CN104478256A - Calcium-magnesium carbonate gel material and preparation method thereof - Google Patents

Calcium-magnesium carbonate gel material and preparation method thereof Download PDF

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CN104478256A
CN104478256A CN201410660848.7A CN201410660848A CN104478256A CN 104478256 A CN104478256 A CN 104478256A CN 201410660848 A CN201410660848 A CN 201410660848A CN 104478256 A CN104478256 A CN 104478256A
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slag
cement
calcium carbonate
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magnesium
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CN104478256B (en
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莫立武
邓敏
张丰
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Suzhou Bonouqiang New Material Technology Co ltd
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Nanjing Tech University
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Abstract

The invention discloses a calcium-magnesium carbonate gel material and a preparation method thereof. The gel material is prepared from the following components in percentage by mass: not smaller than 60% and not greater than 100% of industrial alkaline wastes, not smaller than 0 and not greater than 20% of cement and not smaller than 0 and not greater than 20% of active magnesium oxide through CO2 carbonization. According to the calcium-magnesium carbonate gel material and the preparation method thereof disclosed by the invention, a great deal of solid wastes is utilized, so that the calcium-magnesium carbonate gel material is environmentally friendly, low in cost, excellent in breaking strength and compressive strength; and the greenhouse gas CO2 is recycled to promote the energy conservation and emission reduction in the building material industry.

Description

Magnesium calcium carbonate gelling material and preparation method thereof
Technical field
The invention belongs to building material technical field, be specifically related to a kind of magnesium calcium carbonate gelling material and preparation method thereof.
Background technology
Reduce CO 2greenhouse gas emission, containment global warming are the focuses that the world today pays close attention to.Cement is the main gelling component of preparation conventional concrete material, its production process CO 2quantity discharged is large, often produces 1t cement clinker and about discharges 0.7-0.8tCO 2.Cement industry CO 2quantity discharged accounts for mankind's activity and produces CO 2the 5%-7% of total amount.China's cement output in 2013, up to 2,400,000,000 tons, occupies the first in the world in continuous 27 years.Obviously, China Cement industry CO 2the situation reduced discharging is severeer.Along with the sustainable development of economic society, future will continue to increase the demand of cement concrete, how reduce Cement industry CO 2discharge has caused countries in the world to pay attention to.Application and Development green, environmental protection, energy-saving cement, promote that the Sustainable development of cement concrete material of construction is extremely urgent.Development of new cement and other low-carbon (LC) gelling material are Cement industry CO 2the effective way reduced discharging.
In fact, cement concrete material, can with the CO in air in long service process 2there is carburizing reagent, thus decrease the carbon emission when prepared by concrete.But CO under field conditions (factors) 2concentration extremely low (being about 0.04%), reacts slower.Also high concentration CO is utilized 2curing concrete, can not only Quick high strength to form calcium carbonate, and can absorption portion CO 2, be conducive to reducing CO 2discharge.Even directly use CO 2carbonization trade waste can prepare the building material made with good mechanical properties.
Chinese invention CN101058213 proposes calcic solid waste carbonating and prepares material of construction, but limits the low waste of calcium component content as the application of flyash.Chinese invention CN103771780 adopts solid waste (slag, slag, flyash, coal gangue etc.) and alkaline excitation material (carbide slag, silicate cement or waste cement) to mix, and recarbonizes and prepare material of construction after prehydration.Chinese invention CN101423354 adopts paper mill sludge, slag, slag and discarded concrete as main raw, mixes 2-10%NaHCO 3, the agent of water glass equal excitation, accelerated carbonation temperature is 20-150 DEG C, and the accelerated carbonation time is 2-18h.Univ cambridge uk researchist uses the mixture of extra light calcined magnesia or activated magnesia and flyash, under normal temperature condition, and CO 2concentration is accelerated carbonation reactive magnesium oxide cements under 5%-20% condition, prepares the building material made that intensity is higher, but the required time is 28d.
Summary of the invention
The technical problem solved: the invention provides a kind of magnesium calcium carbonate gelling material and preparation method thereof, recycling greenhouse gases CO 2, and product folding strength and ultimate compression strength excellence.
Technical scheme: magnesium calcium carbonate gelling material, described gelling material by industrial alkaline waste residue, activated magnesia and cement through CO 2carbonization preparation and obtain, described component by mass percentage, 60%≤industrial alkaline waste residue≤100%, 0≤cement≤20%, 0≤activated magnesia≤20%.
Described industrial alkaline waste residue is at least one in ground slag, carbide slag, slag, flyash, magnesium slag, cement flue Dust.
The specific surface area of described activated magnesia is not less than 20m 2/ kg, activity index is not more than 400s, and grain diameter is less than 80 microns.
The preparation method of above-mentioned magnesium calcium carbonate gelling material, industrial alkaline waste residue, activated magnesia and cement are through CO 2carbonization, wherein CO during carbonization 2concentration is 15%-99.9%, and pressure is 0.1-3.0MPa, and carbonization temperature is 20-60 DEG C, CO 2the time of maintenance is 3h-14d.
Described industrial alkaline waste residue is carbide slag and slag, and by percentage to the quality, carbide slag accounts for 10%, slag accounts for 90%.
Described CO 2concentration was 99.9%, and pressure is 0.5MPa, and carbonization temperature is 30 DEG C, through reaction in 24 hours.
Know-why: in conjunction with more industrial residue, develop intensity more fast, the present invention adopts high-concentration industrial CO 2and improve CO 2pressure, accelerates CO 2rapid diffusion in test specimen, accelerated carbonation also improves carbonizing degree.The technical scheme adopted adopts activated magnesia, alkaline industrial residue, cement etc. as starting material, the industrial CO that employing pressure is 0.1-3.0MPa, concentration is 15%-99.9% 2carry out maintenance, temperature is 20-60 DEG C, accelerated carbonation, obtains the novel gelled material using calcium carbonate, magnesium calcium carbonate and serial carbonic acid magnesium salts as main cementing component.
The alkaline industrial residue, the activated magnesia, on a small quantity cement that are rich in magnesium calcium are mixed with appropriate water, make the goods of definite shape, leave standstill 1-3 days, the demoulding, then puts into special carbonizing plant, passes into CO 2gas carries out maintenance, obtains magnesium calcium carbonate gelled material product.
Alkaline industrial residue involved in the present invention mainly comprises at least one in ground slag, carbide slag, slag, flyash, magnesium slag, cement flue Dust etc.
The chemical reaction forming magnesium calcium carbonate in the present invention mainly contains:
CO 2(g)+H 2O(aq)→CO 3 2-(aq)+2H +(aq) Eq(1)
Ca 2+(aq)+CO 3 2-(aq)→CaCO 3(s) Eq(2)
Ca 2+(aq)+Mg 2+(aq)+CO 3 2-(aq)→Ca xMg (1-x)CO 3(s) Eq(3)
Mg 2+(aq)+CO 3 2-(aq)+xH 2O(aq)→MgCO 3·xH 2O(s) Eq(4)
Principal feature of the present invention is, in the forming process of calcium carbonate, form magnesium calcium carbonate, change crystal morphology and bonding, make microtexture finer and close, gelling material mechanical strength is better.High pressure CO 2, make it spread faster.Simultaneously stability CO 2, prepare the carbonate gelatinous material of low-carbon (LC).
Beneficial effect: utilize that a large amount of solid waste, environmental protection, cost are low, product folding strength and ultimate compression strength excellent, recycling greenhouse gases CO 2, promote the energy-saving and emission-reduction of building material industry.
Accompanying drawing explanation
Fig. 1 is the SEM figure of concrete example magnesium calcium carbonate product.The test specimen that this figure is flyash, prepared by activated magnesia and a small amount of cement, through 99.9% concentration C O 2after carbonized maintaining, in test specimen, form the SEM shape appearance figure of magnesium calcium carbonate product.As seen from the figure, define a large amount of close-connected Spherical magnesium carbonate calcium product, between product, bonding closely, is conducive to the raising of mechanical strength.
Fig. 2 is magnesium calcium carbonate product backscattered electron figure; (MC: magnesium calcium carbonate, Fa: flyash, Br: magnesium hydroxide);
Fig. 3 is magnesium calcium carbonate product backscattered electron figure; (S: slag, MC: magnesium calcium carbonate, N: magnesium carbonate trihydrate);
Fig. 2 is activated magnesia, flyash and a small amount of cement admixture, through CO 2after carbonized maintaining, define a large amount of magnesium calcium carbonate products, flyash is cemented together.Fig. 3 is activated magnesia, slag and a small amount of cement admixture, through CO 2after carbonized maintaining, define a large amount of magnesium calcium carbonate products and magnesium carbonate trihydrate product, formation imporosity cementing with slag.
Embodiment
Following examples further illustrate content of the present invention, but should not be construed as limitation of the present invention.Without departing from the spirit and substance of the case in the present invention, the amendment do the inventive method, step or condition and replacement, all belong to scope of the present invention.If do not specialize, the conventional means that technique means used in embodiment is well known to those skilled in the art.
Embodiment 1
Flyash, activated magnesia and cement is selected to be main raw material.By percentage to the quality, flyash accounts for 50%, activated magnesia accounts for 20%, cement accounts for 30%.The activity index of activated magnesia is 50s, and specific surface area is 55m 2/ g.Cement is silicate cement, and specific surface area is 420m 2/ kg.Flyash takes from fuel-burning power plant, Nanjing, and CaO content is 4.8% (mass ratio).By above-mentioned three kinds of starting material Homogeneous phase mixing, add water, stir and make uniform slurry, build shaping 40 × 40 × 40mm test specimen.Adopt CO 2maintenance, CO 2concentration was 99.9%, and pressure is 1.5MPa, and carbonization temperature is 40 DEG C, through reaction in 3 hours.After carburizing reagent, weight increases (i.e. absorbing carbon dioxide) about 11%, and test specimen folding strength is 4.9MPa, and ultimate compression strength is 45MPa.
Embodiment 2
Ground slag, activated magnesia (with embodiment 1) and cement (with embodiment 1) is selected to be main raw material.Ground slag specific surface area is 450m 2/ kg, CaO content is 36%, content of MgO is 12% (mass ratio).By percentage to the quality, slag accounts for 60%, activated magnesia accounts for 20%, cement accounts for 20%.By above-mentioned three kinds of starting material Homogeneous phase mixing, add water, stir and make uniform slurry, build shaping 40 × 40 × 40mm test specimen.Adopt CO 2maintenance, CO 2concentration was 99.9%, and pressure is 1.0MPa, and carbonization temperature is 40 DEG C, through reaction in 6 hours.
After carburizing reagent, weight increases (i.e. absorbing carbon dioxide) about 13%, and test specimen folding strength is 5.3MPa, and ultimate compression strength is 51MPa.
Embodiment 3
Slag, activated magnesia (with embodiment 1) and cement (with embodiment 1) is selected to be main raw material.In slag, CaO content is 42%, and content of MgO is 11%.By percentage to the quality, slag accounts for 80%, activated magnesia accounts for 10%, cement accounts for 10%.By above-mentioned three kinds of starting material Homogeneous phase mixing, add water, stir and make uniform slurry, build shaping 40 × 40 × 40mm test specimen.Adopt CO 2maintenance, CO 2concentration was 99.9%, and pressure is 2.0MPa, and carbonization temperature is 50 DEG C, through reaction in 3 hours.
After carburizing reagent, weight increases (i.e. absorbing carbon dioxide) about 16%, and test specimen folding strength is 5.9MPa, and ultimate compression strength is 57MPa.
Embodiment 4
Carbide slag and slag (with embodiment 3) is selected to be main raw material.In carbide slag, CaO content is 60% (mass ratio).By percentage to the quality, carbide slag accounts for 10%, slag accounts for 90%.By above-mentioned two kinds of starting material Homogeneous phase mixing, add water, stir and make uniform slurry, build shaping 40 × 40 × 40mm test specimen.Adopt CO 2maintenance, CO 2concentration was 99.9%, and pressure is 0.5MPa, and carbonization temperature is 30 DEG C, through reaction in 24 hours.After carburizing reagent, weight increases (i.e. absorbing carbon dioxide) about 19%, and test specimen folding strength is 6.7MPa, and ultimate compression strength is 65MPa.
Embodiment 5
Carbide slag (with embodiment 4), magnesium slag and cement flue Dust is selected to be main raw material.In magnesium slag, CaO content is 43%, and content of MgO is 17% (mass ratio).In cement flue Dust, CaO content is 45%, and content of MgO is 2% (mass ratio).By percentage to the quality, carbide slag accounts for 20%, magnesium slag accounts for 60%, cement flue Dust accounts for 20%.By above-mentioned three kinds of starting material Homogeneous phase mixing, add water, stir and make uniform slurry, build shaping 40 × 40 × 40mm test specimen.Adopt CO 2maintenance, CO 2concentration was 20%, and pressure is 0.1MPa, and carbonization temperature is 30 DEG C, through reaction in 24 hours.After carburizing reagent, weight increases (i.e. absorbing carbon dioxide) about 20%, and test specimen folding strength is 6.3MPa, and ultimate compression strength is 60MPa.

Claims (6)

1. magnesium calcium carbonate gelling material, is characterized in that described gelling material by industrial alkaline waste residue, activated magnesia and cement through CO 2carbonization preparation and obtain, described component by mass percentage, 60%≤industrial alkaline waste residue≤100%, 0≤cement≤20%, 0≤activated magnesia≤20%.
2. magnesium calcium carbonate gelling material according to claim 1, is characterized in that described industrial alkaline waste residue is at least one in ground slag, carbide slag, slag, flyash, magnesium slag, cement flue Dust.
3. magnesium calcium carbonate gelling material according to claim 1, is characterized in that the specific surface area of described activated magnesia is not less than 20m 2/ kg, activity index is not more than 400 s, and grain diameter is less than 80 microns.
4. the preparation method of magnesium calcium carbonate gelling material described in claim 1, is characterized in that industrial alkaline waste residue, activated magnesia and cement are through CO 2carbonization, wherein CO during carbonization 2concentration is 15%-99.9%, and pressure is 0.1-3.0MPa, and carbonization temperature is 20-60 DEG C, CO 2the time of maintenance is 3h-14d.
5. the preparation method of magnesium calcium carbonate gelling material according to claim 4, is characterized in that industrial alkaline waste residue is carbide slag and slag, and by percentage to the quality, carbide slag accounts for 10%, slag accounts for 90%.
6. the preparation method of magnesium calcium carbonate gelling material according to claim 4, is characterized in that CO 2concentration was 99.9%, and pressure is 0.5 MPa, and carbonization temperature is 30 DEG C, through reaction in 24 hours.
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Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107056202A (en) * 2017-05-31 2017-08-18 盐城工学院 Carbonization slag cement prepares accelerator and its application process of low-carbon binder materials
CN107324753A (en) * 2017-04-10 2017-11-07 南京工业大学 A kind of carbonate binder materials and preparation method thereof
CN109485360A (en) * 2018-12-28 2019-03-19 西安交通大学 A kind of building moulding material produced using magnesium-smelting silicothermic process waste residue as raw material and its method
CN109704698A (en) * 2019-01-21 2019-05-03 北京科技大学 A method of utilizing the standby low cost carbonization building materials of prepared from steel slag
CN110818356A (en) * 2019-12-02 2020-02-21 武汉理工大学 Preparation method of high-performance carbonized reinforced concrete
CN111892363A (en) * 2020-07-28 2020-11-06 西安交通大学 Magnesium slag cementing material and forming process method thereof
CN113321477A (en) * 2021-06-16 2021-08-31 乌海市东孚水泥有限责任公司 Carbonate building material and manufacturing method thereof
CN113929326A (en) * 2021-11-25 2022-01-14 青岛海泰能源科学技术研究院 Preparation method and preparation system of cement
CN113968750A (en) * 2021-10-28 2022-01-25 山东汉博昱洲新材料有限公司 Based on deposition method and CO2Artificial stone for driving consolidation and preparation method thereof
CN113979708A (en) * 2021-11-25 2022-01-28 宁波中淳高科股份有限公司 Baking-free carbonized cement soil building block and preparation method thereof
CN115180882A (en) * 2022-05-30 2022-10-14 湖北工业大学 Preparation method of endogenous carbonized light board
CN115466093A (en) * 2022-10-18 2022-12-13 江苏科技大学 Method for carbonizing and curing heavy metal in fly ash based on EDTA (ethylene diamine tetraacetic acid) -calcium-silicon solid waste-light-burned magnesium oxide
CN115724643A (en) * 2022-11-01 2023-03-03 辽宁科技大学 Hydration reaction controllable high-fire-resistance magnesium phosphate cement-based material and preparation method thereof
CN116102272A (en) * 2023-01-06 2023-05-12 湖北工业大学 Green gel material capable of realizing carbon reduction and carbon fixation and preparation method thereof

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101058213A (en) * 2007-06-01 2007-10-24 济南大学 Method for preparing building material with carbonization maintenance waste
CN101343155A (en) * 2008-08-29 2009-01-14 济南大学 Regeneration aggregate made of carbonized maintaining castoff
CN101357829A (en) * 2008-08-28 2009-02-04 济南大学 Strengthening agent for construction material prepared by carbonizing curing waste
US20130000520A1 (en) * 2011-06-30 2013-01-03 NTH Consultants, Ltd. Hybrid magnesium cement and method of manufacture
CN103771780A (en) * 2014-01-01 2014-05-07 大连理工大学 Method for preparing building material products through hydration-carbonation coupling technique
CN104045251A (en) * 2014-05-29 2014-09-17 湖南大学 Method for carbon dioxide strengthening of recycled concrete aggregate

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101058213A (en) * 2007-06-01 2007-10-24 济南大学 Method for preparing building material with carbonization maintenance waste
CN101357829A (en) * 2008-08-28 2009-02-04 济南大学 Strengthening agent for construction material prepared by carbonizing curing waste
CN101343155A (en) * 2008-08-29 2009-01-14 济南大学 Regeneration aggregate made of carbonized maintaining castoff
US20130000520A1 (en) * 2011-06-30 2013-01-03 NTH Consultants, Ltd. Hybrid magnesium cement and method of manufacture
CN103771780A (en) * 2014-01-01 2014-05-07 大连理工大学 Method for preparing building material products through hydration-carbonation coupling technique
CN104045251A (en) * 2014-05-29 2014-09-17 湖南大学 Method for carbon dioxide strengthening of recycled concrete aggregate

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
莫立武等: "高浓度二氧化碳碳化活性氧化镁水泥浆体的显微结构", 《硅酸盐学报》 *

Cited By (24)

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Publication number Priority date Publication date Assignee Title
CN107324753A (en) * 2017-04-10 2017-11-07 南京工业大学 A kind of carbonate binder materials and preparation method thereof
CN107324753B (en) * 2017-04-10 2020-01-17 南京工业大学 Carbonate cementing material and preparation method thereof
CN107056202B (en) * 2017-05-31 2019-11-08 盐城工学院 Carbonization slag cement prepares the promotor and its application method of low-carbon cementitious material
CN107056202A (en) * 2017-05-31 2017-08-18 盐城工学院 Carbonization slag cement prepares accelerator and its application process of low-carbon binder materials
CN109485360B (en) * 2018-12-28 2020-11-10 西安交通大学 Building forming material produced by taking waste residues generated in magnesium smelting by silicothermic process as raw materials and method thereof
CN109485360A (en) * 2018-12-28 2019-03-19 西安交通大学 A kind of building moulding material produced using magnesium-smelting silicothermic process waste residue as raw material and its method
CN109704698A (en) * 2019-01-21 2019-05-03 北京科技大学 A method of utilizing the standby low cost carbonization building materials of prepared from steel slag
CN110818356A (en) * 2019-12-02 2020-02-21 武汉理工大学 Preparation method of high-performance carbonized reinforced concrete
CN110818356B (en) * 2019-12-02 2021-12-07 武汉理工大学 Preparation method of high-performance carbonized reinforced concrete
CN111892363A (en) * 2020-07-28 2020-11-06 西安交通大学 Magnesium slag cementing material and forming process method thereof
CN111892363B (en) * 2020-07-28 2021-10-19 西安交通大学 Magnesium slag cementing material and forming process method thereof
CN113321477A (en) * 2021-06-16 2021-08-31 乌海市东孚水泥有限责任公司 Carbonate building material and manufacturing method thereof
CN113321477B (en) * 2021-06-16 2022-07-15 乌海市东孚水泥有限责任公司 Carbonate building material and preparation method thereof
CN113968750A (en) * 2021-10-28 2022-01-25 山东汉博昱洲新材料有限公司 Based on deposition method and CO2Artificial stone for driving consolidation and preparation method thereof
CN113929326A (en) * 2021-11-25 2022-01-14 青岛海泰能源科学技术研究院 Preparation method and preparation system of cement
CN113979708A (en) * 2021-11-25 2022-01-28 宁波中淳高科股份有限公司 Baking-free carbonized cement soil building block and preparation method thereof
CN113929326B (en) * 2021-11-25 2023-02-28 青岛海泰能源科学技术研究院 Preparation method and preparation system of cement
CN115180882A (en) * 2022-05-30 2022-10-14 湖北工业大学 Preparation method of endogenous carbonized light board
CN115180882B (en) * 2022-05-30 2023-06-16 湖北工业大学 Preparation method of endogenous carbonized light board
CN115466093A (en) * 2022-10-18 2022-12-13 江苏科技大学 Method for carbonizing and curing heavy metal in fly ash based on EDTA (ethylene diamine tetraacetic acid) -calcium-silicon solid waste-light-burned magnesium oxide
CN115466093B (en) * 2022-10-18 2023-06-16 江苏科技大学 Method for carbonizing and solidifying fly ash heavy metal based on EDTA-calcium siliceous solid waste-light burned magnesia
CN115724643A (en) * 2022-11-01 2023-03-03 辽宁科技大学 Hydration reaction controllable high-fire-resistance magnesium phosphate cement-based material and preparation method thereof
CN115724643B (en) * 2022-11-01 2024-02-20 辽宁科技大学 High-fire-resistance magnesium phosphate cement-based material capable of controlling hydration reaction and prolonging setting time and preparation method thereof
CN116102272A (en) * 2023-01-06 2023-05-12 湖北工业大学 Green gel material capable of realizing carbon reduction and carbon fixation and preparation method thereof

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