[go: up one dir, main page]

CN118791323B - Synergist for solid waste-based cementing material and preparation method thereof - Google Patents

Synergist for solid waste-based cementing material and preparation method thereof Download PDF

Info

Publication number
CN118791323B
CN118791323B CN202411259449.XA CN202411259449A CN118791323B CN 118791323 B CN118791323 B CN 118791323B CN 202411259449 A CN202411259449 A CN 202411259449A CN 118791323 B CN118791323 B CN 118791323B
Authority
CN
China
Prior art keywords
phase component
liquid phase
sodium
organic liquid
mass ratio
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN202411259449.XA
Other languages
Chinese (zh)
Other versions
CN118791323A (en
Inventor
马梁
张广田
林双艮
刘东基
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Anhui Luhong New Material Technology Co ltd
Hebei Academy Of Architectural Sciences Co ltd
Original Assignee
Anhui Luhong New Material Technology Co ltd
Hebei Academy Of Architectural Sciences Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Anhui Luhong New Material Technology Co ltd, Hebei Academy Of Architectural Sciences Co ltd filed Critical Anhui Luhong New Material Technology Co ltd
Priority to CN202411259449.XA priority Critical patent/CN118791323B/en
Publication of CN118791323A publication Critical patent/CN118791323A/en
Application granted granted Critical
Publication of CN118791323B publication Critical patent/CN118791323B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08FMACROMOLECULAR COMPOUNDS OBTAINED BY REACTIONS ONLY INVOLVING CARBON-TO-CARBON UNSATURATED BONDS
    • C08F222/00Copolymers of compounds having one or more unsaturated aliphatic radicals, each having only one carbon-to-carbon double bond, and at least one being terminated by a carboxyl radical and containing at least one other carboxyl radical in the molecule; Salts, anhydrides, esters, amides, imides, or nitriles thereof
    • C08F222/10Esters
    • C08F222/12Esters of phenols or saturated alcohols
    • C08F222/22Esters containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/04Waste materials; Refuse
    • C04B18/0409Waste from the purification of bauxite, e.g. red mud
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/04Waste materials; Refuse
    • C04B18/12Waste materials; Refuse from quarries, mining or the like
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B24/00Use of organic materials as active ingredients for mortars, concrete or artificial stone, e.g. plasticisers
    • C04B24/24Macromolecular compounds
    • C04B24/26Macromolecular compounds obtained by reactions only involving carbon-to-carbon unsaturated bonds
    • C04B24/2652Nitrogen containing polymers, e.g. polyacrylamides, polyacrylonitriles
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B40/00Processes, in general, for influencing or modifying the properties of mortars, concrete or artificial stone compositions, e.g. their setting or hardening ability
    • C04B40/0028Aspects relating to the mixing step of the mortar preparation
    • C04B40/0039Premixtures of ingredients
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08FMACROMOLECULAR COMPOUNDS OBTAINED BY REACTIONS ONLY INVOLVING CARBON-TO-CARBON UNSATURATED BONDS
    • C08F220/00Copolymers of compounds having one or more unsaturated aliphatic radicals, each having only one carbon-to-carbon double bond, and only one being terminated by only one carboxyl radical or a salt, anhydride ester, amide, imide or nitrile thereof
    • C08F220/02Monocarboxylic acids having less than ten carbon atoms; Derivatives thereof
    • C08F220/04Acids; Metal salts or ammonium salts thereof
    • C08F220/06Acrylic acid; Methacrylic acid; Metal salts or ammonium salts thereof
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/10Production of cement, e.g. improving or optimising the production methods; Cement grinding

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Organic Chemistry (AREA)
  • Structural Engineering (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Civil Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Medicinal Chemistry (AREA)
  • Polymers & Plastics (AREA)
  • Mining & Mineral Resources (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The invention provides a synergist for a solid waste-based cementing material and a preparation method thereof, belonging to the technical field of solid waste recycling. The organic liquid phase component is obtained by mixing triethanolamine and triisopropanolamine with maleic anhydride and ferric chloride hexahydrate respectively, then heating and reacting, mixing the intermediate obtained by the reaction with sodium methacrylate and concentrated sulfuric acid respectively, then heating and reacting, finally mixing according to a certain proportion, the inorganic liquid phase component is obtained by filtering the red mud and gangue powder after alkali melting and hydrothermal reaction, and the inorganic solid phase component is obtained by grinding the filter residue obtained by filtering the red mud and gangue powder after alkali melting and hydrothermal reaction. The invention plays a synergistic effect through the three components, is beneficial to the generation of AFt and C-S-H, ensures that the strength is rapidly formed, ensures that the strength is continuously increased in the later stage of hydration, and realizes the effects of early strength and high strength of the solid waste base cementing material.

Description

Synergist for solid waste-based cementing material and preparation method thereof
Technical Field
The invention belongs to the technical field of solid waste recycling, and particularly relates to a synergist for a solid waste-based cementing material and a preparation method thereof.
Background
The solid waste-based cementing material is used as a cement substitute product, can effectively reduce the CO 2 emission in the building field while improving the utilization rate of solid waste resources, accords with the double-carbon policy, and has important practical significance for promoting sustainable green development.
At present, the solid waste-based cementing material has the common problems of long setting time, low early strength, increased later strength, hypodynamia, difficult construction and the like.
Disclosure of Invention
The embodiment of the invention provides a synergist for a solid waste-based cementing material and a preparation method thereof, which are prepared from red mud and coal gangue, and aim to solve the problems of low early strength and increased later strength and hypodynamia of the solid waste-based cementing material.
In order to achieve the above purpose, the invention adopts the technical scheme that the synergist for the solid waste-based cementing material is characterized by comprising, by mass, 10-25 parts of an organic liquid phase component, 15-25 parts of an inorganic liquid phase component and 50-70 parts of an inorganic solid phase component.
The invention provides a preparation method of a synergist for a solid waste based cementing material, which comprises the steps of preparing an organic liquid phase component, preparing an inorganic liquid phase component and preparing an inorganic solid phase component, wherein the organic liquid phase component is prepared by mixing triethanolamine, triisopropanolamine, maleic anhydride and ferric chloride hexahydrate respectively according to a certain proportion, heating for reaction, modifying by sodium methacrylate and finally mixing according to a certain proportion, the inorganic liquid phase component is a filtrate obtained by filtering red mud and coal gangue powder after alkali melting and hydrothermal reaction, and the inorganic solid phase component is obtained by grinding filter residues obtained by filtering after the red mud and the coal gangue powder are subjected to alkali melting and hydrothermal reaction.
With reference to the second aspect, in one possible manner, the organic liquid phase component is prepared according to the following method:
Step one, mixing maleic anhydride, triethanolamine and ferric chloride hexahydrate according to the mass ratio of 1:1.2-2.0:0.05-0.2, and reacting to obtain a liquid a;
Preparing three parts of deionized water, wherein the mass of each part of deionized water is 0.5-1.0 times of the consumption of maleic anhydride, adding sodium carbonate into one part of deionized water until the deionized water is excessive, adding sodium chloride into one part of deionized water until the deionized water is excessive, adding calcium chloride into one part of deionized water until the deionized water is excessive, and retaining excessive sodium carbonate, sodium chloride and calcium chloride to obtain a sodium carbonate solution, a sodium chloride solution and a calcium chloride solution;
Mixing the intermediate a with sodium methacrylate and concentrated sulfuric acid in a three-neck flask according to a mass ratio of 259:68-103:3-5, heating at 70-95 ℃ for reaction, slowly dropwise adding sodium methacrylate with an initial dosage of 1-3 times of the mass of the sodium methacrylate by using a separating funnel during the reaction, controlling the dropwise adding time to be 90-150 min, and continuously reacting at the temperature for 60-120 min after the dropwise adding is finished to obtain an organic liquid phase component a, wherein the molecular formula of the organic liquid phase component a is as follows:
Step four, mixing maleic anhydride, triisopropanolamine and ferric chloride hexahydrate according to the mass ratio of 1:1.5-2.5:0.05-0.2, and reacting to obtain a liquid b;
Step five, treating the liquid b reacted in the step four according to the step two to obtain an intermediate b;
Step six, mixing the intermediate b with sodium methacrylate and concentrated sulfuric acid in a three-neck flask according to a mass ratio 289:68-103:0.15-0.25, heating and reacting at 70-95 ℃, slowly dropwise adding sodium methacrylate with an initial dosage of 1-3 times of the mass of the sodium methacrylate by using a separating funnel, controlling the dropwise adding time to be 90-150 min, and continuously reacting at the temperature for 60-120 min after the dropwise adding is finished to obtain an organic liquid phase component b, wherein the molecular formula of the organic liquid phase component b is as follows:
And seventhly, mixing the organic liquid phase component a and the organic liquid phase component b according to the mass ratio of 1:0.25-1.75 to obtain the finished organic liquid phase component.
In combination with the second aspect, in one possible manner, in the first step, maleic anhydride, triethanolamine and ferric chloride hexahydrate are mixed according to a proportion and then reacted for 120-180 min at 70-80 ℃ to obtain the liquid a.
With reference to the second aspect, in one implementation manner, in the second step, the sodium carbonate, the sodium chloride and the calcium chloride are respectively in excess of 1-3 g in deionized water.
In combination with the second aspect, in one implementation manner, in the fourth step, maleic anhydride, triisopropanolamine and ferric chloride hexahydrate are mixed according to a mass ratio and then reacted for 120-180 min at 70-80 ℃.
With reference to the second aspect, in one possible implementation manner, the molecular weight of the organic liquid phase component a is 7000 to 8000, and the molecular weight of the organic liquid phase component b is 7500 to 9000.
With reference to the second aspect, in one possible manner, the inorganic liquid phase component and the inorganic solid phase component are prepared according to the following method:
Step one, testing the mass fractions of Al 2O3 in the gangue and the red mud by using an X-ray fluorescence spectrum, respectively marking the mass fractions as omega 1 and omega 2, crushing the gangue to be below 0.30 mm to obtain gangue particles, and then calculating the feeding mass m 1 of the gangue particles and the feeding mass m 2 of the red mud according to the following mode:
(1) When omega 1 and omega 2 are not less than 20%, the gangue particles and the red mud can be fed according to any mass ratio;
(2) When only one of omega 1 and omega 2 is not less than 20%, calculating the mass ratio range of the gangue particles to the red mud according to the proportion of (m 1ω1+m2ω2)/(m1+m2) not less than 20%;
(3) When omega 1 and omega 2 are less than 20%, adding sodium metaaluminate with the mass of m 3 except for gangue particles and red mud, and calculating the mass ratio range of the gangue particles, the red mud and the sodium metaaluminate according to (m 1ω1+m2ω2+m3)/(m1+m2+m3) to be more than or equal to 20%;
mixing materials according to the calculation result to obtain a mixed material a;
grinding the mixed material a to 400-600 m 2/kg, mixing the mixed material a and solid sodium hydroxide in a ceramic crucible according to the mass ratio of 51:8-32, uniformly stirring, transferring the mixed material a and the solid sodium hydroxide into a muffle furnace, roasting the mixed material a for 60-120 min at 550-750 ℃, taking out the mixed material b after roasting, and airing the mixed material b in a dryer to room temperature;
Adding deionized water into the roasted mixed material b to obtain slurry, wherein the adding amount is that the mass ratio of the deionized water to the roasted mixed material b is 1:6-10, transferring the slurry to a three-neck flask, and carrying out hydrothermal reaction for 90-150 min at 105-125 ℃ by using a chemical microwave reactor under the condition of heating reflux;
And fourthly, filtering the slurry after the hydrothermal reaction, obtaining liquid after filtering, namely the finished inorganic liquid phase component, and grinding filter residues again to 400-600 m 2/kg to obtain the finished inorganic solid phase component.
In combination with the second aspect, in one implementation manner, in the second step, the mixture is stirred uniformly and then transferred to a muffle furnace, and baked for 60-120 min at 550-750 ℃.
With reference to the second aspect, in one possible implementation manner, the triethanolamine, the triisopropanolamine, the maleic anhydride, the ferric chloride hexahydrate, and the sodium methacrylate are all industrial pure, and the sodium metaaluminate is analytically pure.
Compared with the prior art, the synergist for the solid waste-based cementing material and the preparation method thereof have the beneficial effects that:
(1) AFt (i.e. ettringite) is a main source of early strength of the solid waste-based cementing material, the formation of AFt cannot be separated from Al element, and a synergist is added into the solid waste-based cementing material, so that the hydration activity of the Al phase can be excited after the alkaline melting-hydrothermal reaction of red mud and coal gangue, the hydration activity is further improved under the action of an inorganic liquid phase, and meanwhile, a large amount of Al phase is contained in the inorganic liquid phase to be used as supplement, thereby promoting the formation of ettringite AFt in the early hydration stage of the solid waste-based cementing material.
(2) The alkali fusion-hydrothermal reaction process can generate a part of zeolite-like phases, and combines with Si phases in the inorganic liquid phase to facilitate the formation of hydrated calcium silicate gel (C-S-H), thereby ensuring the increase of the later strength.
(3) Because the fineness of the inorganic solid phase component and the solid waste base cementing material is finer, and the raw materials contain coal gangue, the combined system of the inorganic solid phase component and the solid waste base cementing material is easier to generate agglomeration phenomenon, and poor workability is caused. The polymer macromolecules of the organic liquid phase component can be adsorbed on the surfaces of inorganic solid phase components and solid waste base cementing materials to form an adsorption layer due to the fact that the polymer macromolecules contain negatively charged carboxylate groups, the adsorption layer can play a role in dispersing the inorganic solid phase components and the solid waste base cementing materials, the steric hindrance effect generated by long molecular chains of the organic liquid phase component a and the organic liquid phase component b can also prevent the inorganic solid phase components and the solid waste base cementing materials from agglomerating (the stretching directions of chain links of the organic liquid phase components a and b in the space are shown in fig. 2 and 3), meanwhile, the other ends of the organic liquid phase component a and the organic liquid phase component b are relatively strong in polarity due to the fact that the other ends of the organic liquid phase component a and the organic liquid phase component b contain N, and the adsorption layer has hydrophilicity, so that on one hand, a water film can play a lubricating role, meanwhile, the inorganic solid phase components and the solid waste base cementing materials can be hydrated better, and the early strength can be improved.
(4) Because the organic liquid phase component contains Na +, after carbon dioxide in the air reacts with calcium hydroxide generated by hydration of the solid waste base cementing material to generate calcium carbonate, OH - remained in the liquid phase can form NaOH with Na +, so that an alkaline environment is continuously provided for the synergist, and the continuous increase of the strength of the synergist is facilitated.
The preparation method provided by the invention can be used for preparing the early-strength and high-strength solid waste-based cementing material, wherein the organic liquid phase component mainly plays a role in dispersing the solid waste-based cementing material and the inorganic solid phase component, continuously provides an alkaline environment and provides power for later strength increase, the inorganic liquid phase component mainly plays a role in providing an alkaline environment and improving early strength, and the active components in the inorganic solid phase can react under the excitation of the inorganic liquid phase component to improve the early strength. The three components play a synergistic role, are favorable for generating AFt and C-S-H, enable the AFt and the C-S-H to form strength rapidly, enable the strength to be increased continuously in the later stage of hydration, and achieve the effect of early strength and high strength of the solid waste-based cementing material.
Drawings
FIG. 1 is a process flow diagram of a preparation method of a synergist for a solid waste-based cementing material provided by an embodiment of the invention;
FIG. 2 is a schematic view showing the extending direction of the organic liquid phase component a chain link in the space according to the embodiment of the present invention;
fig. 3 is a schematic view showing the extending direction of the organic liquid phase component b links in the space according to the embodiment of the present invention.
Detailed Description
In order to make the technical problems, technical schemes and beneficial effects to be solved more clear, the invention is further described in detail below with reference to the accompanying drawings and embodiments. It should be understood that the specific embodiments described herein are for purposes of illustration only and are not intended to limit the scope of the invention.
As two typical bulk solid wastes, the red mud and the coal gangue are accumulated in a large quantity, so that not only is the land resource wasted, but also the ecological environment is threatened, the human health is endangered, and the sustainable development of related enterprises is restricted. And red mud and coal gangue are applied and synthesized to the synergist for the solid waste-based cementing material, so that the high-value harmless utilization of the cementing material can be realized. Is beneficial to reducing the damage of red mud and coal gangue to the environment and improving the early strength and the later-stage growth strength of the solid waste-based cementing material.
The preparation method of the synergist for the solid waste-based cementing material provided by the embodiment of the invention is understood by combining with fig. 1 as follows:
Embodiment one:
In the embodiment, the proportion of the synergist for the solid waste base cementing material is 20 parts by mass of an organic liquid phase component, 25 parts by mass of an inorganic liquid phase component and 55 parts by mass of an inorganic solid phase component.
1. The preparation process of the organic liquid phase component comprises the following steps:
Step one, mixing maleic anhydride, triethanolamine and ferric chloride hexahydrate according to the mass ratio of 1:1.4:0.06, and reacting 130 min at 70 ℃ to obtain liquid a.
Preparing three parts of deionized water, wherein the mass of each part of deionized water is 0.5 times of the using amount of maleic anhydride, adding sodium carbonate to the excessive amount of 1 g parts of deionized water, adding sodium chloride to the excessive amount of 1 g parts of deionized water, adding calcium chloride to the excessive amount of 1 g parts of deionized water, retaining excessive sodium carbonate, sodium chloride and calcium chloride, sequentially passing the liquid a after the reaction in the step one through the sodium carbonate, sodium chloride and calcium chloride solution, drying the liquid a by using anhydrous sodium sulfate, and filtering the liquid a to obtain an intermediate a.
Step three, mixing the intermediate a with sodium methacrylate and concentrated sulfuric acid in a three-neck flask according to a mass ratio of 259:70:3, heating at 75 ℃ for reaction, and slowly dropwise adding sodium methacrylate with an initial dosage of 1 time of the mass of the sodium methacrylate by using a separating funnel, wherein the dropwise adding time is controlled at 100 min. After the completion of the dropwise addition, the reaction was continued at this temperature for 70 min to obtain an organic liquid phase component a.
And step four, mixing maleic anhydride, triisopropanolamine and ferric chloride hexahydrate according to the mass ratio of 1:1.8:0.08, and adding the mixture into the reaction kettle to react 130 min at the temperature of 70 ℃ to obtain liquid b.
And fifthly, treating the liquid b reacted in the step four according to the step two to obtain an intermediate b.
Step six, mixing the intermediate b with sodium methacrylate and concentrated sulfuric acid according to a mass ratio 289:75:0.16 in a three-neck flask, heating at 75 ℃ for reaction, and slowly dropwise adding sodium methacrylate with an initial dosage of 1 time of mass of sodium methacrylate by using a separating funnel during the reaction, wherein the dropwise adding time is controlled at 110 min. After the completion of the dropwise addition, the reaction was continued at this temperature for 60 min to obtain an organic liquid phase component b.
And seventhly, mixing the organic liquid phase component a and the organic liquid phase component b according to the proportion of 1:0.5 to obtain a finished organic liquid phase component.
2. The preparation process of the inorganic liquid phase component and the inorganic solid phase component is as follows:
Step one, the mass fractions of Al 2O3 in the gangue and the red mud measured by using an X-ray fluorescence spectrum are omega 1 =23.7% and omega 2 =20.3% respectively, and are not less than 20%, so that the gangue particles and the red mud can be mixed according to any proportion, and in the embodiment, the gangue particles and the red mud are mixed according to the mass ratio of 1:3, so that a mixed material a is obtained.
Grinding the mixed material a to 430 m 2/kg by utilizing a vertical mill, mixing the mixed material a and sodium hydroxide in a porcelain crucible according to the mass ratio of the mixed material a to the sodium hydroxide of 51:12, uniformly stirring, transferring the mixed material a and the sodium hydroxide into a muffle furnace, roasting for 75 minutes at 600 ℃, taking out the mixed material b after roasting, and airing the mixed material b in a dryer to room temperature.
Adding deionized water into the roasted mixed material b to obtain slurry, wherein the adding amount is that the mass ratio of the roasted mixed material b to the deionized water is 1:7, transferring the slurry to a three-neck flask, adding a little zeolite, and carrying out hydrothermal reaction at 105 ℃ by using a chemical microwave reactor under the condition of heating reflux to 90 min.
And fourthly, filtering the slurry after the hydrothermal reaction, obtaining liquid after filtering, namely the finished inorganic liquid phase component, and grinding filter residues again to 450m 2/kg to obtain the finished inorganic solid phase component.
3. The triethanolamine, triisopropanolamine, maleic anhydride, ferric chloride hexahydrate, and sodium methacrylate used in this example were all industrially pure and the sodium metaaluminate was analytically pure.
Embodiment two:
In the embodiment, the synergist for the solid waste based cementing material comprises 22 parts by mass of organic liquid phase component, 16 parts by mass of inorganic liquid phase component and 62 parts by mass of inorganic solid phase component.
1. The preparation process of the organic liquid phase component comprises the following steps:
Step one, mixing maleic anhydride, triethanolamine and ferric chloride hexahydrate according to the mass ratio of 1:1.6:0.12, and reacting 150 min at 75 ℃ to obtain liquid a.
Preparing three parts of deionized water, wherein the mass of each part of deionized water is 0.7 times of that of maleic anhydride, adding sodium carbonate to an excessive amount of 2 g, adding sodium chloride to an excessive amount of 1 g, adding calcium chloride to an excessive amount of 3g, retaining excessive sodium carbonate, sodium chloride and calcium chloride, sequentially passing the liquid a after reaction in the step one through the sodium carbonate, sodium chloride and calcium chloride solution, drying by using anhydrous sodium sulfate, and filtering to obtain an intermediate a.
Step three, mixing the intermediate a with sodium methacrylate and concentrated sulfuric acid in a three-neck flask according to a mass ratio of 259:86:4, heating at 85 ℃ for reaction, and slowly dropwise adding sodium methacrylate with the initial dosage of 2 times of the mass of the sodium methacrylate by using a separating funnel during the reaction, wherein the dropwise adding time is controlled at 110 min. After the completion of the dropwise addition, the reaction was continued at this temperature for 100 min hours to obtain an organic liquid phase component a.
And step four, mixing maleic anhydride, triisopropanolamine and ferric chloride hexahydrate according to the mass ratio of 1:2.1:0.1, and reacting 140 min at 70 ℃ to obtain liquid b.
And fifthly, treating the liquid a reacted in the step four according to the step two to obtain an intermediate b.
Step six, mixing the intermediate b with sodium methacrylate and concentrated sulfuric acid according to a mass ratio 289:85:0.19 in a three-neck flask, heating at 85 ℃ for reaction, and slowly dropwise adding sodium methacrylate with an initial dosage of 2 times of mass by using a separating funnel during the reaction, wherein the dropwise adding time is controlled at 135 min. After the completion of the dropwise addition, the reaction was continued at this temperature of 90 min to obtain an organic liquid phase component b.
And seventhly, mixing the organic liquid phase component a and the organic liquid phase component b according to the proportion of 1:1.25 to obtain a finished organic liquid phase component.
2. The preparation process of the inorganic liquid phase component and the inorganic solid phase component is as follows:
The mass fraction of Al 2O3 in the gangue and the red mud measured by using an X-ray fluorescence spectrum is omega 1 =24.0% and omega 2 =18.2%, only one of the mass fractions is not less than 20%, and the mass ratio of the gangue particles to the red mud is calculated according to the proportion of (m 1ω1+m2ω2)/(m1+m2) not less than 20%, and the gangue particles and the red mud are mixed according to the mass ratio of 3:1 in the embodiment, so that a mixed material a is obtained.
Grinding the mixed material a to 500 m 2/kg by utilizing a vertical mill, mixing the mixed material a and sodium hydroxide in a porcelain crucible according to the mass ratio of the mixed material a to the sodium hydroxide of 51:20, uniformly stirring, transferring the mixed material a and the sodium hydroxide into a muffle furnace, roasting for 95min at 650 ℃, taking out the mixed material b after roasting, and airing the mixed material b in a dryer to room temperature.
Adding deionized water into the roasted mixed material b to obtain slurry, wherein the adding amount is that the mass ratio of the roasted mixed material b to the deionized water is 1:8, transferring the slurry to a three-neck flask, adding a little zeolite, and carrying out hydrothermal reaction at 115 ℃ by using a chemical microwave reactor under the condition of heating reflux to 120 min.
And fourthly, filtering the slurry after the hydrothermal reaction, obtaining liquid after filtering, namely the finished inorganic liquid phase component, and grinding filter residues again to 495 m 2/kg to obtain the finished inorganic solid phase component.
3. The triethanolamine, triisopropanolamine, maleic anhydride, ferric chloride hexahydrate, and sodium methacrylate used in this example were all industrially pure and the sodium metaaluminate was analytically pure.
Embodiment III:
In the embodiment, the proportion of the synergist for the solid waste base cementing material is 13 parts by mass of the organic liquid phase component, 20 parts by mass of the inorganic liquid phase component and 67 parts by mass of the inorganic solid phase component.
1. The preparation process of the organic liquid phase component comprises the following steps:
step one, mixing maleic anhydride, triethanolamine and ferric chloride hexahydrate according to the mass ratio of 1:2.0:0.16, and reacting 170 min at 80 ℃ to obtain liquid a.
Step two, three parts of deionized water are prepared, wherein the mass of each part of deionized water is 0.8 times of the using amount of maleic anhydride, sodium carbonate is added to 3g in excess, sodium chloride is added to 3g in excess, calcium chloride is added to 2 g in excess, and excessive sodium carbonate, sodium chloride and calcium chloride are reserved. And (3) sequentially passing the liquid a reacted in the step (I) through the sodium carbonate, sodium chloride and calcium chloride solution, then drying with anhydrous sodium sulfate, and filtering to obtain an intermediate a.
Step three, mixing the intermediate a with sodium methacrylate and concentrated sulfuric acid in a three-neck flask according to a mass ratio of 259:96:5, heating at 90 ℃ for reaction, slowly dropwise adding sodium methacrylate which is 3 times of the initial dosage of the sodium methacrylate by using a separating funnel during the reaction, controlling the dropwise adding time to be 135 min, and continuing to react at the temperature for 110 min after the dropwise adding is finished, so as to obtain the organic liquid phase component a.
Step four, mixing maleic anhydride, triisopropanolamine and ferric chloride hexahydrate according to the mass ratio of 1:2.4:0.15, and reacting 160 min at 75 ℃ to obtain liquid b.
And fifthly, treating the liquid b reacted in the step four according to the step two to obtain an intermediate b.
Step six, mixing the intermediate b with sodium methacrylate and concentrated sulfuric acid according to a mass ratio 289:96:0.23 in a three-neck flask, heating and reacting at 95 ℃, slowly dropwise adding sodium methacrylate with an initial dosage of 2 times of the mass of the sodium methacrylate by using a separating funnel, controlling the dropwise adding time to be 145 min, and continuously reacting at the temperature 105 min after the dropwise adding is finished to obtain the organic liquid phase component b.
And seventhly, mixing the organic liquid phase component a and the organic liquid phase component b according to the proportion of 1:1.55 to obtain a finished organic liquid phase component.
2. The preparation process of the inorganic liquid phase component and the inorganic solid phase component is as follows:
The mass fractions of Al 2O3 in the gangue and the red mud measured by using an X-ray fluorescence spectrum are omega 1 =17.7% and omega 2 =19.1%, which are respectively smaller than 20%, and a certain mass of sodium metaaluminate is needed to be added, and the mass ratio range of the gangue particles, the red mud and the sodium metaaluminate (m 3) is calculated according to (m 1ω1+m2ω2+m3)/(m1+m2+m3) not less than 20%. In the embodiment, coal gangue particles, red mud and sodium metaaluminate are mixed according to the mass ratio of 1:3:0.3, so as to obtain a mixed material a.
Grinding the mixed material a to 530 m 2/kg by using a vertical mill, mixing the mixed material a and sodium hydroxide in a porcelain crucible according to the mass ratio of the mixed material a to the sodium hydroxide of 51:28, uniformly stirring, transferring the mixed material a and the sodium hydroxide into a muffle furnace, roasting for 110min at 720 ℃, taking out the mixed material b after roasting, and airing the mixed material b in a dryer to room temperature.
Adding deionized water into the roasted mixed material b to obtain slurry, wherein the adding amount is that the mass ratio of the roasted mixed material b to the deionized water is 1:9, transferring the slurry to a three-neck flask, adding a little zeolite, and carrying out hydrothermal reaction 140 min at 120 ℃ by using a chemical microwave reactor under the condition of heating reflux.
And fourthly, filtering the slurry after the hydrothermal reaction, obtaining liquid after filtering, namely the finished inorganic liquid phase component, and grinding filter residues again to 550 m 2/kg to obtain the finished inorganic solid phase component.
3. The triethanolamine, triisopropanolamine, maleic anhydride, ferric chloride hexahydrate, and sodium methacrylate used in this example were all industrially pure and the sodium metaaluminate was analytically pure.
The synergists in the first, second and third examples were used to prepare test pieces of gum sand and compared with the blank and comparative groups. Before the preparation of the mortar test block, the organic liquid phase component, the inorganic liquid phase component and water are mixed, the inorganic solid phase component and the solid waste base cementing material are mixed, and then the strength and the setting time are tested according to the relevant regulations of the current national standard of cement mortar strength test method (IOS) method (GB/T17671), cement standard consistency water consumption, setting time and stability test method (GB/T1346). The proportion table and the test result of the glue sand test block are shown in table 1 and table 2.
Table 1 glue sand test block proportioning table
TABLE 2 test results of gel test block strength and set time
As shown in tables 1 and 2, compared with the solid waste-based cementing material without the synergistic agent, the strength of the solid waste-based cementing material 3d after the synergistic agent is added is improved by 26.7-33.5%, the strength of the solid waste-based cementing material 28d is improved by 11.4-16.4%, the initial/final setting time is obviously shortened, and compared with ordinary Portland cement, the strength and the initial/final setting time are basically the same, which shows that the performance of the solid waste-based cementing material is obviously improved.
By way of explanation, analytical purity (AR, red labeled secondary) is slightly less than the top grade purity and the impurity content is slightly greater than the top grade purity, and is suitable for use in important analytical and general research works, such as general laboratory, research institute, and the like where reagents are commonly used, often denoted AR.
Chemical product purity is the purity of the raw material and relatively refers to the impurity content of the raw material. Industrial purity is relatively low grade purity, is suitable for use in relaxed laboratory work such as rinsing, desolventizing or as a raw material in production, and is very low purity.
Chemical product purity is the purity of the raw material and relatively refers to the impurity content of the raw material. The higher the purity, the fewer the impurity species and amount contained in the feedstock. Chemical raw materials can be classified into two main categories of industrial purity and reagent purity according to purity. The raw materials of the reagent can be classified into four grades according to the purity.
The quality grade purity (GR, green label, first grade product) is high in main component content and purity, is suitable for accurate analysis and scientific research determination work, and can be used as a reference substance;
Analytical purity (AR, red label, secondary product) with high content of main component, high purity and low interference impurity, and is suitable for general analysis and scientific research;
Chemical purity (CP, blue label, three-level product) with high content of main component and high purity, and interference impurities, and is suitable for general analysis and synthesis preparation in industrial and teaching processes;
The experimental purity (LR, yellow or brown label) is high in main component content, poor in purity, and only suitable for general chemical experiments and synthetic preparation.
The industrial purity (t.p. reagent, TECHNICALGRADE) is lower than that of the fourth grade, and is suitable for use in relaxed laboratory work such as rinsing, desolventizing or as a raw material in production, with very low purity.
In the foregoing embodiments, the descriptions of the embodiments are emphasized, and in part, not described or illustrated in any particular embodiment, reference is made to the related descriptions of other embodiments.
The foregoing description of the preferred embodiments of the invention is not intended to be limiting, but rather is intended to cover all modifications, equivalents, and alternatives falling within the spirit and principles of the invention.

Claims (9)

1.一种用于固废基胶凝材料的增效剂,其特征在于,按质量百分比计,包括:有机液相组分10~25份、无机液相组分15~25和无机固相组分50~70份;1. A synergist for solid waste-based gelling materials, characterized in that, by mass percentage, it comprises: 10 to 25 parts of an organic liquid phase component, 15 to 25 parts of an inorganic liquid phase component, and 50 to 70 parts of an inorganic solid phase component; 所述的有机液相组分的制备包括:The preparation of the organic liquid phase component comprises: 步骤一,将马来酸酐、三乙醇胺、六水合氯化铁按照质量比1:1.2~2.0:0.05~0.2的比例混合,反应得到液体a;Step 1, maleic anhydride, triethanolamine, and ferric chloride hexahydrate are mixed in a mass ratio of 1:1.2-2.0:0.05-0.2, and react to obtain liquid a; 步骤二,将步骤一中反应得到的液体a依次经过碳酸钠溶液、氯化钠溶液和氯化钙溶液洗涤,然后用元明粉进行干燥,过滤后得到中间体a;Step 2, washing the liquid a obtained in the reaction in step 1 with a sodium carbonate solution, a sodium chloride solution and a calcium chloride solution in sequence, then drying with sodium sulfate, and filtering to obtain an intermediate a; 步骤三,将中间体a与甲基丙烯酸钠、浓硫酸按照质量比259:68~103:3~5在三口烧瓶中混合,于70~95℃下加热反应,得到有机液相组分a,有机液相组分a的分子式为:Step 3, the intermediate a is mixed with sodium methacrylate and concentrated sulfuric acid in a three-necked flask at a mass ratio of 259:68-103:3-5, and heated to react at 70-95° C. to obtain an organic liquid phase component a. The molecular formula of the organic liquid phase component a is: 步骤四,将马来酸酐、三异丙醇胺、六水合氯化铁按照质量比1:1.5~2.5:0.05~0.2的比例混合,反应得到液体b;Step 4, mixing maleic anhydride, triisopropanolamine, and ferric chloride hexahydrate in a mass ratio of 1:1.5-2.5:0.05-0.2, and reacting to obtain liquid b; 步骤五,将步骤四中反应后的液体b按照步骤二进行处理,得到中间体b;Step 5, treating the liquid b after the reaction in step 4 according to step 2 to obtain an intermediate b; 步骤六,将中间体b与甲基丙烯酸钠、浓硫酸按照质量比289:68~103:0.15~0.25在三口烧瓶中混合,于70~95℃下加热反应,得到有机液相组分b,有机液相组分b的分子式为:Step 6: Mix the intermediate b with sodium methacrylate and concentrated sulfuric acid in a three-necked flask at a mass ratio of 289:68-103:0.15-0.25, and heat to react at 70-95° C. to obtain an organic liquid phase component b. The molecular formula of the organic liquid phase component b is: ; ; 步骤七,将有机液相组分a与有机液相组分b按照质量比1:0.25~1.75的比例混合,制得成品有机液相组分;Step 7, mixing the organic liquid phase component a and the organic liquid phase component b at a mass ratio of 1:0.25-1.75 to obtain a finished organic liquid phase component; 所述无机液相组分是由赤泥、煤矸石粉经过碱熔融、水热反应后过滤得到的滤液;所述无机固相组分由赤泥、煤矸石粉经过碱熔融、水热反应后,将过滤得到的滤渣经磨细后得到;所述碱熔融在550~750℃条件下焙烧;所述水热反应于105~125℃进行。The inorganic liquid phase component is a filtrate obtained by filtering red mud and coal gangue powder after alkali melting and hydrothermal reaction; the inorganic solid phase component is obtained by grinding the filter residue obtained by filtering red mud and coal gangue powder after alkali melting and hydrothermal reaction; the alkali melting is calcined at 550-750°C; and the hydrothermal reaction is carried out at 105-125°C. 2.一种用于固废基胶凝材料的增效剂的制备方法,制备如权利要求1所述的用于固废基胶凝材料的增效剂,其特征在于,包括所述有机液相组分的制备、所述无机液相组分的制备以及所述无机固相组分的制备;2. A method for preparing a synergist for solid waste-based gelling materials, comprising preparing the synergist for solid waste-based gelling materials as claimed in claim 1, characterized in that it comprises preparing the organic liquid phase component, preparing the inorganic liquid phase component and preparing the inorganic solid phase component; 所述有机液相组分,按照以下方法制备:The organic liquid phase component is prepared according to the following method: 步骤一,将马来酸酐、三乙醇胺、六水合氯化铁按照质量比1:1.2~2.0:0.05~0.2的比例混合,反应得到液体a;Step 1, maleic anhydride, triethanolamine, and ferric chloride hexahydrate are mixed in a mass ratio of 1:1.2-2.0:0.05-0.2, and react to obtain liquid a; 步骤二,准备三份去离子水,每份去离子水的质量均为马来酸酐用量的0.5~1.0倍,一份去离子水加入碳酸钠直至过量,一份去离子水加入氯化钠直至过量,一份去离子水加入氯化钙直至过量,保留过量的碳酸钠、氯化钠、氯化钙得到碳酸钠溶液、氯化钠溶液和氯化钙溶液;将步骤一中反应得到的液体a依次经过碳酸钠溶液、氯化钠溶液和氯化钙溶液洗涤,然后用元明粉进行干燥,过滤后得到中间体a;Step 2, prepare three portions of deionized water, the mass of each portion of deionized water is 0.5 to 1.0 times the amount of maleic anhydride used, add sodium carbonate to one portion of deionized water until it is excessive, add sodium chloride to one portion of deionized water until it is excessive, add calcium chloride to one portion of deionized water until it is excessive, retain the excess sodium carbonate, sodium chloride, and calcium chloride to obtain a sodium carbonate solution, a sodium chloride solution, and a calcium chloride solution; wash the liquid a obtained by the reaction in step 1 with a sodium carbonate solution, a sodium chloride solution, and a calcium chloride solution in sequence, then dry it with sodium sulfate, and filter it to obtain an intermediate a; 步骤三,将中间体a与甲基丙烯酸钠、浓硫酸按照质量比259:68~103:3~5在三口烧瓶中混合,于70~95℃下加热反应,期间利用分液漏斗缓慢滴加甲基丙烯酸钠初始用量1~3倍质量的甲基丙烯酸钠,滴加时间控制在90~150 min;滴加完毕后继续在此温度下反应60~120min,得到有机液相组分a;Step 3, the intermediate a is mixed with sodium methacrylate and concentrated sulfuric acid in a three-necked flask in a mass ratio of 259:68-103:3-5, and heated to react at 70-95° C., during which 1-3 times the mass of the initial amount of sodium methacrylate is slowly added dropwise using a separatory funnel, and the addition time is controlled at 90-150 min; after the addition is completed, the reaction is continued at this temperature for 60-120 min to obtain an organic liquid phase component a; 步骤四,将马来酸酐、三异丙醇胺、六水合氯化铁按照质量比1:1.5~2.5:0.05~0.2的比例混合,反应得到液体b;Step 4, mixing maleic anhydride, triisopropanolamine, and ferric chloride hexahydrate in a mass ratio of 1:1.5-2.5:0.05-0.2, and reacting to obtain liquid b; 步骤五,将步骤四中反应后的液体b按照步骤二进行处理,得到中间体b;Step 5, treating the liquid b after the reaction in step 4 according to step 2 to obtain an intermediate b; 步骤六,将中间体b与甲基丙烯酸钠、浓硫酸按照质量比289:68~103:0.15~0.25在三口烧瓶中混合,于70~95℃下加热反应,期间利用分液漏斗缓慢滴加甲基丙烯酸钠初始用量1~3倍质量的甲基丙烯酸钠,滴加时间控制在90~150 min;滴加完毕后继续在此温度下反应60~120 min,得到有机液相组分b;Step 6, the intermediate b is mixed with sodium methacrylate and concentrated sulfuric acid in a three-necked flask in a mass ratio of 289:68-103:0.15-0.25, and heated to react at 70-95° C., during which 1-3 times the mass of the initial amount of sodium methacrylate is slowly added dropwise using a separatory funnel, and the addition time is controlled at 90-150 min; after the addition is completed, the reaction is continued at this temperature for 60-120 min to obtain an organic liquid phase component b; 步骤七,将有机液相组分a与有机液相组分b按照质量比1:0.25~1.75的比例混合,制得成品有机液相组分。Step seven, mixing the organic liquid phase component a and the organic liquid phase component b in a mass ratio of 1:0.25-1.75 to obtain a finished organic liquid phase component. 3. 如权利要求2所述的用于固废基胶凝材料的增效剂的制备方法,其特征在于,步骤一中,马来酸酐、三乙醇胺、六水合氯化铁按照比例混合后于70~80℃条件下反应120~180min得到液体a。3. The method for preparing a synergist for solid waste-based gelling materials according to claim 2, characterized in that in step 1, maleic anhydride, triethanolamine, and ferric chloride hexahydrate are mixed in proportion and reacted at 70-80° C. for 120-180 min to obtain liquid a. 4. 如权利要求2所述的用于固废基胶凝材料的增效剂的制备方法,其特征在于,步骤二中,所述碳酸钠、氯化钠、氯化钙在去离子水中分别过量1~3 g。4. The method for preparing a synergist for solid waste-based gelling materials according to claim 2, characterized in that in step 2, the sodium carbonate, sodium chloride and calcium chloride are respectively added in excess of 1 to 3 g in deionized water. 5. 如权利要求2所述的用于固废基胶凝材料的增效剂的制备方法,其特征在于,步骤四中,马来酸酐、三异丙醇胺、六水合氯化铁按照质量比混合后于70~80℃条件下反应120~180 min。5. The method for preparing a synergist for solid waste-based cementitious materials according to claim 2, characterized in that in step 4, maleic anhydride, triisopropanolamine, and ferric chloride hexahydrate are mixed according to a mass ratio and reacted at 70-80° C. for 120-180 min. 6.如权利要求2所述的用于固废基胶凝材料的增效剂的制备方法,其特征在于,所述有机液相组分a的分子量为7000~8000,所述有机液相组分b的分子量为7500~9000。6. The method for preparing a synergist for solid waste-based gelling materials according to claim 2, characterized in that the molecular weight of the organic liquid phase component a is 7000-8000, and the molecular weight of the organic liquid phase component b is 7500-9000. 7.如权利要求2所述的用于固废基胶凝材料的增效剂的制备方法,其特征在于,所述的无机液相组分与所述无机固相组分,按照以下方法制备:7. The method for preparing a synergist for solid waste-based gelling materials according to claim 2, characterized in that the inorganic liquid phase component and the inorganic solid phase component are prepared according to the following method: 步骤一,利用X射线荧光光谱测试煤矸石与赤泥中Al2O3的质量分数,分别记为ω 1ω 2;将煤矸石破碎至0.30 mm以下得到煤矸石颗粒,然后按照以下方式计算煤矸石颗粒的投料质量m 1与赤泥的投料质量m 2Step 1: Use X-ray fluorescence spectroscopy to test the mass fraction of Al 2 O 3 in gangue and red mud, which are recorded as ω 1 and ω 2 respectively; crush the gangue to less than 0.30 mm to obtain gangue particles, and then calculate the feed mass m 1 of the gangue particles and the feed mass m 2 of the red mud in the following way: (1)当ω 1ω 2均不小于20%时,煤矸石颗粒与赤泥可按任意质量比投料;( 1) When ω1 and ω2 are not less than 20%, gangue particles and red mud can be added in any mass ratio ; (2)当ω 1ω 2仅有一个不小于20%时,按照(m 1 ω 1+m 2 ω 2)/(m 1+m 2)≥20%的比例计算煤矸石颗粒与赤泥的质量比范围;(2) When only one of ω1 and ω2 is not less than 20 % , the mass ratio range of gangue particles to red mud is calculated according to the ratio of ( m1ω1 + m2ω2 )/ ( m1 + m2 ) ≥20 % ; (3)当ω 1ω 2均小于20%时,除煤矸石颗粒与赤泥外,需要加入质量为m 3的偏铝酸钠,煤矸石颗粒、赤泥、偏铝酸钠的质量比范围按照(m 1 ω 1+m 2 ω 2+m 3)/(m 1+m 2+m 3)≥20%进行计算;(3) When ω1 and ω2 are both less than 20%, in addition to the gangue particles and red mud, sodium aluminate with a mass of m3 needs to be added, and the mass ratio of the gangue particles , red mud , and sodium aluminate is calculated according to ( m1ω1 + m2ω2 + m3 )/( m1 + m2 + m3 )≥20% ; 按照计算结果进行混料,得到混合物料a;Mix the materials according to the calculation results to obtain mixed material a; 步骤二,将混合物料a磨细至400~600 m2/kg,然后按照混合物料a与固体氢氧化钠质量比51:8~32的比例在瓷坩埚中混合,搅拌均匀后转移至马弗炉中,在550~750℃条件下焙烧60~120min,焙烧结束后,取出在干燥器中晾至室温,得到混合物料b;Step 2, grinding the mixed material a to 400-600 m 2 /kg, then mixing the mixed material a and solid sodium hydroxide in a porcelain crucible at a mass ratio of 51:8-32, stirring evenly and transferring to a muffle furnace, calcining at 550-750°C for 60-120min, and after calcination, taking out and drying in a dryer to room temperature to obtain a mixed material b; 步骤三,在焙烧后的混合物料b中加入去离子水得到浆液,加入量为焙烧后混合物料b:去离子水质量比为1:6~10,将浆液转移至三口烧瓶,在加热回流条件下,利用化学微波反应器于105~125℃进行水热反应90~150min;Step 3, adding deionized water to the calcined mixed material b to obtain a slurry, wherein the added amount is the calcined mixed material b: deionized water mass ratio of 1:6-10, transferring the slurry to a three-necked flask, and performing a hydrothermal reaction at 105-125° C. for 90-150 min in a chemical microwave reactor under heating reflux conditions; 步骤四,将水热反应后的浆液进行过滤,过滤后得到的液体即为成品无机液相组分;将滤渣再次磨细至400~600 m2/kg,得到成品无机固相组分。Step 4: Filter the slurry after the hydrothermal reaction, and the liquid obtained after filtration is the finished inorganic liquid phase component; grind the filter residue again to 400-600 m 2 /kg to obtain the finished inorganic solid phase component. 8.如权利要求7所述的用于固废基胶凝材料的增效剂的制备方法,其特征在于,步骤二中,搅拌均匀后转移至马弗炉中,在550~750℃条件下焙烧60~120min。8. The method for preparing a synergist for solid waste-based cementitious materials according to claim 7, characterized in that in step 2, after stirring evenly, the mixture is transferred to a muffle furnace and calcined at 550-750°C for 60-120 min. 9.如权利要求7所述的用于固废基胶凝材料的增效剂的制备方法,其特征在于,所述三乙醇胺、所述三异丙醇胺、所述马来酸酐、所述六水合氯化铁、所述甲基丙烯酸钠均为工业纯;所述偏铝酸钠为分析纯。9. The method for preparing a synergist for solid waste-based gelling materials according to claim 7, characterized in that the triethanolamine, the triisopropanolamine, the maleic anhydride, the ferric chloride hexahydrate, and the sodium methacrylate are all industrially pure; and the sodium aluminate is analytically pure.
CN202411259449.XA 2024-09-10 2024-09-10 Synergist for solid waste-based cementing material and preparation method thereof Active CN118791323B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202411259449.XA CN118791323B (en) 2024-09-10 2024-09-10 Synergist for solid waste-based cementing material and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202411259449.XA CN118791323B (en) 2024-09-10 2024-09-10 Synergist for solid waste-based cementing material and preparation method thereof

Publications (2)

Publication Number Publication Date
CN118791323A CN118791323A (en) 2024-10-18
CN118791323B true CN118791323B (en) 2024-12-06

Family

ID=93033783

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202411259449.XA Active CN118791323B (en) 2024-09-10 2024-09-10 Synergist for solid waste-based cementing material and preparation method thereof

Country Status (1)

Country Link
CN (1) CN118791323B (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110041015A (en) * 2019-03-27 2019-07-23 广东清大同科环保技术有限公司 Full-solid-waste ecological cementing material
CN118006934A (en) * 2024-04-10 2024-05-10 河北省建筑科学研究院有限公司 Pretreatment method and preparation method of solid waste-based cementing material based on vanadium-titanium slag production

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106866020A (en) * 2015-12-10 2017-06-20 青岛宏致复合织造有限公司 A kind of cement water reducing agent
JP7529426B2 (en) * 2020-03-31 2024-08-06 Ube三菱セメント株式会社 Cement composition, its manufacturing method, and durability improving admixture
EP4095110A1 (en) * 2021-05-26 2022-11-30 HeidelbergCement AG Method for producing supplementary cementitious material
CN114702285B (en) * 2021-12-30 2022-10-14 中国十七冶集团有限公司 Multi-source waste residue-based concrete 3D printing material and preparation method thereof

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110041015A (en) * 2019-03-27 2019-07-23 广东清大同科环保技术有限公司 Full-solid-waste ecological cementing material
CN118006934A (en) * 2024-04-10 2024-05-10 河北省建筑科学研究院有限公司 Pretreatment method and preparation method of solid waste-based cementing material based on vanadium-titanium slag production

Also Published As

Publication number Publication date
CN118791323A (en) 2024-10-18

Similar Documents

Publication Publication Date Title
CN107857496A (en) A kind of method of comprehensive utilization of coal gasification fine slag
CN103613955B (en) Method for preparing special nano calcium carbonate (nano-CaCO3) for vehicle adhesive
CN111233422A (en) A kind of concrete containing coal-to-oil crude residue and preparation method thereof
CN102745924A (en) Phosphogypsum-modifying method capable of shortening coagulating time of phosphogypsum-based cement concrete
CN105130220B (en) With discarded concrete and the method for sludge eco-cement and active sand
US11767432B2 (en) Method for mechanochemical preparation of high-performance iron red/clay mineral hybrid pigment
CN111533473A (en) Method for preparing ferrous aluminate cement clinker by using Bayer process red mud
CN108046650A (en) A kind of cement synergist
CN102745926A (en) Modified phosphogypsum and preparation method thereof
CN103058618B (en) Method of manufacturing silicate bricks with lead-and-zinc tailings
CN102530886B (en) Method for preparing sulfuric acid and cement by using phosphogypsum
CN116675509A (en) A kind of all-solid-waste steam-free concrete and its application
CN107640917A (en) A kind of preparation method of high intensity foam cement
CN105129745B (en) A kind of method that ardealite Sulphuric acid co-producing cement raw material integrate grinding
CN108264308A (en) It is a kind of heat-insulated non-burning brick and preparation method thereof
CN102674405B (en) Method for preparing potassium sulfate by using picromerite
CN105130317A (en) High strength debris aerated brick
CN118791323B (en) Synergist for solid waste-based cementing material and preparation method thereof
CN115321937A (en) Laterite-calcium carbonate-cement-based composite material and preparation method thereof
CN109180131A (en) A kind of preparation method of gypsum based self-leveling mortar
CN110498631A (en) A method for improving the later strength stability of sulphoaluminate cement
CN102936121A (en) Composite material used in mine roadway filling
CN103408050B (en) Method of efficient extraction of aluminum, iron, and titanium in coal gangue
CN210945394U (en) Device for producing II type anhydrous gypsum by phosphogypsum
CN102390947A (en) Ardealite mineral admixture and preparation method thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant