CN115487862A - Low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst and preparation method and application thereof - Google Patents

Low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst and preparation method and application thereof Download PDF

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CN115487862A
CN115487862A CN202211189279.3A CN202211189279A CN115487862A CN 115487862 A CN115487862 A CN 115487862A CN 202211189279 A CN202211189279 A CN 202211189279A CN 115487862 A CN115487862 A CN 115487862A
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furnace slag
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姚璐
胡广
刘清才
杨剑
刘维燥
杨臣
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Chongqing University of Post and Telecommunications
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Abstract

The invention relates to a low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst as well as a preparation method and application thereof, belonging to the technical field of photocatalyst preparation. The invention discloses a low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst, which is mainly characterized in that nano cuprous oxide is loaded on a carrier of low-titanium blast furnace slag zeolite, has better photocatalytic performance and is mixed with pure cuprous oxide (Cu) 2 O) phase ratio, the low titanium blast furnace slag zeolite/cuprous oxide (Cu) of the invention 2 O) the visible light response capability and the photocatalytic degradation capability of the composite photocatalyst are obviously enhanced, the high-value utilization of the low-titanium blast furnace slag is realized, and a new way for utilizing the low-titanium blast furnace slag is developed.

Description

Low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst and preparation method and application thereof
Technical Field
The invention belongs to the technical field of photocatalyst preparation, and relates to a low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst as well as a preparation method and application thereof.
Background
The industrial wastewater discharge in China mainly comes from industries such as petrifaction, coal, papermaking, textile, pharmacy, metallurgy, food and the like, and has the characteristics of complex types, great harm, lasting effect, great treatment difficulty and the like. In particular, industrial wastewater contains a large amount of artificially synthesized organic pollutants, is difficult to convert and degrade into harmless substances in the nature, not only can act on human bodies through food chain enrichment and harm health, but also can pollute soil and underground water and is extremely difficult to restore. Therefore, toxic refractory organic pollutants in industrial wastewater are important links which are not negligible in water environment treatment.
The photocatalysis technology is a green advanced oxidation technology for deeply treating toxic and nondegradable organic pollutants in industrial wastewater, wherein TiO is compared with the traditional water treatment material 2 The photocatalytic material has the advantages of mild reaction conditions, thorough pollutant degradation and no secondary pollution, and has wide application prospects in the field of organic pollutant treatment. However, the development of the photocatalytic material with low price and excellent performance is an important direction for the development of the technology because the photocatalytic material has high production cost and seriously limits the development of the photocatalytic material in industrial application.
The titanium-containing blast furnace slag is used as main solid waste generated by smelting vanadium-titanium magnetite in a blast furnace, and is currently utilized in the forms of building materials, fertilizers, titanium dioxide and enriched titanium extraction. In the prior art, titanium-containing blast furnace slag with medium and high titanium content is mostly used as a raw material, so that a large amount of low-titanium blast furnace slag is stockpiled, land is occupied, and a series of secondary pollution is caused to the environment. While the main component SiO of the low-titanium blast furnace slag 2 、TiO 2 And Al 2 O 3 The total content reaches 50 percent, and is a good choice for synthesizing the photocatalytic material. Furthermore, cu 2 O has the characteristics of high photoresponse activity and good stability in the field of photocatalysis, but the nano Cu 2 O is difficult to recycle in the wastewater treatment process, and the fixation of O on zeolite can effectively solve the problem of nano Cu 2 The recycling of O. Therefore, the zeolite is synthesized by taking the low-titanium blast furnace slag as a raw material, so that the resource utilization of valuable elements such as Si, al and Ti can be realized, the cost of the composite photocatalytic material for wastewater treatment can be reduced, and the cost of the composite photocatalytic material for wastewater treatment can be reducedEffectively improves the added value of the low-titanium blast furnace slag product, and solves the problems of the treatment of the low-titanium blast furnace slag and the recycling of the nano Cu 2O.
Therefore, low titanium blast furnace slag zeolite and cuprous oxide (Cu) are required 2 O) to prepare the photocatalyst which is efficient and stable, meets the requirements of energy conservation and emission reduction and is suitable for circular economy.
Disclosure of Invention
In view of the above, an object of the present invention is to provide a low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst; the second purpose of the invention is to provide a preparation method of the low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst; the invention also aims to provide application of the low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst in catalyzing methyl orange degradation.
In order to achieve the purpose, the invention provides the following technical scheme:
1. the composite photocatalyst comprises a low-titanium blast furnace slag zeolite carrier and nano cuprous oxide loaded on the carrier.
Preferably, the low-titanium blast furnace slag zeolite carrier is prepared according to the following method:
(1) Adding the low-titanium blast furnace slag as a raw material into hydrochloric acid (HCl), stirring for 1-4 times, washing with water, drying, crushing and screening to obtain acid-leaching titanium slag with the particle size of 200 meshes;
(2) Mixing the acid-leached titanium slag with sodium hydroxide (NaOH), roasting at 500-700 ℃ for 2-4 h, fully cooling, crushing and screening to obtain alkali-fused titanium slag with the particle size of 200 meshes;
(3) The alkali fusion titanium slag, deionized water and sodium metaaluminate (NaAlO) 2 ) Mixing and stirring for 1-3 h, and carrying out hydrothermal reaction for 8h at the temperature of 80-100 ℃ to obtain the low-titanium blast furnace slag zeolite.
More preferably, in the step (1), the concentration of the hydrochloric acid is 2 to 5mol/L;
the mass volume ratio of the low-titanium blast furnace slag to the hydrochloric acid is 0.0625-0.125.
Further preferably, in the step (2), the mass ratio of the acid-leached titanium slag to the sodium hydroxide is 1.5.
Further preferably, in the step (3), the alkali-molten titanium slag is deionized water and sodium metaaluminate (NaAlO) 2 ) The mass-to-volume ratio of (A) is 5-7.
2. The preparation method of the composite photocatalyst comprises the following steps:
(1) Adding low-titanium blast furnace slag zeolite into soluble Cu-containing material 2+ Adding polyvinylpyrrolidone (PVP) into the salt solution after ultrasonic oscillation to mix uniformly, continuously dropwise adding a NaOH solution, and stirring for 30min to obtain a mixed solution;
(2) Placing the mixed solution in the step (1) in a constant-temperature water bath, heating at the constant temperature of 60 ℃ for 10-30 min, and then slowly dropwise adding glucose (C) 6 H 12 O 6 ) Stirring the solution for 30-60 min to obtain a brick red precipitate hydration mixture;
(3) Repeatedly cleaning the brick red precipitate hydration mixture in the step (2) by using deionized water and absolute ethyl alcohol, and drying at 40-60 ℃ for 12-24 h to obtain the low-titanium blast furnace slag zeolite/cuprous oxide (Cu) 2 O) the composite photocatalyst.
Preferably, in the step (1), the soluble Cu is contained 2+ Cu in solution of salt 2+ The concentration of (A) is 0.0025-0.01 mol/L;
the low-titanium blast furnace slag zeolite and the soluble Cu-containing zeolite 2+ Cu in solution of salt 2+ The mass ratio of (A) to (B) is 1.
Preferably, in the step (1), the concentration of the NaOH solution is 0.1-2 mol/L; the mass ratio of the low-titanium blast furnace slag zeolite to NaOH in the NaOH solution is (1) from 0.168 to 3.357,g;
the mass ratio of the low-titanium blast furnace slag zeolite to polyvinylpyrrolidone (PVP) is 1.699-1.398.
Preferably, in step (3), glucose (C) 6 H 12 O 6 ) The concentration of the solution is 0.05-2 mol/L; the low-titanium blast furnace slag zeolite and glucose (C) in the step (1) 6 H 12 O 6 ) The mass ratio of glucose in the solution is 1.
3. The composite photocatalyst is applied to catalyzing methyl orange degradation.
The invention has the beneficial effects that:
1. the invention discloses a low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst, which is mainly characterized in that nano cuprous oxide is loaded on a carrier of low-titanium blast furnace slag zeolite, has better photocatalytic performance and is mixed with pure cuprous oxide (Cu) 2 O) phase ratio, the low titanium blast furnace slag zeolite/cuprous oxide (Cu) of the invention 2 O) the visible light response capability and the photocatalytic degradation capability of the composite photocatalyst are obviously enhanced, the high-value utilization of the low-titanium blast furnace slag is realized, and a new way for utilizing the low-titanium blast furnace slag is developed.
2. The invention also discloses a preparation method of the low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst, and the preparation method is simple and convenient in preparation process, high in controllability, easy to popularize and remarkable in economic benefit. The invention mainly takes low-titanium blast furnace slag zeolite which is prepared by modifying low-titanium blast furnace slag obtained by smelting vanadium titano-magnetite as a raw material as a carrier and cuprous oxide (Cu) 2 O) load is mounted, and the device has the advantages of stable performance and low cost; meanwhile, the method realizes the full utilization of valuable chemical elements in the low-titanium blast furnace slag, reduces the negative influence on the environment, and has good social benefit.
Additional advantages, objects, and features of the invention will be set forth in part in the description which follows and in part will become apparent to those having ordinary skill in the art upon examination of the following or may be learned from practice of the invention. The objectives and other advantages of the invention may be realized and attained by the means of the instrumentalities and combinations particularly pointed out hereinafter.
Detailed Description
The embodiments of the present invention are described below with reference to specific embodiments, and other advantages and effects of the present invention will be easily understood by those skilled in the art from the disclosure of the present specification. The invention is capable of other and different embodiments and of being practiced or of being carried out in various ways, and its several details are capable of modification in various respects, all without departing from the spirit and scope of the present invention.
The compositions (mass percentages) of the raw material low-titanium blast furnace slag used in the following examples are shown in table 1 below.
Table 1 composition of the raw low titanium blast furnace slag used in the examples:
Figure BDA0003868699040000031
example 1
A low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst is prepared by the following steps:
(1) Preparing low-titanium blast furnace slag zeolite: adding the low-titanium blast furnace slag into an HCl solution with the concentration of 5mol/L (wherein the mass volume ratio of the low-titanium blast furnace slag to the HCl solution is 1; then mixing the titanium slag with NaOH according to the mass ratio of 1.5; then it is mixed with deionized water, naAlO in a mass to volume ratio of 6 2 Mixing, stirring for 3h, and carrying out hydrothermal reaction for 8h at 100 ℃ to obtain the low-titanium blast furnace slag zeolite.
(2) Adding 0.01mol/L CuSO into the obtained low-titanium blast furnace slag zeolite 4 In solution (wherein low titanium blast furnace slag zeolite and CuSO 4 Cu in (1) 2+ The mass ratio of the low-titanium blast furnace slag zeolite to the NaOH solution is 2.
(3) Then placing the obtained mixed solution in a constant temperature water bath kettle at 60 ℃ for heat preservation for 10min, and then slowly dropwise adding 0.18mol/L glucose (C) 6 H 12 O 6 ) Solution (low titanium blast furnace slag zeolite and glucose (C) 6 H 12 O 6 ) The mass ratio of glucose in the solution is 1)The hydrated mixture precipitated brick red.
(4) Repeatedly cleaning the brick red precipitate hydration mixture with deionized water and absolute ethyl alcohol, and drying at 60 ℃ for 12h to obtain the low-titanium blast furnace slag zeolite/cuprous oxide (Cu) 2 O) the composite photocatalyst.
50mg of the low titanium blast furnace slag zeolite/cuprous oxide (Cu) prepared as described above 2 O) adding the composite photocatalyst into 10mg/L methyl orange solution, and performing a visible light photocatalytic degradation methyl orange performance test, wherein the degradation rate can reach 65.06% when the test time is 120 min.
Example 2
A low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst is prepared by the following steps:
(1) Preparing low-titanium blast furnace slag zeolite: adding the low-titanium blast furnace slag into an HCl solution with the concentration of 2mol/L (wherein the mass volume ratio of the low-titanium blast furnace slag to the HCl solution is 1; then mixing the titanium slag with NaOH according to the mass ratio of 1.5; it was then mixed with deionized water, naAlO in a mass to volume ratio of 7 2 Mixing, stirring for 1h, and carrying out hydrothermal reaction for 8h at 100 ℃ to obtain the low-titanium blast furnace slag zeolite.
(2) Adding 0.005mol/L CuSO into the obtained low-titanium blast furnace slag zeolite 4 In solution (wherein low titanium blast furnace slag zeolite and CuSO 4 Cu in (1) 2+ The mass ratio of (1).
(3) Then placing the obtained mixed solution in a constant temperature water bath kettle at 60 ℃ for heat preservation for 10min, and then slowly dropwise adding 0.05mol/L glucose (C) 6 H 12 O 6 ) Solution (low titanium blast furnace slag zeolite and glucose (C) 6 H 12 O 6 ) The mass ratio of glucose in the solution was 1.378) and stirred for 50min to obtain a brick-red precipitate hydration mixture.
(4) Repeatedly washing the brick red precipitate hydration mixture with deionized water and anhydrous ethanol, and drying at 40 deg.C for 24 hr to obtain low-titanium blast furnace slag zeolite/cuprous oxide (Cu) 2 O) the composite photocatalyst.
50mg of the low titanium blast furnace slag zeolite/cuprous oxide (Cu) prepared in example 2 above was added 2 O) adding the composite photocatalyst into 10mg/L methyl orange solution, and performing a visible light photocatalytic degradation methyl orange performance test, wherein the degradation rate can reach 62.78% when the test time is 120 min.
Example 3
The preparation method of the low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst comprises the following steps:
(1) Preparing low-titanium blast furnace slag zeolite: adding the low-titanium blast furnace slag into an HCl solution with the concentration of 2.5mol/L (wherein the mass volume ratio of the low-titanium blast furnace slag to the HCl solution is 1; then mixing the titanium slag with NaOH according to the mass ratio of 1.5 to 2, roasting for 4 hours at 500 ℃, fully cooling, crushing and sieving to obtain 200-mesh alkali fusion titanium slag; then, the mixture was mixed with deionized water, naAlO in a mass-to-volume ratio of 5 2 Mixing, stirring for 2h, and carrying out hydrothermal reaction for 24h at 80 ℃ to obtain the low-titanium blast furnace slag zeolite.
(2) Adding 0.0025mol/L CuSO into the obtained low-titanium blast furnace slag zeolite 4 In solution (wherein low titanium blast furnace slag zeolite and CuSO 4 The mass ratio of the low titanium blast furnace slag zeolite to the NaOH solution is 1.
(3) Then placing the obtained mixed solution in a constant temperature water bath kettle at 60 ℃ for heat preservation for 30min, and then slowly dropwise adding 2.0mol/L glucose (C) 6 H 12 O 6 ) Solution (low titanium blast furnace slag zeolite and glucose (C) 6 H 12 O 6 ) The mass ratio of glucose in the solution was 1.
(4) Repeatedly washing the brick red precipitate hydration mixture with deionized water and anhydrous ethanol, and drying at 60 deg.C for 12 hr to obtain low-titanium blast furnace slag zeolite/cuprous oxide (Cu) 2 O) the composite photocatalyst.
50mg of the above-prepared low titanium blast furnace slag zeolite/cuprous oxide (Cu) 2 O) adding the composite photocatalyst into 10mg/L methyl orange solution, and performing a visible light photocatalytic degradation methyl orange performance test, wherein the degradation rate can reach 59.62% when the test time is 120 min.
In conclusion, the invention discloses a low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst, which is mainly characterized in that nano cuprous oxide is loaded on a carrier of low-titanium blast furnace slag zeolite, has better photocatalytic performance and is combined with pure cuprous oxide (Cu) 2 O) phase ratio, the low titanium blast furnace slag zeolite/cuprous oxide (Cu) of the invention 2 O) the visible light response capability and the photocatalytic degradation capability of the composite photocatalyst are obviously enhanced, the high-value utilization of the low-titanium blast furnace slag is realized, and a new way for utilizing the low-titanium blast furnace slag is developed. The invention also discloses a preparation method of the low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst, and the preparation method is simple and convenient in preparation process, high in controllability, easy to popularize and remarkable in economic benefit. The invention mainly takes low-titanium blast furnace slag zeolite which is prepared by modifying low-titanium blast furnace slag obtained by smelting vanadium titano-magnetite as a raw material as a carrier and cuprous oxide (Cu) 2 O) load is mounted, so that the device has the advantages of stable performance and low cost; meanwhile, the method realizes the full utilization of valuable chemical elements in the low-titanium blast furnace slag, reduces the negative influence on the environment, and has good social benefit.
Finally, the above embodiments are only intended to illustrate the technical solutions of the present invention and not to limit the present invention, and although the present invention has been described in detail with reference to the preferred embodiments, it will be understood by those skilled in the art that modifications or equivalent substitutions may be made on the technical solutions of the present invention without departing from the spirit and scope of the technical solutions, and all of them should be covered by the claims of the present invention.

Claims (10)

1. The low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst is characterized by comprising a low-titanium blast furnace slag zeolite carrier and nano cuprous oxide loaded on the carrier.
2. The composite photocatalyst of claim 1, wherein the low-titanium blast furnace slag zeolite support is prepared by the following method:
(1) Adding the low-titanium blast furnace slag as a raw material into hydrochloric acid (HCl), stirring for 1-4 h, washing with water, drying, crushing and screening to obtain acid-leaching titanium slag with the particle size of 200 meshes;
(2) Mixing the acid-leaching titanium slag with sodium hydroxide (NaOH), roasting for 2-4 h at 500-700 ℃, fully cooling, crushing and screening to obtain alkali fusion titanium slag with the particle size of 200 meshes;
(3) The alkali fusion titanium slag, deionized water and sodium metaaluminate (NaAlO) 2 ) Mixing and stirring for 1-3 h, and carrying out hydrothermal reaction for 8-24 h at the temperature of 80-100 ℃ to obtain the low-titanium blast furnace slag zeolite.
3. The composite photocatalyst as claimed in claim 2, wherein in step (1), the concentration of the hydrochloric acid is 2-5 mol/L;
the mass volume ratio of the low-titanium blast furnace slag to the hydrochloric acid is 0.0625-0.125.
4. The composite photocatalyst as claimed in claim 2, wherein in step (2), the mass ratio of the acid-leached titanium slag to the sodium hydroxide is 1.5.
5. The composite photocatalyst as claimed in claim 2, wherein in step (3), the alkali-fused titanium slag, deionized water and sodium metaaluminate (NaAlO) 2 ) The mass volume ratio of (1) is 5-7.
6. A process for the preparation of a composite photocatalyst as claimed in any one of claims 1 to 5, which process comprises the steps of:
(1) Adding low-titanium blast furnace slag zeolite into soluble Cu-containing material 2+ Adding polyvinylpyrrolidone (PVP) into the salt solution after ultrasonic oscillation to mix uniformly, continuously dripping NaOH solution, and stirring for 30min to obtain a mixed solution;
(2) Placing the mixed solution in the step (1) in a constant-temperature water bath, heating at the constant temperature of 60 ℃ for 10-30 min, and then slowly dropwise adding glucose (C) 6 H 12 O 6 ) Stirring the solution for 30-60 min to obtain a brick red precipitate hydration mixture;
(3) Repeatedly cleaning the brick red precipitate hydration mixture in the step (2) by using deionized water and absolute ethyl alcohol, and drying at 40-60 ℃ for 12-24 h to obtain the low-titanium blast furnace slag zeolite/cuprous oxide (Cu) 2 O) the composite photocatalyst.
7. The method according to claim 6, wherein in the step (1), the soluble Cu is contained 2+ Cu in solution of salt 2+ The concentration of (A) is 0.0025-0.01 mol/L;
the low-titanium blast furnace slag zeolite and the soluble Cu-containing zeolite 2+ Cu in solution of salt 2+ The mass ratio of (1) to (0.2238) to (0.895).
8. The method according to claim 6, wherein in the step (1), the concentration of the NaOH solution is 0.1 to 2mol/L; the mass ratio of the low-titanium blast furnace slag zeolite to NaOH in the NaOH solution is 1.168-3.357,mol;
the mass ratio of the low-titanium blast furnace slag zeolite to polyvinylpyrrolidone (PVP) is 1.699-1.398.
9. The method according to claim 6, wherein in the step (3), glucose (C) 6 H 12 O 6 ) The concentration of the solution is 0.05-2 mol/L; the low titanium content in the step (1) is highSlag zeolite and glucose (C) 6 H 12 O 6 ) The mass ratio of glucose in the solution is 1.
10. The use of the composite photocatalyst of any one of claims 1 to 5 in catalyzing the degradation of methyl orange.
CN202211189279.3A 2022-09-28 2022-09-28 Low-titanium blast furnace slag zeolite/cuprous oxide composite photocatalyst and preparation method and application thereof Pending CN115487862A (en)

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Application publication date: 20221220