high specific surface area; adsorption


参考文献(References)

[1]杜攀,陈文超,王海增. 硅酸镁材料及其应用[J]. 盐业与化工, 2013, 42(10): 1-6.

DU P, CHEN W C, WANG H Z. Magnesium silicate materials and their applications[J]. Journal of Salt and Chemical Industry, 2013, 42(10): 1-6.

[2]SHAH M H, BIRADAR S V, PARADKAR A R. Spray dried glyceryl monooleate-magnesium trisilicatedry powder as cubic phase precursor[J]. International Journal of Pharmaceutics, 2006, 323(1/2): 18-26.

[3]王子潇. 硅酸镁的改性及其对含油废水处理性能研究[D]. 北京: 北京化工大学, 2021.

WANG Z X. Modification of magnesium silicate and its performance in treating oil-containing wastewater[D]. Beijing: Beijing University of Chemical Technology, 2021.

[4]杜国勇,张洪铭,李艳,等. 硅酸镁的改性及其对稠油污水中有机物的吸附[J]. 功能材料,2017,48(6): 6013-6017.

DU G Y, ZHANG H M, LI Y, et al. Modification of magnesium silicate and its adsorption of organic matter in heavy oil wastewater[J]. Journal of Functional Materials, 2017, 48(6): 6013-6017.

[5]黄人瑶. 多孔硅酸镁高效吸附材料的构筑及其重金属离子吸附性能研究[D]. 北京:北京化工大学, 2018.

HUANG R Y. Construction of porous magnesium silicate high-efficiency adsorbent materials and study on their adsorption performance for heavy metal ions[D]. Beijing: Beijing University of Chemical Technology, 2018.

[6]SUN Z, SRINIVASAKANNAN C, LIANG J, et al. Preparation of hierarchical magnesium silicate with excellent adsorption capacity[J]. Ceramics International, 2019, 45(4): 4590-4595.

[7]冯凌,李敏,刘国强,等. 共沉淀法合成三硅酸镁及其微观分析[J]. 北京科技大学学报,2009,31(12): 1600-1604.

FENG L, LI M, LIU G Q, et al. Synthesis of magnesium trisilicate by coprecipitation method and its microscopic analysis[J]. Journal of University of Science and Technology Beijing, 2009, 31(12): 1600-1604.

[8]程勇. 球形硅酸镁的制备及吸附性能研究[D]. 北京: 北京化工大学, 2019.

CHENG Y. Preparation of spherical magnesium silicate and study on its adsorption performance[D]. Beijing: Beijing University of Chemical Technology. 2019.

[9]朱万军,翟晓颖,黄人瑶,等. 三维花状硅酸镁富集-X⁃射线荧光光谱法测定水中痕量铅锌铜[J]. 分析化学,2018,46(9): 1386-1392.

ZHU W J, ZHAI X Y, HUANG R Y, et al. Determination of trace lead, zinc and copper in water by three-dimensional flower-like magnesium silicate enrichment coupled with X-ray fluorescence spectrometry[J]. Analytical Chemistry, 2018,46(9): 1386-1392.

[10]NARASIMHARAO K,ANGARU G K R, MOMIN Z H, et al.Orange waste biochar-magnesium silicate (OBMS) composite for enhanced removal of U (VI) ions from aqueous solutions[J]. Journal of Water Process Engineering,2023,51: 103359.

[11]MURSALAT M, SKURA A, SCHOENITZ M, et al. Potential one-pot synthesis of spherical magnesium silicate powder by mechanical milling[J]. Powder Technology, 2022, 404: 117458.

[12]ZHANG J J, LI G Y, ZHANG S B, et al. Controlled synthesis of biochar with flower-like morphology for CO2 adsorption: enrichment and efficient accessibility of N-containing sites[J]. ACS Applied Materials & Interfaces, 2025, 17(4): 6742-6754.

[13]ZHAO X H, TONG J T, BAI S, et al. Dual-metal-catalyzed fenton-like reaction on CdxZn1-xS@ Biochar: mechanistic insights into sulfide-metal interactions for water purification[J]. Applied Catalysis B: Environment and Energy, 2025, 15(3): 125654.

[14]XIA L, LI X L, WEI Z J, et al. Biochar-mediated electron transfer in a spinel ferrite catalyst boosts peracetic acid activation for water decontamination[J]. Chemical Engineering Journal, 2025, 25(2): 170068.

[15]PRANCKEVICIENE J, PUNDIENE I. Use of magnesium silicate contaminated with organic compounds in ceramic materials as a pore modifier[J]. Materials, 2022, 15(24): 8833.

[16]GONG Y B, CHEN M Y, ZHANG Y F, et al. Hydrothermal synthesis and formation mechanism of controllable magnesium silicate nanotubes derived from coal fly ash[J]. Nanotechnology, 2023, 34(36): 365701.

[17]WANG X K, WANG J S, TENG W L, et al. Fabrication of highly efficient magnesium silicate and its adsorption behavior towards Cr(VI)[J]. Microporous and Mesoporous Materials, 2021, 323: 111196.

[18]王琪浩, 王余莲, 薛铭, 等. 利用菱镁矿制备非晶态硅酸镁[J]. 中国粉体技术, 2022, 28(5): 128-134.

WANG Q H, WANG Y L, XUE M, et al. Preparation of amorphous magnesium silicate from magnesite[J]. China Powder Science and Technology, 2022, 28(5): 128-134.

[19]TERZIOGLU P, YUCEL S. Synthesis of magnesium silicate from wheat husk ash: effects of parameters on structural and surface properties[J]. BioResources, 2012, 7(4): 5435-5447.

[20]ZHANG Q, LIU G J, PENG S C, et al. The simultaneous removal of cadmium (II) and lead (II) from wastewater with the application of green synthesized magnesium silicate hydrate[J]. Frontiers in Earth Science, 2023, 10: 1074687.

[21]王伟, 孙浩东, 孙蕊. 大孔径介孔二氧化硅纳米粒子研究进展[J]. 中国粉体技术, 2025, 31(2): 31-48.

WANG W, SUN H D, SUN R. Research progress of large-pore mesoporous silica nanoparticles[J]. China Powder Science and Technology, 2025, 31(2): 31-48.

[22]韦祖宇. 介孔硅酸钙和介孔硅酸镁粉体的制备及其性能研究[D]. 北京: 北京化工大学, 2025.

WEI Z Y. Preparation and performance study of mesoporous calcium silicate and mesoporous magnesium silicate powders[D]. Beijing: Beijing University of Chemical Technology. 2025.

[23]MASOOD CHAUDRY U, AHMAD H W, TARIQ M R, et al. Effect of post weld heat treatment on the microstructure and electrochemical characteristics of dissimilar material welded by butter method[J]. Materials, 2020, 13(20): 4512.

[24]LI Y, TIAN G Y, CHEN B, et al. Self-templating construction of flower-like mesoporous magnesium silicate composites from sepiolite for high-efficiency adsorption of aflatoxin B1[J]. Separation and Purification Technology, 2022, 291: 120953.

[25]NAKAMOTO K. Infrared and Raman spectra of inorganic and coordination compounds, Part B: applications in coordination, organometallic, and bioinorganic chemistry[M]. Hoboken:John Wiley & Sons, 2009.

[26]ZHANG L, ZHAO C M, JIANG Y L, et al. Effect of sodium dodecyl benzene sulfonate on morphology and structure of calcium silicate hydrate prepared via precipitation method[J]. Colloids and Surfaces A: Physicochemical and Engineering Aspects, 2018, 540: 249-255.

[27]LU S S, CUI W S, WANG R , et al. Biomimetic mineralization and characterization of hierarchically structured hydrated magnesium carbonates: the effects of sodium alginate[J]. Journal of CO2 Utilization, 2022, 56: 101848.

[28]HARRISON A L, MAVROMATIS V, OELKERS E H, et al. Solubility of the hydrated Mg-carbonates nesquehonite and dypingite from 5 to 35 ℃: implications for CO2 storage and the relative stability of Mg-carbonates[J]. Chemical Geology, 2019, 504: 123-135.

[29]MAZUR M, MLYNARIK V, VALKO M, et al. The time evolution of the sol-gel process: 29Si NMR study of the hydrolysis and condensation reactions of tetraethoxysilane[J]. Applied Magnetic Resonance, 2000, 18(2): 187-197.

[30]SATO Y,SUGIMOTO A,IWASHINA T, et al. Hydrolysis and condensation behavior of tetraethoxysilane, hexaethoxydisiloxane, and octaethoxytrisiloxane[J]. Journal of Sol-Gel Science and Technology, 2023, 108(2): 377-391.

[31]BLITZ J P, MEVERDEN C C, DIEBEL R E. Reactions of dibutylmagnesium with modified silica gel surfaces[J]. Langmuir, 1998, 14(5): 1122-1129.

[32]SOBOTA P, PRZYBYLAK S, EJFLER J, et al. Synthesis and structural characterization of magnesium and titanium siloxanes[J]. Inorganica Chimica Acta, 2002, 334: 159-164.

[33]JIANG C Q, RAMTEKE D D, LI J, et al. Preparation and characterization of binary Mg-silicate glasses via sol-gel route[J]. Journal of Non-crystalline Solids, 2023, 606: 122204.

[34]WANG C F, LIU B F, WEI P X, et al. Optimization of Mg-Al layered double hydroxide film preparation and corrosion resistance study on AZ91D Mg Alloy by multivariate polynomial regression fitting[J].ACS Omega,2024,9(17):19158-19168.

[35]TARZANAGH Y J, SEIFZADEH D, SAMADIANFARD R. Combining the 8-hydroxyquinoline intercalated layered double hydroxide film and sol-gel coating for active corrosion protection of the magnesium alloy[J].International Journal of Minerals, Metallurgy and Materials, 2022, 29(3): 536-546.

[36]YIN W Z, LIU J Y, WANG Y L, et al. New insights into chitosan-induced biomimetic mineralization of hierarchical spherical nesquehonite: characterization, DFT calculations and construction mechanism[J]. Fuel, 2024, 372: 132169.

[37]韩亚, 张晨, 李娜, 等. 两种新型复合改性生物炭对Cr(Ⅵ)吸附机理研究[J/OL]. 河南科学. (2026-01-23)[2026-02-03]. https://link.cnki.net/urlid/41.1084.N.20260122.1535.002.

HAN Y,ZHANG C,LI N,et al.Study on adsorption mechanisms of two novel composite-modified biochars for Cr(VI)[J/OL]. Henan Science.(2026-01-23)[2026-02-03]. https://link.cnki.net/urlid/41.1084.N.20260122.1535.002.

[38]YANG R, LI D W, LI A M, et al. Adsorption properties and mechanisms of palygorskite for removal of various ionic dyes from water[J]. Applied Clay Science, 2018, 151: 20-28.

[39]李海飞,刘怡君,罗波,等. 没食子酰糖类化合物的合成及络合金属锗[J]. 精细化工,2025,42(11): 2535-2542.

LI H F, LIU Y J, LUO B, et al. Synthesis of galloyl glycoside compounds and their complexation with germanium[J]. Fine Chemicals, 2025, 42(11): 2535-2542.

[40]张伟,罗旭彪,欧阳婷,等.吸附法去除水中典型有机络合态重金属的研究进展[J].工业水处理,2024,44(6): 60-68.

ZHANG W, LUO X B, OU Y T, et al. Research progress on removal of typical prganically complexed heavy metals from water by adsorption method[J]. Industrial Water Treatment, 2024, 44(6): 60-68.

[41]王凯,刘恒源,邹丽飞,等. 聚乙烯亚胺功能化磁性微球合成及对Cu2+的吸附性能研究[J/OL]. 化工新型材料. (2025-10-16)[2026-02-03]. https://doi.org/10.19817/j.cnki.issn1006-3536.2026.04.001.

WANG K, LIU H Y, ZHOU L F. Et al. Synthesis of polyethyleneimine-functionalized magnetic microspheres and their adsorption performance for Cu2+[J]. New Chemical Materials.(2025-10-16)[2026-02-03]. https://doi.org/10.19817/j.cnki.issn1006-3536.2026.04.001.

[42]徐昕玮,张丽杰,滕亮,等. 球孢白僵菌Z1对典型重金属的吸附性能与动力学研究[J/OL]. 重庆理工大学学报(自然科学). (2026-01-15)[2026-02-03]. https://link.cnki.net/urlid/50.1205.T.20260115.1022.002.

XUN X W, ZHANG L J, TENG L, et al. Study on adsorption performance and kinetics of eauveria bassiana z1 for typical heavy metals[J]. Journal of Chongqing University of Technology (Natural Science). (2026-01-15)[2026-02-03]. https://link.cnki.net/urlid/50.1205.T.20260115.1022.002.

[43]文琪,宋勇,黄旭娟,等. 硫酸镁和硫酸铵浸矿对离子吸附型稀土与重金属的释放与影响机理[J]. 有色金属工程,2024,14(11): 174-182.

WEN Q, SONG Y, WANG X J, et al. Release and mechanistic impacts of magnesium sulfate and ammonium sulfate leaching on ion-adsorbed rare earths and heavy metals in ores[J]. Nonferrous Metals, 2024, 14(11): 174-182.

[44] NIETO-MARQUEZ A, PINEDO-FLORES A, PICASSO G, et al. Selective adsorption of Pb2+, Cr3+ and Cd2+ mixtures on activated carbons prepared from waste tires[J]. Journal of Environmental Chemical Engineering, 2017, 5(1): 1060-1067.

[45]ZHAO G X, WU X L, TAN X L, et al. Sorption of heavy metal ions from aqueous solutions: a review[J]. Open Colloid Science Journal, 2011, 4(1): 19-31.

[46]鲍静,冯拥军,潘勇,等. 改性多孔硅酸镁纳米材料对废水中Ni2+的吸附性能[J].南京工业大学学报(自然科学版), 2023, 45(6): 647-653.

BAO J, FENG Y J, PAN Y, et al. Adsorption performance of modified porous magnesium silicate nanomaterials for Ni2+ in wastewater[J]. Journal of Nanjing University of Technology (Natural Science Edition). 2023, 45(6): 647-653.

[47]AKSU Z. Biosorption of reactive dyes by dried activated sludge: equilibrium and kinetic modelling[J]. Biochemical Engineering Journal, 2001, 7(1): 79-84.

[48]FERRERO F. Adsorption of methylene blue on magnesium silicate: kinetics, equilibria and comparison with other adsorbents[J]. Journal of Environmental Sciences, 2010, 22(3): 467-473.

[49]MOHANTA D, AHMARUZZAMAN M. Bio-inspired adsorption of arsenite and fluoride from aqueous solutions using activated carbon@ SnO2 nanocomposites: isotherms, kinetics, thermodynamics, cost estimation and regeneration studies[J]. Journal of Environmental Chemical Engineering, 2018, 6(1): 356-366.

[50]HUI K S, CHAO C Y H, KOT S C. Removal of mixed heavy metal ions in wastewater by zeolite 4A and residual products from recycled coal fly ash[J]. Journal of Hazardous Materials, 2005, 127(1/2/3): 89-101.