CN116947338A - Composite biomass binder modified alkali-activated cementing material and preparation method thereof - Google Patents

Composite biomass binder modified alkali-activated cementing material and preparation method thereof Download PDF

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Publication number
CN116947338A
CN116947338A CN202310840966.5A CN202310840966A CN116947338A CN 116947338 A CN116947338 A CN 116947338A CN 202310840966 A CN202310840966 A CN 202310840966A CN 116947338 A CN116947338 A CN 116947338A
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starch
solid waste
alkali
cementing material
industrial solid
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姜娟
牛强
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Inner Mongolia Erdos Electric Power Metallurgy Group Co Ltd
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Inner Mongolia Erdos Electric Power Metallurgy Group Co Ltd
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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
    • C04B7/00Hydraulic cements
    • C04B7/24Cements from oil shales, residues or waste other than slag
    • C04B7/243Mixtures thereof with activators or composition-correcting additives, e.g. mixtures of fly ash and alkali activators
    • 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
    • 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
    • C04B7/00Hydraulic cements
    • C04B7/14Cements containing slag
    • 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
    • C04B7/00Hydraulic cements
    • C04B7/14Cements containing slag
    • C04B7/147Metallurgical slag
    • C04B7/153Mixtures thereof with other inorganic cementitious materials or other activators
    • C04B7/1535Mixtures thereof with other inorganic cementitious materials or other activators with alkali metal containing activators, e.g. sodium hydroxide or waterglass
    • 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
    • C04B7/00Hydraulic cements
    • C04B7/24Cements from oil shales, residues or waste other than slag
    • 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
    • C04B2111/00017Aspects relating to the protection of the environment
    • 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
    • C04B2201/00Mortars, concrete or artificial stone characterised by specific physical values
    • C04B2201/50Mortars, concrete or artificial stone characterised by specific physical values for the mechanical strength
    • 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

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

Abstract

The invention belongs to the technical field of industrial solid waste resource utilization and building materials, and provides a composite biomass binder modified alkali-activated cementing material and a preparation method thereof. The alkali-activated gelling material comprises the following components: alkali excitant, composite biomass binder and industrial solid waste; the composite biomass binder comprises the following components: plant biomass and starch; the alkali-activated cementing material is prepared by activating and exciting plant biomass in an alkali-activated agent solution at room temperature, and then sequentially adding starch and industrial solid wastes. The invention has the advantages of wide raw material sources, reproducibility, low price and environmental friendliness, wherein the starch provides early strength for the cementing material, and the plant biomass is better dispersed in the cementing material after being subjected to alkaline excitation modification, so that the cementing material with uniformly distributed fiber network is obtained, and meanwhile, the early and long-term strength improvement of the cementing material is realized, so that the invention has wide application.

Description

Composite biomass binder modified alkali-activated cementing material and preparation method thereof
Technical Field
The invention belongs to the technical field of industrial solid waste resource utilization and building materials, and provides a composite biomass binder modified alkali-activated cementing material and a preparation method thereof.
Background
The alkali-activated cementing material uses solid waste as a raw material, has a simple preparation process, does not need high-temperature calcination, can be used as a new material for replacing Portland cement, can simultaneously reduce carbon emission, reduce energy consumption and realize the recycling of industrial solid waste, but has mechanical strength, long-term stability and other performances which are inferior to those of the conventional Portland cement; in addition, the containing interval of the alkali-activated cementing material for the water-cement ratio is smaller, and when the water-cement ratio is larger, the structure collapse can be caused; the above problems further limit the development of alkali-activated materials and slow down their progress in replacing portland cement.
Chinese patent No. CN101570425B discloses an inorganic geopolymer composite cementing material reinforced by organic fibers, wherein the composite cementing material is prepared by adding organic fibers into an alkali-activated cementing material, the highest flexural strength of the composite cementing material in 28 days is improved by 1.6MPa compared with that of a phosphorus slag geopolymer, and the highest compressive strength in 28 days is increased by 28.4MPa compared with that of the phosphorus slag geopolymer; the reinforcing and toughening effects of the cementing material are realized; however, the added fibers are not easy to uniformly disperse in the slurry, and the addition of the fibers can reduce the fluidity of the slurry, so that the construction difficulty is increased.
At present, the research is carried out on adding a water-soluble polymer material into an inorganic alkali-activated cementing material to obtain an organic/inorganic hybrid composite material, and the mechanical properties of the alkali-activated cementing material can be improved. Chinese patent No. CN109970377B discloses a method for preparing water-soluble organic polymer toughened slag-based geopolymer cementing material, which uses water-soluble polymer organic matter polyvinyl alcohol powder. Chinese patent No. CN111943532B discloses a method for preparing geopolymer-based organic-inorganic composite gel material, in which aqueous epoxy resin emulsion is added during the preparation process. Chinese patent No. CN101560068B discloses a method for preparing composite gel material of composite organic high molecular reinforced kaolin and slag-based geopolymer, which uses binary compound polyvinyl acetate emulsion powder and polyacrylate resin emulsion.
The technical proposal for preparing the alkali-activated cementing material introduces water-soluble polymer materials, and the strength of the alkali-activated cementing material is improved although the types of the organic polymers are different. However, the high molecular polymer used in the prior art is expensive, so that the carbon emission of the full life cycle of the alkali-activated cementing material is increased, and the price advantage of the alkali-activated cementing material over conventional cement is reduced.
The Chinese patent application CN116003002A discloses a multi-solid waste-based inorganic cementing material, which comprises the following components in parts by mass: 40-50 parts of fly ash, 2535 parts of gangue powder, 0.52 part of cementing agent and 12 parts of alkali-exciting agent; the preparation method of the cementing agent comprises the following steps: taking honey, aluminum sulfate, diethanolamine and phosphoric acid as raw materials, and mixing and adding water to generate a cementing agent; the cementing agent and the alkali-exciting agent are utilized to synergistically increase the flowability and strength of the cementing material.
In order to further reduce the preparation cost of the alkali-activated cementing material, improve the performances of compressive strength, flexural strength and the like, the preparation of the cementing material by adopting different cementing agent modified alkali-activated agents is still to be further researched.
Disclosure of Invention
In order to solve the technical problems in the prior art, the invention provides a preparation method of a cementing material using a composite biomass binder to replace organic artificial fibers and a high polymer binder. The used composite biomass binder comprises plant biomass and starch, wherein the plant biomass contains cellulose, hemicellulose and lignin, and the cellulose and the hemicellulose of the biomass are partially decomposed by alkali liquor modified biomass, so that fibers are dissociated from each other and can be well dispersed in the slurry to play a role in reinforcing and toughening. Starch has good viscosity and is a natural adhesive. The composite biomass binder provided by the invention overcomes the problems of high cost, high carbon emission and the like of using synthetic fibers and high molecular polymers, improves the strength of the cementing material, and has a good application prospect.
The invention aims to provide a composite biomass binder modified alkali-activated cementing material; the alkali-activated gelling material comprises the following components: alkali excitant, composite biomass binder and industrial solid waste; the composite biomass binder comprises the following components: plant biomass and starch.
Preferably, the mass ratio of the alkali-activated agent to the industrial solid waste is 0.1-0.25:1.
Preferably, the mass ratio of the plant biomass to the solid waste is 0.005-0.05:1.
Preferably, the mass ratio of the starch to the industrial solid waste is 0.005-0.05:1.
Preferably, the alkali-activator is at least one of sodium hydroxide, sodium silicate, sodium sulfate, sodium phosphate, sodium citrate, sodium bicarbonate, potassium hydroxide, potassium silicate, potassium sulfate, potassium phosphate, potassium citrate, and potassium bicarbonate.
Preferably, the industrial solid waste is mixed industrial solid waste composed of at least three of carbide slag, tailings, metallurgical slag, coal gangue, fly ash, desulfurized gypsum, red mud, phosphogypsum and stone processing bottom mud.
More preferably, the three components of the mixed industrial solid waste comprise at least one of carbide slag, metallurgical slag and red mud.
Preferably, the industrial solid waste particle size is less than or equal to 200 mu m.
More preferably, the industrial solid waste particle size is less than or equal to 100 mu m.
The plant biomass is at least one of bagasse, corn cob, sawdust, rice chaff, coconut husk, straw, wheat straw and corn straw;
preferably, the plant biomass is at least one of coconut shells, rice straws and wheat straws.
More preferably, the plant biomass particle size is less than or equal to 200 μm.
The starch is at least one of wheat starch, corn starch, water chestnut starch, mung bean starch, pea starch, sweet potato starch, tapioca starch, potato starch and lotus root starch.
Preferably, the starch is at least one of wheat starch, corn starch, mung bean starch, tapioca starch and pea starch.
Preferably, the starch has a particle size of 50-300. Mu.m.
More preferably, the starch particle size is 75-150 μm.
Preferably, the cement composition further comprises water.
More preferably, the mass ratio of the water to the industrial solid waste is 0.35-0.6:1.
The second object of the present invention is to provide a method for preparing the above-mentioned cementing material, comprising the following steps:
(1) Dissolving an alkali-activated agent in water, adding plant biomass for alkali activation and excitation to obtain slurry 1;
(2) To the slurry 1 is added starch, stirring and dispersing to obtain slurry 2;
(3) And adding industrial solid waste into the slurry 2, and stirring and dispersing to obtain the cementing material.
Further, in the step (1), the alkali activation excitation temperature is room temperature and the time is 2-24 hours; preferably 12-16h.
Further, in the step (2), stirring and dispersing temperature is room temperature, and the time is 5-30min; preferably 15-30min.
Further, in the step (3), stirring and dispersing temperature is room temperature, and the time is 3-10min; preferably 5-10min.
Further, before the strength of the cementing material is tested, steam curing and room temperature curing are sequentially carried out.
Further, the temperature of the steam curing is 80+/-2 ℃ and the humidity is not less than 95%; the steam curing time is 12-36h; the steam curing time is preferably 24-36 hours.
Further, the room temperature curing temperature is 20+/-2 ℃ and the humidity is not less than 95%; the curing time at room temperature is 1-28d; the curing time at room temperature is preferably 14-28d.
Compared with the prior art, the invention has the beneficial effects that:
(1) The plant biomass used in the invention can be better dispersed in the cementing material after being subjected to alkaline excitation modification, so that the problem of poor dispersibility of common fibers is solved, and the cementing material with uniformly distributed fiber network is obtained; the starch has good cementing effect and can provide early strength for the cementing material;
(2) Plant biomass and starch can improve the short-term strength of the cementing material, but the improvement of the long-term strength of the cementing material mainly depends on the excitation reaction of an alkali excitant and industrial solid wastes; the excessive content of plant biomass and starch occupies most positions of the interfaces of industrial solid waste particles, so that the contact between an alkali excitant and industrial solid waste is influenced, the dissolution reaction is further influenced, and the long-term strength of the cementing material is not facilitated; the early strength and the long-term strength of the cementing material are improved simultaneously by further optimizing the dosage of the plant biomass and the starch;
(3) The invention finally forms the solid waste-based cementing material which is modified by starch bonding, plant biomass toughening and reinforcing and alkali excitation, and the compressive strength of the solid waste-based cementing material is obviously improved by the synergistic effect of the components; meanwhile, the phenomena of low strength of the cementing material, saltpetering and the like are improved by reasonably controlling the dosage proportion of each component.
(4) The invention uses the alkali excitant to excite industrial solid waste into the cementing material, and no additional cementing material is needed, thereby realizing the reutilization of resources and reducing the cost of raw materials; the compressive strength of the product is further improved through the selection of industrial solid wastes; meanwhile, the composite biomass binder is used as plant biomass and starch, so that the method has the advantages of wide sources, reproducibility, low price, environmental friendliness and the like, and solves the problems of high cost, high carbon emission and the like of reinforcing materials and binders in the prior art.
Detailed Description
The following non-limiting examples will enable those of ordinary skill in the art to more fully understand the invention and are not intended to limit the invention in any way. The following is merely illustrative of the scope of the invention as it is claimed and many variations and modifications of the invention will be apparent to those skilled in the art in light of the disclosure, which should be construed to fall within the scope of the invention as it is further described in the following detailed description of the invention.
Example 1
The cementing material comprises the following components in percentage by mass: the mass ratio of water to solid waste is 0.4:1, the mass ratio of alkaline excitant to solid waste is 0.15:1, the mass ratio of plant biomass to solid waste is 0.03:1, and the mass ratio of starch to solid waste is 0.02:1;
the preparation process of the cementing material comprises the following steps:
(1) Completely dissolving sodium hydroxide as an alkali-exciting agent in water, adding plant biomass (rice straw, wheat straw and coconut shell according to the mass ratio of 1:1:1; the particle size is less than or equal to 200 mu m), and carrying out alkali-activating excitation for 12 hours at room temperature to obtain slurry 1;
(2) Adding starch (corn starch; particle size of 75 μm) into the slurry 1, stirring and dispersing at room temperature for 15min to obtain slurry 2;
(3) Adding industrial solid wastes (carbide slag, metallurgical slag and red mud with the mass ratio of 1:1:1; the particle size is less than or equal to 100 mu m) into the slurry 2, stirring for 5min at room temperature, and fully and uniformly mixing; obtaining slurry 3;
(4) And finally pouring the slurry 3 into a die, vibrating compaction, steam curing for 24 hours, and curing at room temperature for 28 days to obtain the cementing material product.
Example 2
The cementing material comprises the following components in percentage by mass: the mass ratio of water to solid waste is 0.4:1, the mass ratio of alkaline excitant to solid waste is 0.15:1, the mass ratio of plant biomass to solid waste is 0.05:1, and the mass ratio of starch to solid waste is 0.02:1;
the preparation process of the cementing material comprises the following steps:
(1) Completely dissolving an alkaline excitant potassium hydroxide in water, then adding plant biomass (corn stalk, bagasse, rice chaff and coconut husk with the mass ratio of 1:1:1; the particle size is less than or equal to 200 mu m), and performing alkaline activation excitation for 16 hours at room temperature to obtain slurry 1;
(2) Adding starch (wheat starch and corn starch according to a mass ratio of 1:1; the grain size is 75 mu m) into the slurry 1, and fully stirring and dispersing for 15min at room temperature to obtain slurry 2;
(3) Adding industrial solid waste (carbide slag, coal gangue and fly ash with the mass ratio of 1:1:1, and the particle size of less than or equal to 100 mu m) into the slurry 2, stirring for 5 minutes at room temperature, and fully and uniformly mixing to obtain slurry 3;
(4) And finally pouring the slurry 3 into a die, vibrating compaction, steam curing for 24 hours, and curing at room temperature for 28 days to obtain the cementing material product.
Example 3
The cementing material comprises the following components in percentage by mass: the mass ratio of water to solid waste is 0.4:1, the mass ratio of alkaline excitant to solid waste is 0.15:1, the mass ratio of plant biomass to solid waste is 0.03:1, and the mass ratio of starch to solid waste is 0.05:1;
the preparation process of the cementing material comprises the following steps:
(1) Completely dissolving sodium sulfate as an alkaline activator in water, adding plant biomass (rice straw, wheat straw and coconut shell according to the mass ratio of 1:1:1; the particle size is less than or equal to 200 mu m), and performing alkaline activation and excitation for 12 hours at room temperature to obtain slurry 1.
(2) Adding starch (mung bean starch, tapioca starch and pea starch with the mass ratio of 1:1:1 and the particle size of 200 mu m) into the slurry 1, and fully stirring and dispersing for 15min at room temperature to obtain slurry 2;
(3) Adding industrial solid waste (metallurgical slag, coal gangue and fly ash with the mass ratio of 1:1:1, and particle size of less than or equal to 100 μm) into the slurry 2, stirring for 5min at room temperature, and fully and uniformly mixing to obtain slurry 3;
(4) And finally pouring the slurry 3 into a die, vibrating compaction, steam curing for 24 hours, and curing at room temperature for 28 days to obtain the cementing material product.
Example 4
The cementing material comprises the following components in percentage by mass: the mass ratio of water to solid waste is 0.4:1, the mass ratio of alkaline excitant to solid waste is 0.15:1, the mass ratio of plant biomass to solid waste is 0.03:1, and the mass ratio of starch to solid waste is 0.02:1;
the preparation process of the cementing material comprises the following steps:
(1) Completely dissolving alkaline excitant potassium sulfate in water, then adding plant biomass (straw, wheat straw and coconut shell according to the mass ratio of 1:1:1; the particle size is less than or equal to 200 mu m), and performing alkaline activation excitation for 12 hours at room temperature to obtain slurry 1;
(2) Adding starch (corn starch; particle size of 75 μm) into the slurry 1, stirring and dispersing at room temperature for 15min to obtain slurry 2;
(3) Adding industrial solid waste (red mud, coal gangue and fly ash with the mass ratio of 1:1:1; the particle size is less than or equal to 100 mu m) into the slurry 2, stirring for 5min at room temperature, and fully and uniformly mixing to obtain slurry 3;
(4) And finally pouring the slurry 3 into a die, vibrating compaction, steam curing for 24 hours, and curing at room temperature for 28 days to obtain the cementing material product.
Example 5
The cementing material comprises the following components in percentage by mass: the mass ratio of water to solid waste is 0.4:1, the mass ratio of alkaline excitant to solid waste is 0.2:1, the mass ratio of plant biomass to solid waste is 0.03:1, and the mass ratio of starch to solid waste is 0.02:1;
the preparation process of the cementing material comprises the following steps:
(1) Completely dissolving alkaline excitant sodium hydroxide in water, then adding plant biomass (wheat straw; particle size is less than or equal to 200 mu m), and performing alkaline activation excitation for 12 hours at room temperature to obtain slurry 1;
(2) Adding starch (corn starch and mung bean starch according to a mass ratio of 1:1; the grain size is 75 μm) into the slurry 1, and fully stirring and dispersing for 15min at room temperature to obtain slurry 2;
(3) Adding industrial solid wastes (carbide slag, tailings and metallurgical slag with the mass ratio of 1:1:1; the particle size is less than or equal to 100 mu m) into the slurry 2, stirring for 5min at room temperature, and fully and uniformly mixing to obtain slurry 3;
(4) And finally pouring the slurry 3 into a die, vibrating compaction, steam curing for 24 hours, and curing at room temperature for 28 days to obtain the cementing material product.
Example 6
The cementing material comprises the following components in percentage by mass: the mass ratio of water to solid waste is 0.55:1, the mass ratio of alkaline excitant to solid waste is 0.15:1, the mass ratio of plant biomass to solid waste is 0.03:1, and the mass ratio of starch to solid waste is 0.02:1;
the preparation process of the cementing material comprises the following steps:
(1) Completely dissolving alkaline excitant sodium hydroxide in water, then adding plant biomass (coconut shell; particle size is less than or equal to 200 mu m), and performing alkaline activation excitation for 12 hours at room temperature to obtain slurry 1;
(2) Adding starch (corn starch; particle size of 75 μm) into the slurry 1, stirring and dispersing at room temperature for 15min to obtain slurry 2;
(3) Adding industrial solid wastes (carbide slag, fly ash and desulfurized gypsum according to the mass ratio of 1:1:1; the particle size is less than or equal to 100 mu m) into the slurry 2, stirring for 5min at room temperature, and fully and uniformly mixing to obtain slurry 3;
(4) And finally pouring the slurry 3 into a die, vibrating compaction, steam curing for 24 hours, and curing at room temperature for 28 days to obtain the cementing material product.
Example 7
The cementing material comprises the following components in percentage by mass: the mass ratio of water to solid waste is 0.55:1, the mass ratio of alkaline excitant to solid waste is 0.15:1, the mass ratio of plant biomass to solid waste is 0.03:1, and the mass ratio of starch to solid waste is 0.02:1;
the preparation process of the hair gel material comprises the following steps:
(1) Completely dissolving alkaline excitant sodium hydroxide in water, adding plant biomass (straw; particle size less than or equal to 200 mu m), and performing alkaline activation excitation for 12 hours at room temperature to obtain slurry 1;
(2) Adding starch (corn starch; particle size of 75 μm) into the slurry 1, stirring and dispersing at room temperature for 15min to obtain slurry 2;
(3) Adding industrial solid waste (carbide slag, metallurgical slag, coal gangue and fly ash with the mass ratio of 1:1:1:1; the particle size is less than or equal to 100 mu m) into the slurry 2, stirring for 3-10min at room temperature, and fully and uniformly mixing to obtain slurry 3;
(4) And finally pouring the slurry 3 into a die, vibrating compaction, steam curing for 12 hours, and curing at room temperature for 28 days to obtain the cementing material product.
Comparative example 1
Compared with example 1, the only difference is that: the particle size of the plant biomass and the industrial solid waste is 300-400 mu m, and the rest conditions are the same.
Comparative example 2
Compared with example 1, the only difference is that: the mass ratio of the plant biomass to the industrial solid waste is 0.001:1, and the rest conditions are the same.
Comparative example 3
Compared with example 1, the only difference is that: the mass ratio of the plant biomass to the industrial solid waste is 0.08:1, and the rest conditions are the same.
Comparative example 4
Compared with example 1, the only difference is that: the mass ratio of the alkaline excitant to the industrial solid waste is 0.03:1, and the rest conditions are the same.
Comparative example 5
Compared with example 1, the only difference is that: the mass ratio of water to industrial solid waste is 0.7:1, and the rest conditions are the same.
Comparative example 6
Compared with example 1, the only difference is that: no composite binder of plant biomass and starch is added, and the other conditions are the same.
Comparative example 7
Compared with example 1, the only difference is that: plant biomass is not added, and the mass ratio of starch to industrial solid waste is 0.05:1; the remaining conditions were the same.
Comparative example 8
Compared with example 1, the only difference is that: starch is not added, and the mass ratio of the plant biomass to the industrial solid waste is 0.05:1; the remaining conditions were the same.
Comparative example 9
Compared with example 1, the only difference is that: the mass ratio of the starch to the industrial solid waste is 0.08:1, and the rest conditions are the same.
Comparative example 10
Compared with example 1, the only difference is that: the industrial solid waste is carbide slag and metallurgical slag with the ratio of 1:1, and the rest conditions are the same.
Comparative example 11
Compared with example 1, the only difference is that: the industrial solid waste is carbide slag and red mud in a ratio of 1:1, and the rest conditions are the same.
Comparative example 12
Compared with example 1, the only difference is that: the metallurgical slag and the red mud with the industrial solid waste of 1:1 have the same rest conditions.
Comparative example 13
Compared with example 1, the only difference is that: in the preparation process of the alkali-activated cementing material, the alkali-activated activation temperature of the plant biomass is 80 ℃, and the rest conditions are the same.
The properties of the cement prepared in the above examples and comparative examples were examined, and the results are shown in Table 1.
TABLE 1 detection of the Properties of the cementing Material
As can be seen from table 1:
comparative example 1 has a low gel strength because it is difficult to obtain a dense microstructure because both the particle size of plant biomass and industrial solid wastes are too large compared with example 1;
compared with the embodiment 1, the embodiment 2 has the advantages that the plant biomass is less in amount, a complete enhanced network cannot be generated, the enhancement effect is limited, and the overall strength of the cementing material is low;
compared with the embodiment 1, the comparative example 3 has the advantages that the plant biomass content is high, and the plant biomass content can be widely distributed at the interface of the solid waste particles, so that the dissolution reaction of alkali to the solid waste is affected, and the long-term strength of the cementing material is reduced;
comparative example 4, compared with example 1, has poor excitation effect because the amount of the alkali-activator is too small, and a jelly cannot be formed between particles, and the jelly cannot be combined into a whole, so that sufficient overall strength cannot be provided; in addition, the alkali-exciting agent cannot be excessive, and excessive alkali-exciting agent can generate whiskering;
comparative example 5 compared with example 1, because the mass ratio of water to solid waste is too high, i.e., the water to ash ratio is too large, the spacing of the solid particles in the slurry is large, the colloid produced by hydration cannot fill the gaps between the particles, and in addition, too much water evaporates to leave more water gaps, thereby reducing the strength of the cementitious material;
comparative examples 6, 7 and 8 did not contain biomass and/or starch composite binder, so that the early strength of the samples was lowered and the later strength was raised as alkali excitation proceeded for a long period of time, compared with example 1; as can be seen from the comparison of comparative examples 6 and 7 with example 1, the flexural strength of the samples was drastically reduced in the absence of the plant biomass binder; in addition, the cementing material prepared by the invention achieves better compressive strength and flexural strength under the synergistic effect of plant biomass and starch in the composite binder;
comparative example 9 compared with example 1, the starch content is too high and is widely distributed at the interface of the solid waste particles, so that the dissolution reaction of alkali on the solid waste is affected, and the long-term strength of the cementing material is reduced;
as can be seen from comparison of comparative examples 10, 11 and 12 with example 1, at least three industrial solid wastes exist simultaneously, so that the compressive strength and the flexural strength of the cementing material can be synergistically enhanced;
in comparative example 13, the alkali activation excitation temperature is higher, on the one hand, the plant biomass dissolution reaction is more thoroughly carried out, the residual quantity of the fiber of the early-stage excited plant matter is reduced, and the early strength is reduced; on the other hand, too much alkali is consumed in the early stage, so that the subsequent smooth progress of alkali-activated industrial solid waste is affected, and the long-term strength is also reduced.
Finally, it should be noted that the above description is only for illustrating the technical solution of the present invention, and not for limiting the scope of the present invention, and that the simple modification and equivalent substitution of the technical solution of the present invention can be made by those skilled in the art without departing from the spirit and scope of the technical solution of the present invention.

Claims (10)

1. The composite biomass binder modified alkali-activated cementing material is characterized in that the cementing material comprises the following components: alkali excitant, composite biomass binder and industrial solid waste; the composite biomass binder comprises the following components: plant biomass and starch.
2. The cementing material according to claim 1, wherein the mass ratio of the alkali-activator to the industrial solid waste is 0.1-0.25:1; the mass ratio of the plant biomass to the industrial solid waste is 0.005-0.05:1; the mass ratio of the starch to the industrial solid waste is 0.005-0.05:1.
3. The cementitious material of claim 1, wherein said alkali-activator is at least one of sodium hydroxide, sodium silicate, sodium sulfate, sodium phosphate, sodium citrate, sodium bicarbonate, potassium hydroxide, potassium silicate, potassium sulfate, potassium phosphate, potassium citrate, and potassium bicarbonate;
the industrial solid waste is mixed industrial solid waste composed of at least three of carbide slag, tailings, metallurgical slag, coal gangue, fly ash, desulfurized gypsum, red mud, phosphogypsum and stone processing bottom mud;
the plant biomass is at least one of bagasse, corn cob, sawdust, rice chaff, coconut husk, straw, wheat straw and corn straw;
the starch is at least one of wheat starch, corn starch, water chestnut starch, mung bean starch, pea starch, sweet potato starch, tapioca starch, potato starch and lotus root starch.
4. A cementitious material in accordance with claim 3, wherein said mixed industrial solid waste comprises at least one of carbide slag, metallurgical slag and red mud;
the plant biomass is at least one of coconut shells, rice straws and wheat straws;
the starch is at least one of wheat starch, corn starch, mung bean starch, tapioca starch and pea starch.
5. The cementitious material of claim 1, wherein said industrial solid waste has a particle size of 200 μm or less; the particle size of the plant biomass is less than or equal to 200 mu m; the grain size of the starch is 50-300 mu m.
6. The cement according to claim 1, wherein the cement composition further comprises water; the mass ratio of water to industrial solid waste is 0.35-0.6:1.
7. The method for preparing a cement according to any one of claims 1 to 6, comprising the steps of:
(1) Dissolving an alkali-activated agent in water, adding plant biomass for alkali activation and excitation to obtain slurry 1;
(2) Adding starch into the slurry 1, stirring and dispersing to obtain slurry 2;
(3) And adding industrial solid waste into the slurry 2, and stirring and dispersing to obtain the cementing material.
8. The method according to claim 7, wherein in the step (1), the alkali activation excitation temperature is room temperature for 2 to 24 hours.
9. The process according to claim 7, wherein in the step (2), the stirring and dispersing temperature is room temperature for 5 to 30 minutes.
10. The process according to claim 7, wherein in the step (3), the stirring and dispersing temperature is room temperature for 3 to 10 minutes.
CN202310840966.5A 2023-07-11 2023-07-11 Composite biomass binder modified alkali-activated cementing material and preparation method thereof Pending CN116947338A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN117602893A (en) * 2024-01-24 2024-02-27 南京工业大学 High-strength high-durability biomass non-calcium cement, preparation and use methods thereof
CN117843303A (en) * 2024-01-09 2024-04-09 淮阴工学院 Geopolymer-based composition, composite material and preparation method thereof

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN117843303A (en) * 2024-01-09 2024-04-09 淮阴工学院 Geopolymer-based composition, composite material and preparation method thereof
CN117602893A (en) * 2024-01-24 2024-02-27 南京工业大学 High-strength high-durability biomass non-calcium cement, preparation and use methods thereof

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