CN114873919A - TiO 2 Method for harmless and high-value utilization of reinforced stainless steel slag in large quantity - Google Patents

TiO 2 Method for harmless and high-value utilization of reinforced stainless steel slag in large quantity Download PDF

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CN114873919A
CN114873919A CN202210690605.2A CN202210690605A CN114873919A CN 114873919 A CN114873919 A CN 114873919A CN 202210690605 A CN202210690605 A CN 202210690605A CN 114873919 A CN114873919 A CN 114873919A
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stainless steel
steel slag
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tio
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CN114873919B (en
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佟志芳
谢肇勋
李英杰
王佳兴
许聪聪
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Jiangxi University of Science and Technology
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    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03CCHEMICAL COMPOSITION OF GLASSES, GLAZES OR VITREOUS ENAMELS; SURFACE TREATMENT OF GLASS; SURFACE TREATMENT OF FIBRES OR FILAMENTS MADE FROM GLASS, MINERALS OR SLAGS; JOINING GLASS TO GLASS OR OTHER MATERIALS
    • C03C10/00Devitrified glass ceramics, i.e. glass ceramics having a crystalline phase dispersed in a glassy phase and constituting at least 50% by weight of the total composition
    • C03C10/0063Devitrified glass ceramics, i.e. glass ceramics having a crystalline phase dispersed in a glassy phase and constituting at least 50% by weight of the total composition containing waste materials, e.g. slags
    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03BMANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
    • C03B19/00Other methods of shaping glass
    • C03B19/06Other methods of shaping glass by sintering, e.g. by cold isostatic pressing of powders and subsequent sintering, by hot pressing of powders, by sintering slurries or dispersions not undergoing a liquid phase reaction
    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03BMANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
    • C03B32/00Thermal after-treatment of glass products not provided for in groups C03B19/00, C03B25/00 - C03B31/00 or C03B37/00, e.g. crystallisation, eliminating gas inclusions or other impurities; Hot-pressing vitrified, non-porous, shaped glass products
    • C03B32/02Thermal crystallisation, e.g. for crystallising glass bodies into glass-ceramic articles
    • 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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Abstract

The invention relates to a TiO compound 2 A method for harmless and high-value utilization of reinforced stainless steel slag in large quantity. The invention prepares the basic glass by melting the stainless steel slag, the titanium dioxide and other raw materials, the basic glass is firstly subjected to nucleation heat treatment to obtain the nucleated glass, Cr in the basic glass can be promoted to form a large amount of fine nano-scale magnesium-chromium spinel crystal grains with low leaching rate in the nucleation heat treatment process by adjusting the content of titanium dioxide in the glass, the effect of strengthening and fixing chromium is achieved, and the nucleated glass is subjected to crystallization heat treatment to finally obtain the high-valued microcrystal ceramic. The invention has good harmless treatment effect and large treatment capacity on the stainless steel slag, and when TiO is used, the invention can be used for treating the stainless steel slag 2 At a content of 3.4 wt%, the acid resistance of the glass ceramics (20 wt% H) 2 SO 4 ) 99.95% and 99.96% of alkalinity resistance (20 wt% NaOH), water absorption0.01 percent, the compressive strength is 267.4MPa, and the Vickers hardness is 1211.8 HV.

Description

TiO 2 Method for harmless and high-value utilization of reinforced stainless steel slag in large quantity
Technical Field
The inventionRelates to a harmless treatment technology of metallurgical secondary resources, in particular to TiO 2 A method for harmless and high-value utilization of reinforced stainless steel slag in large quantity.
Background
Stainless steel is used as an important production material and is widely applied in the fields of metallurgy, building, traffic, food, medical treatment and the like. The national stainless steel crude steel yield is 3013.9 ten thousand tons in 2020, and the produced stainless steel slag exceeds 900 ten thousand tons. The chromium element in the stainless steel slag is often Cr 3+ And a small amount of Cr 6+ A state exists. Research shows that the stainless steel slag is piled up in natural environment for a long time, and Cr 3+ Can be oxidized into Cr 6+ ,Cr 6+ Has high toxicity, is easily dissolved in water, and can permeate into the environment to cause harm to the environment and human body. Therefore, the stainless steel slag piled in large quantity severely restricts the production of the stainless steel industry, and whether the stainless steel slag can be harmlessly treated becomes the bottleneck of sustainable development of the stainless steel manufacturing industry. At present, the harmless and high-value utilization of a large amount of stainless steel slag becomes an important problem which is urgently needed to be solved by the industry.
The microcrystal ceramic is a polycrystal solid material containing a large number of microcrystal phases and glass phases, which is prepared by carrying out nucleation and crystallization on base glass with a specific composition in a heating process. Compared with common glass, the microcrystal ceramic has the advantages of high mechanical strength, good wear resistance, stable chemical property and the like, so that the microcrystal ceramic is widely applied to a plurality of fields of buildings, chemical engineering, medical treatment and the like. Because the main chemical components of the stainless steel slag are similar to those of microcrystalline ceramics, and the chromium oxide in the slag can be used as a main nucleating agent for preparing the microcrystalline ceramics, the chromium in the slag can be solidified by using the stainless steel slag to prepare the microcrystalline ceramics, and the method is an effective way for realizing harmless and high-value utilization of the stainless steel slag.
The traditional stainless steel slag is most harmlessly cured by a curing method. The cement solidification method is that the stainless steel slag and other solid waste are mixed and added with cement to be wrapped by the cement. The method has the advantages of large treatment capacity of the stainless steel slag and convenient operation, wherein the defect is that the solidification degree of Cr is not high enough. The invention discloses a method for harmless treatment of stainless steel slag by molten blast furnace slag at high temperature (patent No. 201611053294X), which comprises the steps of adding the stainless steel slag into the molten blast furnace slag, heating by electrifying, stirring, and quenching by water to obtain mixed slag vitreous body, so that heavy metal Cr is fixed in the mixed slag vitreous body. When the addition amount of the stainless steel slag is 40 wt%, the leaching concentration of Cr in glassy slag is 0.03mg/L, and the slag has a certain Cr solidification effect, but the obtained product has low additional value and cannot be directly used as a building material.
The article published by the smooth property of Euro Yang and the like "preparation of microcrystalline glass by using stainless steel slag: crystal structure and solidification of heavy metal chromium "(" scientific report ", 2019,9(1): 1-9): [ Preparation of Glass-ceramic Using Chromium-containing stainless Steel slab [ Scientific Reports, 2019,9(1):1-9) ] discloses that the Glass-ceramic prepared by Using 0-20 wt% of stainless steel slag has a compressive strength of 222.9MPa and a Vickers hardness of 729.27 HV. The utilization rate of the stainless steel slag in the article is only about 20 percent, and the mechanical property of the prepared microcrystalline glass is not high enough.
Disclosure of Invention
The invention aims to provide TiO 2 A method for harmless and high-value utilization of reinforced stainless steel slag in large quantity. Stainless steel slag, titanium dioxide and other raw materials are melted to prepare base glass, the base glass is firstly subjected to nucleation heat treatment, and the added titanium dioxide (titanium dioxide) can promote Cr in the base glass to form nano magnesium-chromium spinel crystal grains with low leaching rate in the nucleation heat treatment process, so that the nucleated glass is obtained, and the purpose of primarily strengthening and fixing chromium is realized (as shown in figure 1); then carrying out crystallization heat treatment on the nucleated glass, taking the nano-scale magnesium chromium spinel crystal grains as heterogeneous nuclei to induce and separate out diopside crystal phases (as shown in figure 2), wherein Cr in the nano-scale magnesium chromium spinel crystal grains is diffused into diopside, and meanwhile, Cr in the glass phase is gradually diffused into diopside crystal lattices along with the generation of the diopside, so that more Cr is solidified, and further, the strengthening and the solidifying of the Cr are achieved, and the harmless effect of the stainless steel slag is greatly improved. With the addition of a proper amount of titanium dioxide, the number of nano-scale magnesia-chrome spinel crystal grains can be obviously increased, and a large amount of fine nano-scale magnesia-chrome spinel crystal grains are taken as heterogeneous cores in the crystallization heat treatment processInducing to separate out a large amount of fine diopside crystals, greatly improving the compressive strength of the glass ceramic and further realizing the high-value utilization of the stainless steel slag. Therefore, the stainless steel slag is used for preparing the microcrystalline ceramic by adjusting TiO 2 The addition amount can solve the difficult problems of harmless and high-value utilization of large amount of stainless steel slag.
The technical scheme of the invention is as follows:
TiO 2 2 The method for harmless and high-value utilization of large amount of reinforced stainless steel slag comprises the following steps:
(1) crushing the raw materials, drying and screening;
(2) putting the raw materials sieved in the step (1) into a ball mill for ball milling and mixing uniformly, and mixing TiO in the raw materials 2 The content of (A) is 1-6 wt%;
(3) putting the mixed raw materials subjected to ball milling in the step (2) into an alumina crucible, placing the alumina crucible into a tube furnace, heating to 1450-1650 ℃, preserving heat for 0.5-1.5 h to obtain a molten glass solution, and simultaneously placing a stainless steel mold into a muffle furnace to heat to 550 ℃;
(4) taking out the stainless steel mold from the muffle furnace, pouring the molten glass solution obtained in the step (3) into the stainless steel mold, putting the stainless steel mold into the muffle furnace again, keeping the temperature at 550 ℃ for 0.5-1.5 h for annealing, and cooling along with the furnace to obtain base glass;
(5) respectively carrying out nucleation heat treatment and crystallization heat treatment on the base glass obtained in the step (4) in an isothermal gradient furnace, obtaining nucleation glass after the nucleation heat treatment, and finally obtaining microcrystalline ceramics after the crystallization heat treatment on the nucleation glass;
the raw materials in the step (1) comprise 50-70 wt% of stainless steel slag, 10-30 wt% of fly ash, 5-15 wt% of quartz sand, 0-8 wt% of light magnesium oxide, 0-5 wt% of titanium dioxide, 0-4 wt% of industrial iron oxide and 0-3 wt% of soda ash.
The heating system of the tubular furnace in the step (3) is that the temperature is increased from room temperature to 1000 ℃ at the heating rate of 10 ℃/min, then the temperature is increased from 1000 ℃ to 1300 ℃ at the heating rate of 7 ℃/min, and then the temperature is increased from 1300 ℃ to 1450-1650 ℃ at the heating rate of 5 ℃/min.
The nucleation heat treatment system of the base glass in the step (5) is heat preservation for 1.5-2.5 h at 670-780 ℃, and the crystallization heat treatment system of the nucleation glass is heat preservation for 2-3 h at 830-900 ℃.
TiO in the mixed raw material of the step (2) 2 The content is preferably 3.4 wt%.
The raw material in step (1) was dried at 100 ℃ for 24 hours and sieved through a 200 mesh sieve.
The ball milling time in the step (2) is 3 hours.
The invention has the beneficial effects that:
(1) the invention has good harmless treatment effect on stainless steel slag by adjusting TiO 2 The content of the chromium spinel in the stainless steel slag promotes the heavy metal element Cr to be present in the chromium spinel lattice at the nucleation stage of the microcrystalline ceramic, and the crystallized spinel is wrapped and fused by diopside crystals, so that the solidification degree of the Cr is further improved. When TiO is present 2 At a content of 3.4 wt%, 97.4 wt% of Cr in the stainless steel slag was present in diopside crystals of the microcrystalline ceramic, and the Cr leaching concentration was only 0.009 mg/L.
(2) The invention has large treatment capacity on the stainless steel slag, the utilization rate of the stainless steel slag reaches more than 60 wt%, the use amount of the stainless steel slag is greatly increased (by 40%), and the harmless effect of the bulk quantity of the invention is far better than that of the prior art.
(3) The invention strengthens the harmless treatment of the stainless steel slag in large quantity, and simultaneously the obtained product microcrystalline ceramic has better chemical stability and mechanical property, thereby realizing the high-value utilization of solid wastes. When TiO is present 2 At a content of 3.4 wt%, the acid resistance of the glass ceramics (20 wt% H) 2 SO 4 ) 99.95 percent, the alkali resistance (20wt percent NaOH) is 99.96 percent, the water absorption is 0.01 percent, the compressive strength is 267.4MPa, the Vickers hardness is 1211.8HV, which is far higher than that of the prior art.
Drawings
FIG. 1 is a SEM image (a) and XRD pattern (b) of a nucleated glass of the present invention;
FIG. 2 is an SEM image (a) and an XRD pattern (b) of a crystallized glass (microcrystalline ceramic) according to the present invention;
FIG. 3 shows the results of testing the compressive strength and Vickers hardness of microcrystalline ceramics according to examples T1-T5 of the present invention.
Detailed Description
The invention prepares the microcrystalline ceramic by using the stainless steel slag and adjusts TiO 2 The addition amount of the chromium-free slag additive enables more Cr in the slag to migrate and be added into diopside crystals in the microcrystalline ceramic, so that the effects of strengthening solid chromium and reducing the leaching amount of Cr are achieved, meanwhile, the high-strength microcrystalline ceramic is obtained, and technical support is provided for realizing the harmless and high-value utilization of large amount of stainless steel slag.
The following 5 examples were selected from 120 experiments.
Example 1(T1)
60 wt% of stainless steel slag, 20 wt% of fly ash, 10 wt% of quartz sand, 0 wt% of titanium dioxide, 6 wt% of light magnesium oxide, 2 wt% of industrial iron oxide and 2 wt% of soda ash are crushed, dried at 100 ℃ for 24 hours and sieved by a 200-mesh sieve. Ball milling for 3 hr to mix the material homogeneously. The mixture contains CaO25.1wt%, MgO 12.5 wt% and Al 2 O 3 10wt%、SiO 2 45wt%、Cr 2 O 3 1.3wt%、Fe 2 O 3 2.9wt%、TiO 2 1.4wt%、Na 2 O 1.6wt%、K 2 O 0.1wt%;
The mixture obtained was placed in a 200ml alumina crucible and heated from room temperature to 1000 ℃ in a tube furnace at a heating rate of 10 ℃/min, from 1000 ℃ to 1300 ℃ at a heating rate of 7 ℃/min, from 1300 ℃ to 1550 ℃ at a heating rate of 5 ℃/min and held at 1550 ℃ for 1 h. Simultaneously, placing the stainless steel mold into a muffle furnace to be heated to 550 ℃;
and pouring the molten glass into a mold for annealing, keeping the temperature for 1h, and cooling along with the furnace to obtain the base glass. And carrying out nucleation heat treatment on the obtained base glass in an isothermal gradient furnace under the condition of keeping the temperature of 730 ℃ for 2h to obtain the nucleated glass. Carrying out crystallization heat treatment on the obtained nucleated glass in an isothermal gradient furnace under the condition of keeping the temperature of 860 ℃ for 2.5 hours to prepare microcrystalline ceramic;
carrying out Cr element XPS detection on the prepared microcrystalline ceramic, taking XPS electron binding energy spectrums of chromium ions in magnesium-chromium spinel and base glass as reference, and fitting peak separation on the detection resultAs a result, 93.13 wt% of Cr was present in the crystal lattice of diopside. The results of the Cr leaching test and the chemical stability test on the microcrystalline ceramics are shown in Table 1, the leaching concentration of Cr in the microcrystalline ceramics is 0.018mg/L, and the acid resistance (20 wt% H) 2 SO 4 ) 99.84 percent, the alkalinity resistance (20wt percent NaOH) 99.81 percent and the water absorption rate 0.07 percent. The mechanical property test of the microcrystalline ceramic shows that the compressive strength of the microcrystalline ceramic is 248MPa and the Vickers hardness is 1082.5HV as shown in figure 3.
Example 2(T2)
60 wt% of stainless steel slag, 19 wt% of fly ash, 10 wt% of quartz sand, 1 wt% of titanium dioxide, 6 wt% of light magnesium oxide, 2 wt% of industrial iron oxide and 2 wt% of soda ash are crushed, dried at 100 ℃ for 24 hours and sieved by a 200-mesh sieve. Ball milling for 3 hr to mix the material homogeneously. The mixture contains 25.1 wt% of CaO, 12.5 wt% of MgO and Al by analysis 2 O 3 9.7wt%、SiO 2 44.5wt%、Cr 2 O 3 1.3wt%、Fe 2 O 3 2.9wt%、TiO 2 2.4wt%、Na 2 O 1.6wt%、K 2 O 0.1wt%;
The mixture obtained was placed in a 200ml alumina crucible and heated from room temperature to 1000 ℃ in a tube furnace at a heating rate of 10 ℃/min, from 1000 ℃ to 1300 ℃ at a heating rate of 7 ℃/min, from 1300 ℃ to 1550 ℃ at a heating rate of 5 ℃/min and held at 1550 ℃ for 1 h. Simultaneously, placing the stainless steel mold into a muffle furnace to be heated to 550 ℃;
and pouring the molten glass into a mold for annealing, keeping the temperature for 1h, and cooling along with the furnace to obtain the base glass. And carrying out nucleation heat treatment on the obtained base glass in an isothermal gradient furnace under the condition of keeping the temperature of 730 ℃ for 2h to obtain the nucleated glass. Carrying out crystallization heat treatment on the obtained nucleated glass in an isothermal gradient furnace under the condition of keeping the temperature of 860 ℃ for 2.5 hours to prepare microcrystalline ceramic;
the prepared microcrystalline glass is subjected to Cr element XPS detection, XPS electron binding energy spectrums of chromium ions in the magnesium-chromium spinel and the base glass are taken as references, the detection result is subjected to peak splitting, and 95.15 wt% of Cr is added in crystal lattices of the diopside crystal. Cr treatment of microcrystalline ceramicsThe results of the leaching test and the chemical stability test are shown in Table 1, the leaching concentration of the microcrystalline ceramic Cr is 0.013mg/L, and the acid resistance is (20 wt% H) 2 SO 4 ) 99.90%, the alkali resistance (20 wt% NaOH) 99.91%, and the water absorption 0.03%. The mechanical property test of the microcrystalline ceramic shows that the compressive strength of the microcrystalline ceramic is 255.3MPa and the Vickers hardness is 1132.5HV as shown in figure 3.
Example 3(T3)
60 wt% of stainless steel slag, 19 wt% of fly ash, 9 wt% of quartz sand, 2 wt% of titanium dioxide, 6 wt% of light magnesium oxide, 2 wt% of industrial iron oxide and 2 wt% of soda ash are crushed, dried at 100 ℃ for 24 hours and sieved by a 200-mesh sieve. Ball milling for 3h by using a ball mill to uniformly mix the raw materials; the mixed raw material was analyzed to contain 25.1 wt% of CaO, 12.5 wt% of MgO, and Al 2 O 3 9.7wt%、SiO 2 43.4wt%、Cr 2 O 3 1.3wt%、Fe 2 O 3 2.9wt%、TiO 2 3.4wt%、Na 2 O 1.6wt%、K 2 O 0.1wt%;
The obtained mixed raw materials are put into a 200ml alumina crucible and are placed in a tubular furnace to be heated from room temperature to 1000 ℃ at the heating rate of 10 ℃/min, from 1000 ℃ to 1300 ℃ at the heating rate of 7 ℃/min, from 1300 ℃ to 1550 ℃ at the heating rate of 5 ℃/min, and the temperature is kept for 1h at 1550 ℃. Simultaneously putting the stainless steel mould into a muffle furnace and heating to 550 ℃;
pouring the melted glass into a stainless steel mold for annealing, preserving heat for 1h, and then cooling along with the furnace to obtain base glass; carrying out nucleation heat treatment on the obtained base glass in an isothermal gradient furnace under the condition of keeping the temperature of 730 ℃ for 2h to prepare nucleated glass; carrying out crystallization heat treatment on the obtained nucleated glass in an isothermal gradient furnace under the condition of keeping the temperature of 860 ℃ for 2.5 hours to prepare microcrystalline ceramic;
carrying out Cr element XPS detection on the prepared microcrystalline ceramic, taking XPS electron binding energy spectrums of chromium ions in the magnesium-chromium spinel and the base glass as references, and fitting and splitting peaks on detection results to obtain 97.4 wt% of Cr which is added in a diopside crystal lattice; the results of Cr leaching test and chemical stability test on the microcrystalline ceramics are shown in Table 1, and the Cr leaching concentration of the microcrystalline ceramics is shown in Table 1Degree of 0.009mg/L, acid resistance (20 wt% H) 2 SO 4 ) 99.95 percent, the alkalinity resistance (20wt percent NaOH) is 99.88 percent, and the water absorption is 0.02 percent; the mechanical property test of the microcrystalline ceramic shows that the compressive strength of the microcrystalline ceramic is 267.4MPa and the Vickers hardness is 1211.8HV as shown in figure 3.
Example 4(T4)
Crushing 60 wt% of stainless steel slag, 18 wt% of fly ash, 9 wt% of quartz sand, 3 wt% of titanium dioxide, 6 wt% of light magnesium oxide, 2 wt% of industrial iron oxide and 2 wt% of soda ash, drying for 24 hours at 100 ℃, and sieving by a 200-mesh sieve; ball milling for 3h by using a ball mill to uniformly mix the raw materials; the mixture contains 25 wt% of CaO, 12.5 wt% of MgO and Al by analysis 2 O 3 9.3wt%、SiO 2 42.9wt%、Cr 2 O 3 1.3wt%、Fe 2 O 3 2.9wt%、TiO 2 4.4wt%、Na 2 O 1.6wt%、K 2 O 0.1wt%;
Putting the obtained mixture into a 200ml alumina crucible, heating the mixture in a tubular furnace from room temperature to 1000 ℃ at a heating rate of 10 ℃/min, heating the mixture from 1000 ℃ to 1300 ℃ at a heating rate of 7 ℃/min, heating the mixture from 1300 ℃ to 1550 ℃ at a heating rate of 5 ℃/min, and preserving heat for 1h at 1550 ℃ to obtain molten glass; simultaneously, placing the stainless steel mold into a muffle furnace to be heated to 550 ℃;
pouring the melted glass into a stainless steel mold for annealing, preserving heat at 550 ℃ for 1h, and then cooling with a furnace to obtain base glass; carrying out nucleation heat treatment on the obtained base glass in an isothermal gradient furnace under the condition of keeping the temperature of 730 ℃ for 2h to prepare nucleated glass; carrying out crystallization heat treatment on the obtained nucleated glass in an isothermal gradient furnace under the condition of keeping the temperature of 860 ℃ for 2.5 hours to prepare microcrystalline ceramic;
the prepared microcrystalline ceramic is subjected to Cr element XPS detection, XPS electron binding spectra of chromium ions in magnesium-chromium spinel and base glass are taken as references, and peaks are fitted to detection results to obtain the microcrystalline ceramic, wherein 96.15 wt% of Cr is added in crystal lattices of diopside crystals. The results of Cr leaching test and chemical stability test on the microcrystalline ceramics are shown in Table 1, the Cr leaching concentration of the microcrystalline ceramics is 0.011mg/L, and the acid resistance (20 wt% H) is 2 SO 4 ) 99.92%, the alkali resistance (20 wt% NaOH) 99.92%, and the water absorption 0.01%. The mechanical property test of the microcrystalline ceramic shows that the compressive strength of the microcrystalline ceramic is 258.6MPa and the Vickers hardness is 1182.6HV as shown in figure 3.
Example 5(T5)
60 wt% of stainless steel slag, 18 wt% of fly ash, 8 wt% of quartz sand, 4 wt% of titanium dioxide, 6 wt% of light magnesium oxide, 2 wt% of industrial iron oxide and 2 wt% of soda ash are crushed, dried at 100 ℃ for 24 hours and sieved by a 200-mesh sieve. Ball milling for 3 hr to mix the material homogeneously. The mixture contains 25 wt% of CaO, 12.5 wt% of MgO and Al 2 O 3 9.3wt%、SiO 2 41.9wt%、Cr 2 O 3 1.3wt%、Fe 2 O 3 2.9wt%、TiO 2 5.4wt%、Na 2 O 1.6wt%、K 2 O 0.1wt%;
The mixture obtained is placed in a 200ml alumina crucible and heated in a tube furnace from room temperature to 1000 ℃ at a heating rate of 10 ℃/min, from 1000 ℃ to 1300 ℃ at a heating rate of 7 ℃/min, from 1300 ℃ to 1550 ℃ at a heating rate of 5 ℃/min and held at 1550 ℃ for 1 h. Simultaneously, placing the stainless steel mold into a muffle furnace to be heated to 550 ℃;
and pouring the molten glass into a mold for annealing, keeping the temperature for 1h, and cooling along with the furnace to obtain the base glass. And carrying out nucleation heat treatment on the obtained base glass in an isothermal gradient furnace under the condition of keeping the temperature of 730 ℃ for 2h to obtain the nucleated glass. Carrying out crystallization heat treatment on the obtained nucleated glass in an isothermal gradient furnace under the condition of keeping the temperature of 860 ℃ for 2.5 hours to prepare microcrystalline ceramic;
the prepared microcrystalline ceramic is subjected to Cr element XPS detection, XPS electron binding energy spectrums of chromium ions in magnesium-chromium spinel and base glass are taken as references, and peaks are fitted to detection results to obtain the microcrystalline ceramic, wherein 95.33 wt% of Cr is added in crystal lattices of diopside crystals. The results of Cr leaching test and chemical stability test on the microcrystalline ceramics are shown in Table 1, the Cr leaching concentration of the microcrystalline ceramics is 0.011mg/L, and the acid resistance (20 wt% H) is 2 SO 4 ) 99.87%, the alkali resistance (20 wt% NaOH) 99.88%, and the water absorption rate0.04 percent. The mechanical property test of the microcrystalline ceramic shows that the compressive strength of the microcrystalline ceramic is 249.1MPa and the Vickers hardness is 1093.4HV as shown in figure 3.
TABLE 1 Cr leaching, acid and alkali resistance and water absorption detection of the microcrystalline ceramic prepared by the invention
Examples Cr Leaching concentration (mg/L) Acid resistance (%) Alkali resistance (%) Water absorption (%)
1 0.018 99.84 99.81 0.07
2 0.013 99.90 99.91 0.03
3 0.009 99.95 99.96 0.01
4 0.011 99.92 99.92 0.01
5 0.011 99.87 99.88 0.04
The mechanical properties of the microcrystalline ceramic prepared by the present invention were compared with those of microcrystalline glass prepared by eudipleura and the like, and the results are shown in table 2.
TABLE 2 comparison of mechanical properties of the microcrystalline ceramics prepared according to the present invention and the microcrystalline glass prepared by Ouyanghou et al
Examples Strength (MPa) Vickers Hardness (HV)
1 248 1082.5
2 255.3 1132.5
3 267.4 1211.8
4 258.6 1182.6
5 249.1 1093.4
Europe and Yang are smoothly 222.9 729.27

Claims (6)

1. TiO 2 2 The method for harmless and high-value utilization of large amount of reinforced stainless steel slag is characterized by comprising the following steps:
(1) crushing the raw materials, drying and screening;
(2) putting the raw materials sieved in the step (1) into a ball mill for ball milling and mixing uniformly, and mixing TiO in the raw materials 2 The content of (A) is 1-6 wt%;
(3) putting the mixed raw materials subjected to ball milling in the step (2) into an alumina crucible, placing the alumina crucible into a tube furnace, heating to 1450-1650 ℃, preserving heat for 0.5-1.5 h to obtain a molten glass solution, and simultaneously placing a stainless steel mold into a muffle furnace to heat to 550 ℃;
(4) taking out the stainless steel mold from the muffle furnace, pouring the molten glass solution obtained in the step (3) into the stainless steel mold, putting the stainless steel mold into the muffle furnace again, keeping the temperature at 550 ℃ for 0.5-1.5 h for annealing, and cooling along with the furnace to obtain base glass;
(5) respectively carrying out nucleation heat treatment and crystallization heat treatment on the base glass obtained in the step (4) in an isothermal gradient furnace, obtaining nucleation glass after the nucleation heat treatment, and finally obtaining microcrystalline ceramics after the crystallization heat treatment on the nucleation glass;
the raw materials in the step (1) comprise 50-70 wt% of stainless steel slag, 10-30 wt% of fly ash, 5-15 wt% of quartz sand, 0-8 wt% of light magnesium oxide, 0-5 wt% of titanium dioxide, 0-4 wt% of industrial iron oxide and 0-3 wt% of soda ash.
2. A TiO according to claim 1 2 The method for harmless and high-value utilization of large amount of reinforced stainless steel slag is characterized by comprising the following steps: and (3) heating the tubular furnace from room temperature to 1000 ℃ at a heating rate of 10 ℃/min, then from 1000 ℃ to 1300 ℃ at a heating rate of 7 ℃/min, and then from 1300 ℃ to 1450-1650 ℃ at a heating rate of 5 ℃/min.
3. A TiO according to claim 1 2 The method for harmless and high-value utilization of large amount of reinforced stainless steel slag is characterized by comprising the following steps: the nucleation heat treatment system of the base glass in the step (5) is heat preservation for 1.5-2.5 h at 670-780 ℃, and the crystallization heat treatment system of the nucleation glass is heat preservation for 2-3 h at 830-900 ℃.
4. A TiO according to claim 1 2 The method for harmless and high-value utilization of large amount of reinforced stainless steel slag is characterized by comprising the following steps: TiO in the mixed raw material of the step (2) 2 The content is preferably 3.4 wt%.
5. A TiO according to claim 1 2 The method for harmless and high-value utilization of large amount of reinforced stainless steel slag is characterized by comprising the following steps: the raw material in step (1) was dried at 100 ℃ for 24 hours and sieved through a 200 mesh sieve.
6. A TiO according to claim 1 2 The method for harmless and high-value utilization of large amount of reinforced stainless steel slag is characterized by comprising the following steps: the ball milling time in the step (2) is 3 hours.
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Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102211874A (en) * 2011-05-10 2011-10-12 北京科技大学 Microcrystalline glass and preparation method thereof
CN105347684A (en) * 2015-11-26 2016-02-24 上海宝田新型建材有限公司 Blast-furnace-slag glass ceramics and preparation method therefor
CN106082679A (en) * 2016-06-15 2016-11-09 北京科技大学 A kind of method that full waste material short route prepares devitrified glass

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102211874A (en) * 2011-05-10 2011-10-12 北京科技大学 Microcrystalline glass and preparation method thereof
CN105347684A (en) * 2015-11-26 2016-02-24 上海宝田新型建材有限公司 Blast-furnace-slag glass ceramics and preparation method therefor
CN106082679A (en) * 2016-06-15 2016-11-09 北京科技大学 A kind of method that full waste material short route prepares devitrified glass

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
云飞: "不锈钢渣玻璃陶瓷的制备及热处理制度优化", 《中国优秀硕士学位论文全文数据库工程科技Ⅰ辑》 *
杨健: "含铬钢渣制备微晶玻璃及一步热处理研究", 《中国博士学位论文全文数据库 工程科技I辑》 *

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