CN111559899A - Recycled material terrace brick and preparation method thereof - Google Patents

Recycled material terrace brick and preparation method thereof Download PDF

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Publication number
CN111559899A
CN111559899A CN202010356648.8A CN202010356648A CN111559899A CN 111559899 A CN111559899 A CN 111559899A CN 202010356648 A CN202010356648 A CN 202010356648A CN 111559899 A CN111559899 A CN 111559899A
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China
Prior art keywords
red mud
petroleum coke
slag
brick
desulfurization ash
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CN202010356648.8A
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Inventor
高嵩
侯东帅
侯双明
李楠
金祖权
李秋义
张蕾
黄庆强
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Qindao University Of Technology
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Qindao University Of Technology
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Priority to CN202010356648.8A priority Critical patent/CN111559899A/en
Publication of CN111559899A publication Critical patent/CN111559899A/en
Priority to PCT/CN2021/090860 priority patent/WO2021219058A1/en
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    • 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
    • C04B28/00Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
    • C04B28/24Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing alkyl, ammonium or metal silicates; containing silica sols
    • C04B28/26Silicates of the alkali metals
    • 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
    • C04B28/00Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
    • C04B28/02Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing hydraulic cements other than calcium sulfates
    • C04B28/10Lime cements or magnesium oxide cements
    • EFIXED CONSTRUCTIONS
    • E01CONSTRUCTION OF ROADS, RAILWAYS, OR BRIDGES
    • E01CCONSTRUCTION OF, OR SURFACES FOR, ROADS, SPORTS GROUNDS, OR THE LIKE; MACHINES OR AUXILIARY TOOLS FOR CONSTRUCTION OR REPAIR
    • E01C5/00Pavings made of prefabricated single units
    • E01C5/06Pavings made of prefabricated single units made of units with cement or like binders
    • EFIXED CONSTRUCTIONS
    • E04BUILDING
    • E04FFINISHING WORK ON BUILDINGS, e.g. STAIRS, FLOORS
    • E04F15/00Flooring
    • E04F15/02Flooring or floor layers composed of a number of similar elements
    • 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
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/60Flooring materials
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Structural Engineering (AREA)
  • Architecture (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Civil Engineering (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention provides a recycled material terrace brick and a preparation method thereof, wherein the raw materials comprise a cementing material and an aggregate, and the recycled material terrace brick is characterized in that: the cementing material accounts for 25-50% of the total mass of the raw materials, the aggregate accounts for 50-75% of the total mass of the raw materials, and the cementing material comprises the following components: red mud, petroleum coke desulfurization ash, carbide slag, slag powder, water glass and sodium sulfate; the aggregate is river sand. The preparation method comprises the following steps: weighing the raw materials according to the proportion for later use; drying and grinding the red mud, the petroleum coke desulfurization ash and the carbide slag, uniformly mixing the red mud, the petroleum coke desulfurization ash and the carbide slag with the slag powder, adding river sand to obtain a uniformly mixed mixture, putting the uniformly mixed mixture into a mortar stirring container, adding a proper amount of water, stirring, pouring and forming, placing the mixture indoors for 20-30 hours, removing a mold, and then curing for 25-30 days. The waste material resources are utilized, so that the environmental pollution can be reduced, and the manufacturing cost of the terrace brick is reduced; the preparation method is quick and simple, and is suitable for large-scale industrial production.

Description

Recycled material terrace brick and preparation method thereof
Technical Field
The invention belongs to the fields of civil engineering, solid waste resource recycling and building materials, and particularly relates to a recycled material terrace brick and a preparation method thereof.
Background
In recent years, the yield of the aluminum oxide in China exceeds 50% of the global yield, the capacity of the aluminum oxide in China reaches 7071 million tons by 3 months in 2017, and the huge capacity simultaneously promotes the development of the aluminum industry in China. Currently, the mode of producing alumina is mainly Bayer process, the yield of the alumina accounts for about 90 percent of the total yield of the alumina worldwide, and the main advantage of the method is that the energy consumption can be effectively reduced. However, in the process of producing alumina by the bayer process, raw materials such as caustic soda, lime and the like are usually added, and other alkali-insoluble substances are filtered out while alumina is dissolved out, and the solid waste slag generated in the production process is the red mud. Because of the influence of factors such as alumina production process, raw materials and the like, Bayer process red mud has extremely fine particles, high alkalinity and easy generation of dust pollution, and alkali or other heavy metal substances separated out in the stacking process can also permeate underground and cause soil alkalization or pollution of underground water sources.
According to statistics, the discharge amount of red mud in China per year exceeds 7000 million tons, and the accumulated stock amount exceeds 3.5 million tons. Due to the fact that supervision is not in place, enterprises are difficult to carry out harmless treatment when stacking red mud, and serious environmental pollution is caused to the periphery of a yard and nearby areas; along with the development of urbanization construction, land resources are deficient, environmental problems become the first problem to be solved in social development, and for the alumina industry, the sustainable development can be better realized by solving the problem of comprehensive recycling of red mud. At present, the comprehensive utilization of red mud in China is to extract useful components in the red mud, such as valuable metals and the like; and secondly, the organic silicon is integrally utilized as a raw material, such as an environment repairing material or a building material. The process for recovering valuable metal components is complex, the cost is high, the process for using the material for environmental remediation is simple, the cost is relatively low, and secondary pollution can be generated in application. The two application modes reduce the discharge amount of the red mud to a certain extent, but the consumption of the red mud is still limited, and secondary pollution cannot be avoided in the application process.
Meanwhile, the contents of sulfur, nitrogen and metal elements in crude oil imported from the middle east, heavy crude oil and poor crude oil mainly by large-scale oil refineries in coastal areas of our province are increased continuously, so that petroleum coke can only be used as fuel. The current common high-sulfur petroleum coke treatment technology is to burn by a circulating fluidized bed boiler, and to generate CaSO by adding CaO decomposed by limestone at high temperature and sulfur burnt by petroleum coke4Thus achieving the aim of desulfurizing the petroleum coke, and the mixture of the desulfurized gypsum and other combustion products forms the desulfurization ash of the petroleum coke. Taking an oil refinery in a certain place as an example, the annual discharge amount of petroleum coke desulfurized gypsum residue is more than 50 million tons, at present, the petroleum coke desulfurized gypsum residue can only be stacked in the open air, and a proper way for large-scale treatment is not available, so that serious environmental pollution is caused. The desulfurized ash residue of petroleum coke is the ash residue formed by the water content in the fuel and the water content formed after the hydrogen element in the fuel is burnt together in a gaseous state on the heating surface of a boiler. The mineral impurities become ash, and are essentially present in the form of metallic and non-metallic oxides, such as oxides of silicon, aluminum, iron, calcium, potassium, sodium, nickel, magnesium, and the like. The resource utilization technology of the petroleum coke slag is always a hotspot and a difficult point of domestic and overseas research, although the achievement is more, the actual popularization and application are less, and the resource utilization level is to be improved urgently.
The method is difficult to realize the large utilization of the Bayer process red mud no matter the valuable metals are recycled or the method is used for environmental remediation and the like, and becomes a great difficulty in the comprehensive utilization of the red mud resource.
The method is to prepare the activity excitant of the Bayer process red mud by using the solid waste desulfurized petroleum coke residue in the oil refining industry as the main raw material and to prepare the floor brick by doping wastes such as carbide slag and the like. The thought of treating wastes with wastes is exerted, the cost is reduced, and the activation treatment is carried out on the Bayer process red mud by utilizing large-dosage petroleum coke desulfurization ash and other auxiliary materials, thereby achieving the purpose of dual resource utilization of alumina waste residues and solid wastes in the oil refining industry. This is a technical problem which is urgently to be solved at present.
Disclosure of Invention
Aiming at the problems in the prior art, the invention provides a recycled material terrace brick and a preparation method thereof, which achieve the aim of dual resource utilization of aluminum oxide waste residues and oil refining industry solid wastes, can effectively reduce environmental pollution and reduce the manufacturing cost of the terrace brick, have easily available raw materials, are quick and simple in preparation method, and are suitable for large-scale industrial production.
In order to solve the above problems, the object of the present invention is achieved by the following technical solutions:
the recycled material terrace brick is characterized in that the raw materials of the recycled material terrace brick comprise a cementing material and an aggregate, the cementing material accounts for 25% -50% of the total mass of the raw materials, the aggregate accounts for 50% -75% of the total mass of the raw materials, and the cementing material comprises the following components in percentage by mass: 30-70% of red mud, 20-60% of petroleum coke desulfurization ash, 0-35% of carbide slag, 7.5-30% of slag powder, 1-2% of water glass and 1-2% of sodium sulfate; the aggregate is river sand.
The improvement of the technical scheme is as follows: the cementing material comprises the following components in percentage by mass: 45-70% of red mud, 20-55% of petroleum coke desulfurization ash, 0-30% of carbide slag, 7.5-25% of slag powder, 1-2% of water glass and 1-2% of sodium sulfate.
The technical scheme is further improved as follows: the dosage of the external water is 10-15% of the mass of the cementing material, and the external water is not counted in the mass percentage of the raw material of the regenerated material terrace brick.
The technical scheme is further improved as follows: the red mud is Bayer process red mud which is muddy residue discharged by leaching alumina in bauxite by using a Bayer process; the petroleum coke desulfurization ash is waste residue generated by burning heavy metal-containing petroleum coke in a boiler and mixing with lime powder; the carbide slag is a solid deposit generated after acetylene gas is hydrolyzed from carbide.
The invention also provides a preparation method of the recycled material terrace brick, which is characterized by comprising the following steps:
(1) weighing red mud, petroleum coke desulfurization ash, carbide slag, slag and river sand according to the raw material mixing ratio for later use;
(2) drying and grinding the red mud, the petroleum coke desulfurization ash, the carbide slag and the slag, mixing the materials in proportion, and adding river sand to obtain a uniformly mixed mixture;
(3) and putting the mixture into a mortar stirring container, adding a proper amount of water, stirring, pouring and forming after fully stirring, placing the mixture indoors for 20-30 hours, removing the mold, and then curing the mixture in a natural environment for 25-30 days to obtain the red mud baking-free tailing brick.
The improvement of the technical scheme is as follows: the cementing material accounts for 25-50% of the total mass of the raw materials, the aggregate accounts for 50-75% of the total mass of the raw materials, and the cementing material comprises the following components in percentage by mass: 30-70% of red mud, 20-60% of petroleum coke desulfurization ash, 0-35% of carbide slag, 7.5-30% of slag powder, 1-2% of water glass and 1-2% of sodium sulfate.
The technical scheme is further improved as follows: the cementing material comprises the following components in percentage by mass: 45-70% of red mud, 20-55% of petroleum coke desulfurization ash, 0-30% of carbide slag, 7.5-25% of slag powder, 1-2% of water glass and 1-2% of sodium sulfate.
The technical scheme is further improved as follows: the dosage of the external water is 10-15% of the mass of the cementing material, and the external water is not counted in the mass percentage of the raw material of the regenerated material terrace brick.
The technical scheme is further improved as follows: the red mud is Bayer process red mud which is muddy residue discharged by leaching alumina in bauxite by using a Bayer process; the petroleum coke desulfurization ash is waste residue generated by burning heavy metal-containing petroleum coke in a boiler and mixing with lime powder; the carbide slag is a solid deposit generated after acetylene gas is hydrolyzed from carbide.
Compared with the prior art, the invention has the following advantages and positive effects:
the Bayer process red mud activity excitant is prepared by using oil refining waste ash as a main raw material, and can be uniformly mixed with Bayer process red mud in a certain proportion to obtain better strength. The invention can achieve the purpose of dual resource utilization of the alumina waste residue and the oil refining industry solid waste, can reduce the pollution degree to the surrounding environment and the resource waste, and has great economic value, social value and environmental protection value. The preparation method can also reduce the manufacturing cost of the floor brick, has easily obtained raw materials, is quick and simple, and is suitable for large-scale industrial production.
Detailed Description
The present invention will be described in further detail with reference to specific examples.
The invention relates to a specific implementation mode of a recycled material terrace brick, wherein the recycled material terrace brick comprises raw materials of a cementing material and an aggregate, the cementing material accounts for 25-50% of the total mass of the raw materials, the aggregate accounts for 50-75% of the total mass of the raw materials, and the cementing material comprises the following components in percentage by mass: 30-70% of red mud, 20-60% of petroleum coke desulfurization ash, 0-35% of carbide slag, 7.5-30% of slag powder, 1-2% of water glass and 1-2% of sodium sulfate; the aggregate is river sand.
Preferably, the mass percentages of the components in the cementing material are as follows: 45-70% of red mud, 20-55% of petroleum coke desulfurization ash, 0-30% of carbide slag, 7.5-25% of slag powder, 1-2% of water glass and 1-2% of sodium sulfate.
Furthermore, the using amount of the external water is 10-15% of the mass of the cementing material, and the external water is not counted in the mass percentage of the raw material of the regenerated material terrace brick.
Specifically, the method comprises the following steps: the red mud is Bayer process red mud which is muddy residue discharged by leaching alumina in bauxite by using a Bayer process; the petroleum coke desulfurization ash is waste residue generated by burning heavy metal-containing petroleum coke in a boiler and mixing with lime powder; the carbide slag is a solid deposit generated after acetylene gas is hydrolyzed from carbide.
The invention also provides a specific implementation mode of the preparation method of the recycled material terrace brick, which comprises the following steps:
(1) weighing red mud, petroleum coke desulfurization ash, carbide slag, slag and river sand according to the raw material mixing ratio for later use;
(2) drying and grinding the red mud, the petroleum coke desulfurization ash, the carbide slag and the slag, mixing the materials in proportion, and adding river sand to obtain a uniformly mixed mixture;
(3) and putting the mixture into a mortar stirring container, adding a proper amount of water, stirring, pouring and forming after fully stirring, placing the mixture indoors for 20-30 hours, removing the mold, and then curing the mixture in a natural environment for 25-30 days to obtain the red mud baking-free tailing brick.
The following are specific examples of the recycled material terrace brick of the invention:
the tailing brick material is selected from Bayer process red mud, petroleum coke slag, carbide slag, slag and river sand. Two forming modes, namely static pouring forming and pressing forming, are adopted in the test. The test detection method refers to (GB/T4111-2013) concrete block and brick test method to detect the mechanical property, the drying shrinkage, the softening coefficient and the frost resistance. Each performance meets each index requirement specified in non-sintered refuse tailing bricks (JC/T422-2007).
Example 1:
the red mud brick is prepared with Bayer process red mud 12.25 wt%, petroleum coke slag 3.5 wt%, calcium carbide slag 1.75 wt%, slag 7.5 wt%, river sand 75 wt%, added polycarboxylic acid water reducing agent 0.2 wt% and water 12.5 wt% and through mixing, grinding, mixing in certain proportion, adding river sand, stirring in mortar stirring pot with water, casting to form, demolding after 1 day, and curing in natural environment to 28 days to obtain the red mud brick as the burning-free tailing brick3The pavement brick has the flexural strength of 6.6MPa and the compressive strength of 21.8MPa after 28 days, the average water absorption of 8.4 percent, the drying shrinkage of 0.512mm/m and the softening coefficient of 1.07, and the quality after 25 times of slow freezing and thawing cyclesThe loss rate of the amount was 0, and the loss rate of the strength was 9.05%.
Example 2:
the red mud brick is prepared with Bayer process red mud 24.5 wt%, petroleum coke slag 7 wt%, calcium carbide slag 3.5 wt%, slag 15 wt%, river sand 50 wt%, water 0.5 wt%, and casting 40 × 100 × 200mm in weight proportion3The 28d flexural strength of the pavement brick is 10.3MPa, the compressive strength is 43.0MPa, the average water absorption is 2.6%, the drying shrinkage is 0.465mm/m, the softening coefficient is 1.0, the mass loss rate after 25 times of slow freezing and thawing cycles is 0, and the strength loss rate is 1.88%.
Example 3:
the red mud brick is prepared with Bayer process red mud 24.5 wt%, petroleum coke slag 10.5 wt%, slag 15 wt%, river sand 50 wt%, added polycarboxylic acid water reducing agent 0.5 wt% and water 15 wt%, and through mixing, adding river sand and water in certain proportion, and curing in natural environment to 28 days3The 28d flexural strength of the pavement brick is 8.9MPa, the compressive strength is 36.9MPa, the average water absorption is 2.5 percent, the drying shrinkage is 0.467mm/m, the softening coefficient is 1.03, the mass loss rate after 25 times of slow freezing and thawing cycles is 0, and the strength loss rate is 1.12 percent.
Example 4:
drying and grinding the Bayer process red mud, the petroleum coke residue, the carbide slag and the slag, then mixing the materials in proportion, and adding part of river sand. Placing the mixture into a mortar stirring pot, adding appropriate amount of water, stirring, fully stirring, press-forming with a pressure tester 80KN, placing indoors for 1d, removing the mold, and curing in natural environment to 28d to obtain the final productThe red mud baking-free tailing brick is prepared with Bayer process red mud 12.25 wt%, petroleum coke desulfurizing cinder 3.5 wt%, calcium carbide slag 1.75 wt%, slag 7.5 wt%, river sand 75 wt% and 12.5 wt% water, and through pressing into 55 × 100-100 × 200mm size3The 28d flexural strength of the pavement brick is 8.4MPa, the compressive strength is 29.6MPa, the average water absorption is 11%, the drying shrinkage is 0.10mm/m, the softening coefficient is 0.95, the mass loss rate after 25 times of slow freezing and thawing cycles is 0.6%, and the strength loss rate is 7.92%.
According to the invention, the experiment is carried out according to the formula, the exciting agent is doped into the red mud, the die is removed after the maintenance is carried out for 24 hours, and the test block is cemented and molded, can be completely demoulded, has certain strength up to 25MPa, and can be directly used for hardening floors and floor tiles. In the test block, the activity of the red mud powder is further improved by the petroleum coke desulfurization ash, and active ingredients in auxiliary materials such as high belite cement, water glass and the like are subjected to composite reaction with the red mud to generate a substance with a gelling property, so that the compactness and the strength of the material are improved.
The above embodiments are only used for illustrating the technical solution of the present invention, and not for limiting the same; although the invention has been described in detail with reference to the foregoing embodiments, it will be apparent to those skilled in the art that various changes may be made and equivalents may be substituted for elements thereof; such modifications and substitutions do not depart from the spirit and scope of the present invention as set forth in the appended claims.

Claims (6)

1. The recycled material terrace brick is characterized in that the raw materials of the recycled material terrace brick comprise a cementing material and an aggregate, the cementing material accounts for 25% -50% of the total mass of the raw materials, the aggregate accounts for 50% -75% of the total mass of the raw materials, and the cementing material comprises the following components in percentage by mass: 30-70% of red mud, 20-60% of petroleum coke desulfurization ash, 0-35% of carbide slag, 7.5-30% of slag powder, 1-2% of water glass and 1-2% of sodium sulfate; the aggregate is river sand.
2. The recycled material floor tile of claim 1, wherein the cementitious material comprises the following components in percentage by mass: 45-70% of red mud, 20-55% of petroleum coke desulfurization ash, 0-30% of carbide slag, 7.5-25% of slag powder, 1-2% of water glass and 1-2% of sodium sulfate.
3. The recycled material terrace brick according to claim 1 or 2, wherein the amount of externally doped water is 10-15% of the mass of the cementing material, and the externally doped water is not counted in the mass percentage of the recycled material terrace brick raw material.
4. The recycled material floor tile according to claim 1 or 2, wherein the red mud is bayer process red mud, which is a sludge-like residue discharged from alumina leaching in bauxite by using a bayer process; the petroleum coke desulfurization ash is waste residue generated by burning heavy metal-containing petroleum coke in a boiler and mixing with lime powder; the carbide slag is a solid deposit generated after acetylene gas is hydrolyzed from carbide.
5. The recycled material floor tile of claim 3, wherein the red mud is Bayer process red mud, wherein the Bayer process red mud is a sludge-like residue discharged from the leaching of alumina from bauxite by using a Bayer process; the petroleum coke desulfurization ash is waste residue generated by burning heavy metal-containing petroleum coke in a boiler and mixing with lime powder; the carbide slag is a solid deposit generated after acetylene gas is hydrolyzed from carbide.
6. The preparation method of the recycled material floor tile according to any one of claims 1 to 5, characterized in that the preparation method comprises the following steps:
(1) weighing red mud, petroleum coke desulfurization ash, carbide slag, slag and river sand according to the raw material mixing ratio for later use;
(2) drying and grinding the red mud, the petroleum coke desulfurization ash, the carbide slag and the slag, mixing the materials in proportion, and adding river sand to obtain a uniformly mixed mixture;
(3) and putting the mixture into a mortar stirring container, adding a proper amount of water, stirring, pouring and forming after fully stirring, placing the mixture indoors for 20-30 hours, removing the mold, and then curing the mixture in a natural environment for 25-30 days to obtain the red mud baking-free tailing brick.
CN202010356648.8A 2020-04-29 2020-04-29 Recycled material terrace brick and preparation method thereof Pending CN111559899A (en)

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Application publication date: 20200821