[go: up one dir, main page]

CN117285325B - A preparation process of highly water-resistant magnesium-phosphate cement-based material - Google Patents

A preparation process of highly water-resistant magnesium-phosphate cement-based material Download PDF

Info

Publication number
CN117285325B
CN117285325B CN202311332500.0A CN202311332500A CN117285325B CN 117285325 B CN117285325 B CN 117285325B CN 202311332500 A CN202311332500 A CN 202311332500A CN 117285325 B CN117285325 B CN 117285325B
Authority
CN
China
Prior art keywords
parts
based material
water
phosphate cement
preparation process
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
CN202311332500.0A
Other languages
Chinese (zh)
Other versions
CN117285325A (en
Inventor
甘星宇
姜承志
于欣欣
李来波
芦令超
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.)
University of Jinan
Original Assignee
University of Jinan
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 University of Jinan filed Critical University of Jinan
Priority to CN202311332500.0A priority Critical patent/CN117285325B/en
Publication of CN117285325A publication Critical patent/CN117285325A/en
Application granted granted Critical
Publication of CN117285325B publication Critical patent/CN117285325B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • C04B28/34Compositions 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 cold phosphate binders
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B32/00Carbon; Compounds thereof
    • C01B32/05Preparation or purification of carbon not covered by groups C01B32/15, C01B32/20, C01B32/25, C01B32/30
    • 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
    • C04B12/00Cements not provided for in groups C04B7/00 - C04B11/00
    • C04B12/02Phosphate 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
    • C04B14/00Use of inorganic materials as fillers, e.g. pigments, for mortars, concrete or artificial stone; Treatment of inorganic materials specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B14/02Granular materials, e.g. microballoons
    • C04B14/022Carbon
    • C04B14/026Carbon of particular shape, e.g. nanotubes
    • 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
    • C04B2111/20Resistance against chemical, physical or biological attack
    • C04B2111/27Water resistance, i.e. waterproof or water-repellent materials
    • 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
    • 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

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Nanotechnology (AREA)
  • Civil Engineering (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

本发明涉及磷镁水泥技术领域,具体公开一种高耐水性磷镁水泥基材料的制备工艺。该制备工艺包括如下步骤:(1)将生物质碳源置于加热炉中密闭后在静态空气状态下进行热解碳化处理。完成后冷却至室温,将得到的碳化产物与磷源混合研磨成粉体,然后将该粉体置于加热炉中密闭后在静态空气状态下进行热处理。完成后冷却至室温,将得到的产物酸洗后水洗、干燥,即得改性多孔碳材料。(2)将所述改性多孔碳材料与重烧氧化镁、磷酸二氢铵或磷酸二氢钾、硼砂、粉煤灰、硅灰、细骨料、粗骨料、水复配,即得高耐水性磷镁水泥。本发明通过能够特异性吸附磷酸根离子的多孔碳材料,有效改善了磷镁水泥因磷酸根离子的溶出而造成的强度损失和泛碱的问题。

The present invention relates to the technical field of magnesium phosphate cement, and specifically discloses a preparation process of a magnesium phosphate cement-based material with high water resistance. The preparation process comprises the following steps: (1) placing a biomass carbon source in a sealed heating furnace and then performing pyrolysis and carbonization treatment under a static air state. After completion, the biomass carbon source is cooled to room temperature, the obtained carbonized product is mixed with a phosphorus source and ground into a powder, and then the powder is placed in a sealed heating furnace and then heat-treated under a static air state. After completion, the biomass carbon source is cooled to room temperature, and then the obtained product is acid-washed, washed with water, and dried to obtain a modified porous carbon material. (2) The modified porous carbon material is compounded with dead-burned magnesium oxide, ammonium dihydrogen phosphate or potassium dihydrogen phosphate, borax, fly ash, silica fume, fine aggregate, coarse aggregate, and water to obtain a magnesium phosphate cement with high water resistance. The present invention effectively improves the strength loss and alkali-fading problems of magnesium phosphate cement caused by the dissolution of phosphate ions by using a porous carbon material that can specifically adsorb phosphate ions.

Description

Preparation process of high-water-resistance phosphorus-magnesium cement-based material
Technical Field
The invention relates to the technical field of phosphorus-magnesium cement-based materials, in particular to a preparation process of a high-water-resistance phosphorus-magnesium cement-based material.
Background
The disclosure of this background section is only intended to increase the understanding of the general background of the invention and is not necessarily to be construed as an admission or any form of suggestion that this information forms the prior art already known to those of ordinary skill in the art.
The phosphorus-magnesium cement is a new type special cement, which has quick setting and hardening, high early strength and good compatibility with common silicate cement, so that the phosphorus-magnesium cement is often used for quick rush repair engineering. However, the hydration product of the phosphorus-magnesium cement, namely struvite (Struvite, mgNH 4PO4·6H2 O), has weaker water stability, and after being corroded by water, the struvite is often corroded into phosphate ions, ammonium ions and magnesium ions, migrates to the outside from pores inside the phosphorus-magnesium cement, and is recrystallized on the surface of the phosphorus-magnesium cement to generate struvite crystals again, so that the phosphorus-magnesium cement has serious strength loss and has a large-area 'whiskering' phenomenon. Therefore, improving the water resistance of phosphorus magnesium cements has been a challenging task.
Because of the specificity of the composition of the phosphorus-magnesium cement, the consumption of magnesium raw materials is often far more than that of the phosphorus raw materials, the rest magnesium serves as a framework structure to play a supporting role in the cement, hydration products begin to nucleate and grow by taking magnesium as a framework, and gradually crosslink into a reticular structure, and finally the cement body is formed. Since phosphorus is indispensable and the content is far lower than that of magnesium, reducing the dissolution of phosphorus is a fundamental measure for solving the water resistance of phosphorus-magnesium cement. The main method at present is to add mineral admixture and superfine powder into phosphorus-magnesium cement. The purpose of this method is to allow finer mineral particles to fill the pores of the cement, thereby reducing the ingress of water into the cement matrix in the external environment. However, the method does not fundamentally improve the water resistance of the phosphorus-magnesium cement, and the prepared phosphorus-magnesium cement still has the problem of insufficient water resistance.
Disclosure of Invention
Aiming at the problems, the invention provides a preparation process of a high-water-resistance phosphorus-magnesium cement-based material, and the problems of strength loss and whiskering of phosphorus-magnesium cement caused by dissolution of phosphate ions are effectively solved by the porous carbon material capable of specifically adsorbing the phosphate ions. In order to achieve the above purpose, the present invention discloses the following technical solutions.
A preparation process of a high-water-resistance phosphorus-magnesium cement-based material comprises the following steps:
(1) And (3) placing the biomass carbon source into a heating furnace, sealing, and performing pyrolysis carbonization treatment in a static air state. Cooling to room temperature after completion, mixing and grinding the obtained carbonized product and a phosphorus source into powder, and then placing the powder into a heating furnace for sealing and then carrying out heat treatment in a static air state. And cooling to room temperature after the completion, washing the obtained product with acid, and drying to obtain the modified porous carbon material.
(2) And (3) compounding the modified porous carbon material with the re-burned magnesium oxide, ammonium dihydrogen phosphate or potassium dihydrogen phosphate, borax, fly ash, silica fume, fine aggregate, coarse aggregate and water to obtain the high-water-resistance phosphorus-magnesium cement-based material.
Further, in step (1), the biomass carbon source includes, but is not limited to: at least one of chitosan, wheat straw, wood, rice straw, hemp stalk, etc.
In the invention, the static air state refers to that air in a heating environment is not circulated or external air is introduced in the heating process, and the atmosphere environment in the initial heating state is taken as a process environment until the pyrolysis carbonization treatment or the heat treatment is finished, and the product obtained by the treatment is continuously naturally cooled to the room temperature in the environment.
Further, in the step (1), the temperature of the pyrolysis carbonization treatment is 200-700 ℃ and the time is 2-8 h.
Further, in the step (1), the mass ratio of the carbonized product to the phosphorus source is 1-3: 1. preferably, the phosphorus source includes at least one of monopotassium phosphate, sodium acid pyrophosphate, sodium metaphosphate, manganese hypophosphite, metaphosphoric acid, and the like.
Further, in the step (1), the heat treatment temperature is 200-500 ℃ and the time is 2-8 h. And introducing a phosphorus source into the carbonized product, and then performing heat treatment again in a static air state to regulate and control the carbonized product so as to form positively charged oxygen vacancies and form the porous carbon material rich in the special oxygen vacancies.
Further, in the step (1), the pickling process comprises the following steps: and (3) placing the product into citric acid or acetic acid and stirring for 10-30 min to finish the pickling process. Optionally, the mass fraction of the citric acid or the acetic acid is 5-20%. The acid washing is used for removing superfluous functional groups on the surface of the product, so that the reaction with a cement matrix is avoided, and the adsorption effect is reduced.
Further, in the step (1), the water washing process is as follows: and washing the acid-washed product with clear water until the washing liquid is neutral, thereby completing the water washing process.
Further, in the step (1), the drying temperature is 30-70 ℃ and the drying time is 12-24 h.
Further, in the step (2), the proportion of each raw material is as follows: 5 to 30 parts of modified porous carbon material, 200 to 400 parts of burned magnesia, 80 to 120 parts of ammonium dihydrogen phosphate or potassium dihydrogen phosphate, 70 to 130 parts of borax, 20 to 90 parts of fly ash, 20 to 90 parts of silica fume, 500 to 700 parts of fine aggregate, 800 to 1600 parts of coarse aggregate and 150 to 300 parts of water.
Optionally, the fineness of the monoammonium phosphate or potassium dihydrogen phosphate, the fly ash and the silica fume is 100-300 meshes.
Compared with the prior art, the technical scheme of the invention has at least the following beneficial effects:
Aiming at the problems of strength loss and alkali efflorescence caused by the dissolution of phosphate ions of the phosphorus-magnesium cement, the invention prepares the porous carbon material capable of specifically adsorbing the phosphate ions, and the porous carbon material is matched with the phosphorus-magnesium cement to radically improve the water resistance of the phosphorus-magnesium cement. The porous carbon material prepared by adopting the special process has rich oxygen vacancies and obvious electropositivity, can specifically adsorb phosphate ions in cement paste, is chemically inert, and can adsorb and release the phosphate ions according to the concentration difference of the phosphate ions in the internal environment of the phosphorus-magnesium cement. Thereby: when the phosphate cement is corroded by water, the hydration product, namely bird droppings Dan Rongshi, is phosphate ions and the like, the concentration of the phosphate ions in the phosphate cement is increased, and the excessive phosphate ions are adsorbed and stored in the porous carbon material and cannot be lost to the outside of the phosphate cement. And after the normal environment without rain wash is restored, ammonium ions and magnesium ions formed by the struvite corrosion react with phosphate ions from new water to form struvite crystals. As the cement hydration proceeds, the phosphate ions in the phosphorus-magnesium cement are gradually consumed, when the phosphate ion concentration is lower than that in the porous carbon material, the phosphate ions stored in the carbon material are released into the cement body continuously to participate in the hydration reaction, new hydration products are continuously generated until the hydration is complete, and the problems of phosphorus-magnesium cement strength loss and alkali efflorescence caused by the loss of the phosphate ions with lower content but indispensable content due to dissolution are well avoided, so that the water resistance of the phosphorus-magnesium cement is fundamentally improved.
In addition, in order to achieve the above object, the present invention proposes a process capable of preparing a porous carbon material having abundant positively charged oxygen vacancies, and first, the present invention subjects a biomass carbon source to pyrolysis carbonization treatment in a static air state, thereby being capable of forming a carbonized product while also being capable of introducing a special site of oxygen vacancies therein. Furthermore, the invention also utilizes a phosphorus source to regulate oxygen vacancies in the carbonized product, and the existence of phosphorus is used for balancing charges, increasing vacancies and increasing the adsorption quantity of phosphate ions. This is because phosphorus is less electronegative than oxygen and carbon, and therefore has less ability to attract electrons than carbon and oxygen, and has weaker adsorption ability to electrons when oxygen vacancies are formed. Oxygen atoms are less limited as they become superoxide radicals and electrons leave the matrix, thereby making it easier to create more oxygen vacancies in the carbon material.
Drawings
The accompanying drawings, which are included to provide a further understanding of the invention and are incorporated in and constitute a part of this specification, illustrate embodiments of the invention and together with the description serve to explain the invention. Embodiments of the present invention are described in detail below with reference to the attached drawing figures, wherein:
FIG. 1 is a graph showing the effect of the modified porous carbon material prepared in example 1 of the present invention.
FIG. 2 is a graph showing the curing effect in water of the test block prepared in example 1 of the present invention.
FIG. 3 is a graph showing the compressive strength test of the test block prepared in example 1 of the present invention.
Fig. 4 is an effect diagram of the modified porous carbon material prepared in example 4 of the present invention.
Detailed Description
The invention will be further illustrated with reference to specific examples. It is to be understood that these examples are illustrative of the present invention and are not intended to limit the scope of the present invention. The experimental procedures, which do not address the specific conditions in the examples below, are generally carried out under conventional conditions or under conditions recommended by the manufacturer.
Unless defined otherwise, all technical and scientific terms used herein have the same meaning as commonly understood by one of ordinary skill in the art to which this invention belongs. The reagents or materials used in the present invention may be purchased in conventional manners, and unless otherwise indicated, they may be used in conventional manners in the art or according to the product specifications.
In addition, any methods and materials similar or equivalent to those described herein can be used in the methods of the present invention. The technical scheme of the invention is further described with reference to the specification, the drawings and the specific embodiments.
Example 1
A preparation process of a high-water-resistance phosphorus-magnesium cement-based material comprises the following steps:
(1) Placing chitosan into a tubular furnace, heating the tubular furnace to 400 ℃ at a heating rate of 10 ℃/min in a static air state, and preserving the temperature for 5 hours to carry out pyrolysis carbonization treatment on the chitosan. And naturally cooling to room temperature after the completion of the process to obtain a carbonized product for standby.
(2) Mixing the carbonized product with sodium metaphosphate according to the following 2:1, grinding the mixture into 200-mesh powder after mixing, then placing the powder into a tube furnace, heating the tube furnace to 400 ℃ at a heating rate of 10 ℃/min in a static air state after sealing the tube furnace, and carrying out heat treatment by preserving heat for 3 hours. After completion, cooling to room temperature, adding the obtained solid product into 5% citric acid solution by mass fraction, stirring for 30min, and pickling. After completion, the solid product was separated by centrifugation and washed with clean water until the wash liquor was neutral. And then placing the solid product in an oven and drying at 70 ℃ for 12 hours to obtain the modified porous carbon material (shown in figure 1) for standby.
(3) The following raw materials are taken: 10 parts of modified porous carbon material, 300 parts of burned magnesia, 100 parts of ammonium dihydrogen phosphate, 105 parts of borax, 75 parts of fly ash, 60 parts of silica fume, 650 parts of river sand fine aggregate, 1300 parts of crushed stone coarse aggregate and 260 parts of water. Wherein: the fineness of the monoammonium phosphate, the fly ash and the silica fume is 300 meshes. And adding the solid components in the raw materials into a stirrer, dry mixing for 2min, and then adding the water, and rapidly stirring for 3min to obtain the phosphorus-magnesium cement slurry.
1. The X-ray absorption fine structure spectrum test and Zeta potential test of the modified porous carbon material synchrotron radiation prepared in the embodiment show that: oxygen vacancy content=2.57%, zeta potential=3.65 mV. It can be seen that: the modified porous carbon material has rich oxygen vacancies and obvious electropositive characteristic.
2. Mass loss rate test: the phosphorus magnesium cement slurry prepared in this example was poured into a mold having a size of 40 x 40mm, and demolding after six hours. And then curing (shown in figure 2) in water for 28 days to obtain the test block. The concrete calculation method of the mass loss rate comprises the following steps: the mass of the test block before entering water is recorded as A1, after curing in water for 28 days, the test block is taken out from the water, the water on the surface of the test block is wiped off, the mass of the test block is measured as A2, and the mass loss rate is the ratio of (A1-A2)/A1.
3. Intensity loss rate test: the phosphorus magnesium cement slurry prepared in this example was poured into a mold having a size of 40 x 40mm, and demolding after six hours. And curing in the air for 28 days to obtain the test block. Test pieces were prepared by the same method, and after demolding, were left in water for curing for 28 days. The specific calculation method of the intensity loss rate comprises the following steps: the compressive strength of the block obtained by curing in air for 28 days was denoted as B1 (see FIG. 3), the compressive strength of the block obtained by curing in water for 28 days was denoted as B2, and (B1-B2)/B1 was denoted as strength loss.
The phosphorus-magnesium cement prepared by the invention can be characterized in terms of water resistance through the mass loss rate and the strength loss rate, and the test results are as follows: mass loss rate=0.77%, strength loss rate=20.04%.
Example 2
A preparation process of a high-water-resistance phosphorus-magnesium cement-based material comprises the following steps:
(1) Placing crushed straw into a tube furnace, sealing the tube furnace, heating to 700 ℃ at a heating rate of 10 ℃/min in a static air state, and preserving heat for 2 hours to carry out pyrolysis carbonization treatment on the straw. And naturally cooling to room temperature after the completion of the process to obtain a carbonized product for standby.
(2) Mixing the carbonized product with potassium dihydrogen phosphate according to the weight ratio of 1.5:1, grinding the mixture into 200-mesh powder after mixing, then placing the powder into a tube furnace, heating the tube furnace to 500 ℃ in a static air state at a heating rate of 10 ℃/min, and preserving heat for 2 hours for heat treatment. After completion, cooling to room temperature, adding the obtained solid product into a citric acid solution with the mass fraction of 10%, stirring for 20min, and carrying out acid washing. After completion, the solid product was separated by centrifugation and washed with clean water until the wash liquor was neutral. And then placing the solid product in an oven and drying at 30 ℃ for 24 hours to obtain the modified porous carbon material (shown in figure 4) for standby.
(3) The following raw materials are taken: 30 parts of modified porous carbon material, 400 parts of burned magnesia, 120 parts of monopotassium phosphate, 130 parts of borax, 90 parts of fly ash, 90 parts of silica fume, 700 parts of river sand fine aggregate, 1600 parts of crushed stone coarse aggregate and 300 parts of water. Wherein: the fineness of the potassium dihydrogen phosphate, the fly ash and the silica fume is 100 meshes. And adding the solid components in the raw materials into a stirrer, dry mixing for 2min, and then adding the water, and rapidly stirring for 3min to obtain the phosphorus-magnesium cement slurry.
1. And carrying out spectrum test on the X-ray absorption fine structure of the synchrotron radiation of the modified porous carbon material prepared in the embodiment. The results show that: oxygen vacancy content=2.68%, zeta potential=3.89 mV. It can be seen that: the modified porous carbon material has rich oxygen vacancies and obvious electropositive characteristic.
2. The mass loss rate and the strength loss rate of the phosphorus-magnesium cement test block prepared in this example were tested by the same method as in example 1, and the test results were: mass loss rate=0.72%, strength loss rate=17.54%.
Example 3
A preparation process of a high-water-resistance phosphorus-magnesium cement-based material comprises the following steps:
(1) Placing the crushed hemp stems into a tubular furnace, heating the tubular furnace to 200 ℃ at a heating rate of 10 ℃/min in a static air state, and preserving the heat for 8 hours to carry out pyrolysis carbonization treatment on the hemp stems. And naturally cooling to room temperature after the completion of the process to obtain a carbonized product for standby.
(2) Mixing the carbonized product with sodium acid pyrophosphate according to a ratio of 3:1, grinding the mixture into 300 meshes of powder after mixing, then placing the powder into a tube furnace, heating the tube furnace to 200 ℃ at a heating rate of 10 ℃/min in a static air state after sealing the tube furnace, and carrying out heat treatment by preserving heat for 8 hours. After completion, cooling to room temperature, adding the obtained solid product into a citric acid solution with the mass fraction of 20%, stirring for 10min, and carrying out acid washing. After completion, the solid product was separated by centrifugation and washed with clean water until the wash liquor was neutral. And then placing the solid product in an oven and drying at 40 ℃ for 18 hours to obtain the modified porous carbon material for later use.
(3) The following raw materials are taken: the modified porous carbon material prepared in the embodiment comprises 5 parts by weight of burned magnesium oxide 200 parts by weight, potassium dihydrogen phosphate 80 parts by weight, borax 70 parts by weight, fly ash 20 parts by weight, silica fume 20 parts by weight, river sand fine aggregate 500 parts by weight, crushed stone coarse aggregate 800 parts by weight and water 150 parts by weight. Wherein: the fineness of the potassium dihydrogen phosphate, the fly ash and the silica fume is 200 meshes. And adding the solid components in the raw materials into a stirrer, dry mixing for 2min, and then adding the water, and rapidly stirring for 3min to obtain the phosphorus-magnesium cement slurry.
The spectrum test of the X-ray absorption fine structure of the synchrotron radiation of the modified porous carbon material prepared in the embodiment shows that: oxygen vacancy content=2.44%, zeta potential=3.51 mV. It can be seen that: the modified porous carbon material has rich oxygen vacancies and obvious electropositive characteristic.
2. The mass loss rate and the strength loss rate of the phosphorus-magnesium cement test block prepared in this example were tested by the same method as in example 1, and the test results were: mass loss rate=0.86%, strength loss rate=21.60%.
Example 4
A preparation process of a high-water-resistance phosphorus-magnesium cement-based material comprises the following steps: the following raw materials are taken: 300 parts of burned magnesia, 100 parts of ammonium dihydrogen phosphate, 105 parts of borax, 75 parts of fly ash, 60 parts of silica fume, 650 parts of river sand fine aggregate, 1300 parts of crushed stone coarse aggregate and 260 parts of water. Wherein: the fineness of the monoammonium phosphate, the fly ash and the silica fume is 300 meshes. And adding the solid components in the raw materials into a stirrer, dry mixing for 2min, and then adding the water, and rapidly stirring for 3min to obtain the phosphorus-magnesium cement slurry.
The mass loss rate and the strength loss rate of the phosphorus-magnesium cement test block prepared in this example were tested by the same method as in example 1, and the test results were: mass loss rate=1.79%, strength loss rate=52.14%.
Example 5
A preparation process of a high-water-resistance phosphorus-magnesium cement-based material comprises the following steps:
The following raw materials are taken: 30 parts of mineral particles (fly ash with 300 meshes), 400 parts of burned magnesia, 120 parts of monopotassium phosphate, 130 parts of borax, 90 parts of fly ash, 90 parts of silica fume, 700 parts of river sand fine aggregate, 1600 parts of crushed stone coarse aggregate and 300 parts of water. Wherein: the fineness of the potassium dihydrogen phosphate, the fly ash and the silica fume is 100 meshes. And adding the solid components in the raw materials into a stirrer, dry mixing for 2min, and then adding the water, and rapidly stirring for 3min to obtain the phosphorus-magnesium cement slurry.
The mass loss rate and the strength loss rate of the phosphorus-magnesium cement test block prepared in this example were tested by the same method as in example 1, and the test results were: mass loss rate=1.64%, intensity loss rate= 47.58%.
Example 6
A preparation process of a high-water-resistance phosphorus-magnesium cement-based material comprises the following steps:
The following raw materials are taken: 30 parts of mineral particles (silica fume with fineness of 400 meshes), 400 parts of burned magnesia, 120 parts of monopotassium phosphate, 130 parts of borax, 90 parts of fly ash, 90 parts of silica fume, 700 parts of river sand fine aggregate, 1600 parts of crushed stone coarse aggregate and 300 parts of water. Wherein: the fineness of the potassium dihydrogen phosphate, the fly ash and the silica fume is 100 meshes. And adding the solid components in the raw materials into a stirrer, dry mixing for 2min, and then adding the water, and rapidly stirring for 3min to obtain the phosphorus-magnesium cement slurry.
The mass loss rate and the strength loss rate of the phosphorus-magnesium cement test block prepared in this example were tested by the same method as in example 1, and the test results were: mass loss rate=1.68% and strength loss rate= 46.27%.
Example 7
The preparation process of the high-water-resistance phosphorus-magnesium cement-based material is the same as that of the above example 3, except that the modified porous carbon material of this example is prepared by the following method:
(1) Placing the crushed hemp stems into a tubular furnace, heating the tubular furnace to 200 ℃ at a heating rate of 10 ℃/min in a static air state, and preserving the heat for 8 hours to carry out pyrolysis carbonization treatment on the hemp stems. And naturally cooling to room temperature after the completion of the process to obtain a carbonized product for standby.
(2) And adding the carbonized product into a citric acid solution with the mass fraction of 20%, and stirring for 10min for pickling. After completion, the solid product was separated by centrifugation and washed with clean water until the wash liquor was neutral. And then placing the solid product in an oven and drying at 40 ℃ for 12 hours to obtain the modified porous carbon material.
1. And carrying out spectrum test on the X-ray absorption fine structure of the synchrotron radiation of the modified porous carbon material prepared in the embodiment. The results show that: oxygen vacancy content=2.08%, zeta potential=2.95 mV. It can be seen that: the modified porous carbon material has low oxygen vacancy content and obviously weakened electropositive characteristic.
2. The mass loss rate and the strength loss rate of the phosphorus-magnesium cement test block prepared in this example were tested by the same method as in example 1, and the test results were: mass loss rate=1.26%, strength loss rate=36.5%.
Example 8
The preparation process of the high-water-resistance phosphorus-magnesium cement-based material is the same as that of the above example 2, except that the modified porous carbon material of this example is prepared by the following method:
(1) Crushed straw was mixed with potassium dihydrogen phosphate according to 1.5:1, placing the rice straw into a tubular furnace, heating the rice straw to 700 ℃ at a heating rate of 10 ℃/min in a static air state after sealing the tubular furnace, and preserving the heat for 2 hours to carry out pyrolysis carbonization treatment on the rice straw. And naturally cooling to room temperature after the completion of the process to obtain a carbonized product for standby.
(2) The carbonized product is ground into 200-mesh powder, and then added into 10% citric acid solution by mass fraction, and stirred for 20min for pickling. After completion, the solid product was separated by centrifugation and washed with clean water until the wash liquor was neutral. And then placing the solid product in an oven and drying at 30 ℃ for 24 hours to obtain the modified porous carbon material for later use.
1. And carrying out spectrum test on the X-ray absorption fine structure of the synchrotron radiation of the modified porous carbon material prepared in the embodiment. The results show that: oxygen vacancy content=2.17%, zeta potential=3.03 mV. It can be seen that: the modified porous carbon material has relatively low oxygen vacancy content and obviously weakened electropositive characteristic.
2. The mass loss rate and the strength loss rate of the phosphorus-magnesium cement test block prepared in this example were tested by the same method as in example 1, and the test results were: mass loss = 1.07%, strength loss = 25.33%.
The foregoing description is only a preferred embodiment of the present invention, and the present invention is not limited thereto, but it is to be understood that modifications and equivalents of some of the technical features described in the foregoing embodiments may be made by those skilled in the art, although the present invention has been described in detail with reference to the foregoing embodiments. Any modification, equivalent replacement, improvement, etc. made within the spirit and principle of the present invention should be included in the protection scope of the present invention.

Claims (10)

1.一种高耐水性磷镁水泥基材料的制备工艺,其特征在于,包括如下步骤:1. A preparation process of a highly water-resistant magnesium-phosphate cement-based material, characterized in that it comprises the following steps: (1)将生物质碳源置于加热炉中密闭后在静态空气状态下进行热解碳化处理;完成后冷却至室温,将得到的碳化产物与磷源按质量比1~3:1混合后研磨成粉体,然后将该粉体置于加热炉中密闭后在静态空气状态下进行热处理;完成后冷却至室温,将得到的产物酸洗后水洗、干燥,即得改性多孔碳材料;(1) placing a biomass carbon source in a sealed heating furnace and then performing pyrolysis carbonization treatment under static air conditions; after completion, cooling to room temperature, mixing the obtained carbonization product with a phosphorus source at a mass ratio of 1 to 3:1 and grinding the mixture into powder, and then placing the powder in a sealed heating furnace and then performing heat treatment under static air conditions; after completion, cooling to room temperature, acid-washing the obtained product, washing it with water, and drying it to obtain a modified porous carbon material; (2)将所述改性多孔碳材料5~30重量份、重烧氧化镁200~400重量份、磷酸二氢铵或磷酸二氢钾80~120重量份、硼砂70~130重量份、粉煤灰20~90重量份、硅灰20~90重量份、细骨料500~700重量份、粗骨料800~1600重量份、水150~300重量份复配,即得高耐水性磷镁水泥基材料。(2) 5-30 parts by weight of the modified porous carbon material, 200-400 parts by weight of dead-burned magnesium oxide, 80-120 parts by weight of ammonium dihydrogen phosphate or potassium dihydrogen phosphate, 70-130 parts by weight of borax, 20-90 parts by weight of fly ash, 20-90 parts by weight of silica fume, 500-700 parts by weight of fine aggregate, 800-1600 parts by weight of coarse aggregate, and 150-300 parts by weight of water are compounded to obtain a highly water-resistant magnesium phosphate cement-based material. 2.根据权利要求1所述的高耐水性磷镁水泥基材料的制备工艺,其特征在于,步骤(1)中,所述生物质碳源包括:壳聚糖、麦秸秆、木材、稻草、麻杆中的至少一种。2. The preparation process of the highly water-resistant magnesium-phosphate cement-based material according to claim 1, characterized in that in step (1), the biomass carbon source comprises at least one of chitosan, wheat straw, wood, rice straw, and hemp stalks. 3.根据权利要求1所述的高耐水性磷镁水泥基材料的制备工艺,其特征在于,步骤(1)中,所述热解碳化处理的温度为200~700℃,时间为2~8h。3. The process for preparing a highly water-resistant magnesium-phosphate cement-based material according to claim 1, characterized in that, in step (1), the temperature of the pyrolysis carbonization treatment is 200-700°C and the time is 2-8 hours. 4.根据权利要求1所述的高耐水性磷镁水泥基材料的制备工艺,其特征在于,所述磷源包括磷酸二氢钾、酸式焦磷酸钠、偏磷酸钠、次磷酸锰、偏焦磷酸中的至少一种。4. The preparation process of the highly water-resistant magnesium-phosphate cement-based material according to claim 1, characterized in that the phosphorus source includes at least one of potassium dihydrogen phosphate, sodium acid pyrophosphate, sodium metaphosphate, manganese hypophosphite, and metapyrophosphoric acid. 5.根据权利要求1所述的高耐水性磷镁水泥基材料的制备工艺,其特征在于,步骤(1)中,所述热处理温度为200~500℃,时间为2~8h。5. The preparation process of the highly water-resistant magnesium-phosphate cement-based material according to claim 1, characterized in that in step (1), the heat treatment temperature is 200-500°C and the time is 2-8 hours. 6.根据权利要求1所述的高耐水性磷镁水泥基材料的制备工艺,其特征在于,步骤(1)中,所述酸洗的工艺为:将所述产物置于柠檬酸或醋酸中搅拌10~30min,即完成酸洗工序。6. The preparation process of the highly water-resistant magnesium phosphate cement-based material according to claim 1 is characterized in that in step (1), the pickling process is: placing the product in citric acid or acetic acid and stirring for 10 to 30 minutes to complete the pickling process. 7.根据权利要求6所述的高耐水性磷镁水泥基材料的制备工艺,其特征在于,所述柠檬酸或醋酸的质量分数为5~20%。7. The preparation process of the highly water-resistant magnesium phosphate cement-based material according to claim 6, characterized in that the mass fraction of the citric acid or acetic acid is 5-20%. 8.根据权利要求1所述的高耐水性磷镁水泥基材料的制备工艺,其特征在于,步骤(1)中,所述水洗的工艺为:将所述酸洗后的产物用清水洗涤至洗涤液为中性,即完成所述水洗工序。8. The process for preparing a highly water-resistant magnesium-phosphate cement-based material according to claim 1, characterized in that in step (1), the water washing process is: washing the acid-washed product with clean water until the washing liquid is neutral, thus completing the water washing process. 9.根据权利要求1所述的高耐水性磷镁水泥基材料的制备工艺,其特征在于,步骤(1)中,所述干燥的温度为30~70℃,时间为12~24h。9. The process for preparing a highly water-resistant magnesium-phosphate cement-based material according to claim 1, characterized in that in step (1), the drying temperature is 30-70°C and the drying time is 12-24 hours. 10.根据权利要求9所述的高耐水性磷镁水泥基材料的制备工艺,其特征在于,所述磷酸二氢铵或磷酸二氢钾、粉煤灰、硅灰的细度均为100~300目。10. The preparation process of the highly water-resistant magnesium-phosphate cement-based material according to claim 9, characterized in that the fineness of the ammonium dihydrogen phosphate or potassium dihydrogen phosphate, fly ash and silica fume is 100-300 mesh.
CN202311332500.0A 2023-10-16 2023-10-16 A preparation process of highly water-resistant magnesium-phosphate cement-based material Active CN117285325B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202311332500.0A CN117285325B (en) 2023-10-16 2023-10-16 A preparation process of highly water-resistant magnesium-phosphate cement-based material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202311332500.0A CN117285325B (en) 2023-10-16 2023-10-16 A preparation process of highly water-resistant magnesium-phosphate cement-based material

Publications (2)

Publication Number Publication Date
CN117285325A CN117285325A (en) 2023-12-26
CN117285325B true CN117285325B (en) 2024-11-12

Family

ID=89244344

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202311332500.0A Active CN117285325B (en) 2023-10-16 2023-10-16 A preparation process of highly water-resistant magnesium-phosphate cement-based material

Country Status (1)

Country Link
CN (1) CN117285325B (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101058213A (en) * 2007-06-01 2007-10-24 济南大学 Method for preparing building material with carbonization maintenance waste
CN112774628A (en) * 2021-01-07 2021-05-11 昆明理工大学 Method for preparing biochar by self-boosting carbonization of phosphoric acid activated traditional Chinese medicine residues

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2556721B2 (en) * 1988-02-01 1996-11-20 大建工業株式会社 Method for producing modified wood
MY141254A (en) * 2003-01-24 2010-03-31 Handy Chemicals Ltd Sacrificial agents for fly ash concrete
MX2009007500A (en) * 2009-07-13 2011-01-25 Francisco Xavier Villasea Or Perez Verdia Biocarbon obtained from biomass or organic matter and uses thereof.
CN107021470A (en) * 2017-04-27 2017-08-08 农玉金 A kind of preparation method of composite biomass carbon material
CN114436394B (en) * 2020-10-30 2023-06-06 中国环境科学研究院 A composite treatment and restoration technology for polluted water and soil
CN112875699A (en) * 2021-02-07 2021-06-01 西安科技大学 Preparation method and application of special steel slag-based biomass activated carbon
CN115504760A (en) * 2022-11-04 2022-12-23 安徽海螺材料科技股份有限公司 A kind of early-strength magnesium phosphate cement repair material and preparation method thereof

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101058213A (en) * 2007-06-01 2007-10-24 济南大学 Method for preparing building material with carbonization maintenance waste
CN112774628A (en) * 2021-01-07 2021-05-11 昆明理工大学 Method for preparing biochar by self-boosting carbonization of phosphoric acid activated traditional Chinese medicine residues

Also Published As

Publication number Publication date
CN117285325A (en) 2023-12-26

Similar Documents

Publication Publication Date Title
CN112707663B (en) A kind of preparation method of red mud core-shell structure fine aggregate
CN101215149B (en) Preparation method of low-temperature fired sludge glass ultra-light ceramsite
PT2247551E (en) Healing agent in cement-based materials and structures, and process for its preparation
CN110041035B (en) C30 high-impermeability concrete with low consumption of rubber materials and preparation method thereof
CN114988735B (en) Method for preparing phosphate-based geopolymer by using low-activity solid waste
CN112592156B (en) Foamed ceramic and preparation method and application thereof
CN115557716B (en) Full-solid waste pavement base layer cementing material and preparation method thereof
CN117285325B (en) A preparation process of highly water-resistant magnesium-phosphate cement-based material
CN117567091B (en) Mine water corrosion-resistant coal-based solid waste filling paste and preparation method thereof
CN114873938A (en) Method for preparing baking-free ceramsite from casting ash
CN118255557A (en) A preparation process of glass-ceramic aggregate concrete
KR101611441B1 (en) A Environmental-friendly Plastering additives Containing Natural Mineral Powder and Environmental-friendly Plastering Cement and Mortar Containing the Same
CN115784702B (en) Preparation method of carbon-negative gypsum-based biochar thermal insulation plaster mortar
CN116102048B (en) Method for preparing cement retarder by deeply removing phosphate impurities from phosphogypsum
CN108516741B (en) A kind of steel slag sand-straw ash compound mortar and preparation method thereof
CN112897915B (en) A kind of preparation method of core-shell structure high-alumina fly ash chloride ion-bonded pottery sand
KR101843816B1 (en) Hybrid Admixture Composition with Early Self-Healing Development Properties and Cement Binder Composition Using the same
CN107814535A (en) A kind of concrete with good ductility
CN107117839A (en) One kind polyaluminium chloride producing cement from fag end new technology
CN105197977A (en) Preparation method for developing beta type phosphor building gypsum by utilizing microwaves
CN110002898A (en) A kind of complex building plastering periodicity maintaining process
CN117550913B (en) A kind of lightweight solid waste porous aggregate and its preparation method and application
CN119241203B (en) A low-temperature high-fluidity magnesium phosphate cement-based material and its preparation method and application
CN118206321B (en) Low-resilience alkali-free quick-setting agent and preparation method thereof
CN113372070B (en) Self-compacting concrete for floor heating protective layer 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