CN112206790A - Preparation method and application of modified pyrite with photocatalytic performance - Google Patents

Preparation method and application of modified pyrite with photocatalytic performance Download PDF

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CN112206790A
CN112206790A CN202011261786.4A CN202011261786A CN112206790A CN 112206790 A CN112206790 A CN 112206790A CN 202011261786 A CN202011261786 A CN 202011261786A CN 112206790 A CN112206790 A CN 112206790A
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pyrite
silane
powder
adhesive tape
drying
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CN112206790B (en
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李�雨
严滨
叶茜
黄茵茵
曾孟祥
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Xiamen University of Technology
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/02Sulfur, selenium or tellurium; Compounds thereof
    • B01J27/04Sulfides
    • B01J27/043Sulfides with iron group metals or platinum group metals
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/02Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides
    • B01J31/0272Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides containing elements other than those covered by B01J31/0201 - B01J31/0255
    • B01J31/0274Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides containing elements other than those covered by B01J31/0201 - B01J31/0255 containing silicon
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/70Treatment of water, waste water, or sewage by reduction
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/163Nitrates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • C02F2101/22Chromium or chromium compounds, e.g. chromates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/36Organic compounds containing halogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
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Abstract

The invention belongs to the technical field of sewage treatment, and particularly relates to a preparation method and application of modified pyrite powder with photocatalytic performance. The method comprises the steps of bonding pyrite powder on the bonding surface of an adhesive tape, placing the adhesive tape in silane hydrolysate for reaction, taking out, cleaning, drying and removing the adhesive tape to obtain silane-treated pyrite; and reacting the silane-treated pyrite with an anthraquinone compound, filtering out solids, cleaning and drying to obtain the modified pyrite powder with photocatalytic performance. The modified pyrite with photocatalytic performance can effectively degrade heavy metal ions and promote the degradation rate of microorganisms on nitrate, azo dyes and the like, and has a good application prospect.

Description

Preparation method and application of modified pyrite with photocatalytic performance
Technical Field
The invention belongs to the technical field of sewage treatment, and relates to a preparation method and application of modified pyrite with photocatalytic performance.
Background
Sewage, including industrial wastewater, domestic sewage, etc., has become one of the important pollutants that destroy the environment and affect human health. Pyrite, because of its photocatalytic activity, has been used in the treatment of some effluents to remove some organic pollutants or heavy metal ions.
Anthraquinone compounds have been reported to be used for the microbial degradation of sewage containing nitrate, azo dyes and the like, and can promote and increase the degradation rate of the nitrate and the azo dyes by the microorganisms.
Further increasing the degradation rate of nitrates, azo dyes, etc. remains the direction of industry efforts.
Disclosure of Invention
The invention aims to overcome the defects of the prior art and provide a preparation method of modified pyrite with photocatalytic performance.
Another object of the present invention is to provide the use of modified pyrite having photocatalytic properties.
The technical scheme of the invention is as follows:
the preparation method of the modified pyrite powder with photocatalytic performance comprises the following steps,
s1, bonding the pyrite powder to the bonding surface of the adhesive tape, placing the tape in silane hydrolysate for reaction for 0.5-5 hours, taking out, cleaning, drying, and removing the adhesive tape to obtain silane-treated pyrite;
s2, placing the silane-treated pyrite in the step S1 in an organic solvent, performing ultrasonic dispersion, adding an anthraquinone compound and an auxiliary agent, stirring and reacting for 1-5 hours at the temperature of 20-50 ℃, filtering out solids, cleaning and drying to obtain modified pyrite powder with photocatalytic performance.
In the application, the pyrite powder is bonded on the bonding surface of the adhesive tape, the pyrite powder can be directly bonded by the bonding surface of the adhesive tape, or the pyrite powder can be dispersed in a solvent to form a dispersion liquid, then the dispersion liquid is coated on a base material and is dried, and then the pyrite powder is bonded by the adhesive tape, and the method can be specifically carried out according to the following method: ultrasonically dispersing 1 weight part of pyrite powder in 100 weight parts of absolute ethyl alcohol, uniformly coating the powder on a glass substrate to form a thin layer, heating and drying, bonding the powder by using an adhesive tape, then placing the powder in the absolute ethyl alcohol or deionized water for ultrasonic treatment, and drying to bond the pyrite powder on the bonding surface of the adhesive tape.
In the present application, the step of removing the tape in step S1 is not particularly limited as long as the pyrite powder can be detached and collected from the tape, and the tape may be placed in an organic solvent such as tetrahydrofuran or acetone to collect the detached pyrite powder, filtered, cleaned, and dried, or the tape may be placed in an oven at 60 ℃ to be baked for 2 minutes, taken out, and scraped off.
In the present application, the organic solvent in step S2 may be absolute ethanol, tetrahydrofuran, ethyl acetate, butyl acetate, or the like.
In the present application, the reaction in step S2 may be a stirring reaction at a temperature of 20 to 50 ℃ for 1 to 5 hours.
Preferably, the average particle size of the pyrite powder in step S1 is 0.5 to 100 μm. More preferably, the pyrite powder has an average particle size of 2 to 50 μm, and still more preferably, an average particle size of 5 to 30 μm.
Preferably, the adhesive tape in step S1 is a single-sided adhesive tape or a double-sided adhesive tape. One surface of the single-sided tape is an adhesive surface, and the other surface of the tape has no adhesive ability. The double-sided adhesive tape is an adhesive tape with two surfaces being adhesive surfaces. The adhesive tape can be transparent adhesive tape, box sealing adhesive tape, insulating adhesive tape, double-sided adhesive tape, etc.
Preferably, the silane in step S1 is selected from epoxysilanes. More preferably, the epoxysilane is selected from one or more of 3- (2, 3-epoxypropoxy) propyltrimethoxysilane, 3- (2, 3-epoxypropoxy) propyltriethoxysilane, 3- (2, 3-epoxypropoxy) propylmethyldiethoxysilane, 3- (2, 3-epoxypropoxy) propylmethyldimethoxysilane, 2- (3, 4-epoxycyclohexyl) ethyltrimethoxysilane, 2- (3, 4-epoxycyclohexyl) ethyltriethoxysilane, 2- (3, 4-epoxycyclohexyl) ethylmethyldiethoxysilane and 2- (3, 4-epoxycyclohexyl) ethylmethyldimethoxysilane.
Preferably, the silane hydrolysate in step S1 is obtained by: adding 1 part by weight of epoxy silane into 30-100 parts by weight of a mixed solvent of anhydrous ethanol and water in a volume ratio of 80: 20-90: 10, adjusting the pH value to be acidic, and stirring for 0.5-5 hours to obtain a silane hydrolysate.
Preferably, the weight ratio of the silane-treated pyrite, the organic solvent and the anthraquinone compound in step S2 is 1: 10-100: 0.05-0.2.
Preferably, the anthraquinone compound in step S2 is selected from amino-containing anthraquinone compounds.
More preferably, the aminoanthraquinone-containing compound is at least one selected from the group consisting of 1-amino-2-bromo-4-hydroxyanthraquinone, 2-aminoanthraquinone 1, 2-diaminoanthraquinone, 1, 4-diaminoanthraquinone, 2, 6-diaminoanthraquinone, 1, 8-diaminoanthraquinone, 1, 5-diaminoanthraquinone, 1-amino-2-methylanthraquinone, 1, 5-dihydroxy-4, 8-diaminoanthraquinone and 1-aminoanthraquinone.
Preferably, the assistant in step S2 is an accelerator, and is one or more selected from 2-methylimidazole, 1-methylimidazole, 2-ethyl-4-methylimidazole, 2-phenylimidazole, 2-undecylimidazole and 2-phenyl-4-methylimidazole. More preferably, the weight of the auxiliary agent is 8-20% of the weight of the anthraquinone compound.
A modified pyrite having photocatalytic properties, prepared by the method of any one of the embodiments described above.
The application of the modified pyrite of the embodiment in sewage treatment. Preferably, the sewage contains at least one of nitrate and azo dyes.
The invention has the beneficial effects that: according to the invention, the pyrite powder is firstly bonded by the adhesive tape, so that when the pyrite powder reacts in the silane hydrolysate, the part of the surface which is not bonded by the adhesive tape reacts, and the part of the surface which is bonded by the adhesive tape does not react, therefore, the surface of the pyrite powder is half-coated by the silane. The part of the pyrite surface which is semi-coated by the silane continuously reacts with the anthraquinone compound, and the part which is not coated cannot react with the anthraquinone compound, so that a semi-coating structure of the anthraquinone compound on the pyrite powder is formed. The uncoated part of the pyrite powder body with the semi-coating structure can absorb ultraviolet light to generate photocatalytic activity, and the coated part can prevent the pyrite from absorbing the ultraviolet light due to the existence of the coating, so the modified pyrite powder body has photocatalytic performance, can generate degradation effect on heavy metal ions under the irradiation of the ultraviolet light, has obvious effect, and can promote the improvement of the microbial degradation rate of nitrate, azo dyes and the like under the irradiation of the ultraviolet light. Therefore, the modified pyrite with photocatalytic performance has better effects on the reduction treatment of heavy metals and the degradation of nitrate and azo dyes.
Detailed Description
The technical solution of the present invention is further illustrated and described by the following detailed description.
Unless otherwise specified, the parts in the following examples are parts by weight.
Preparation of silane hydrolysate
1 part of 3- (2, 3-glycidoxy) propyltriethoxysilane was added to 60 parts of a mixed solvent of anhydrous ethanol and water at a volume ratio of 90:10, the pH was adjusted to 4.5, and stirring was carried out for 2 hours to obtain silane hydrolysate 1.
1 part of 2- (3, 4-epoxycyclohexyl) ethyltriethoxysilane was added to 95 parts of a mixed solvent of anhydrous ethanol and water in a volume ratio of 85:15, the pH was adjusted to 4.0, and stirring was carried out for 1.5 hours to obtain silane hydrolysate 2.
Example 1
Directly bonding pyrite powder with the average particle size of 20 microns to the bonding surface of the adhesive tape by using a single-sided transparent adhesive tape, placing the single-sided transparent adhesive tape in the silane hydrolysate 1 for reaction for 2 hours, taking out, cleaning and drying the single-sided transparent adhesive tape, placing the single-sided transparent adhesive tape in tetrahydrofuran for soaking for 0.5 hour, filtering out solids, cleaning and drying the solids to obtain silane-treated pyrite 1;
placing 1 part of the silane-treated pyrite 1 in 50 parts of absolute ethyl alcohol, performing ultrasonic dispersion, adding 0.06 part of 1-aminoanthraquinone and 0.006 part of 1-methylimidazole, stirring and reacting at 30 ℃ for 3 hours, filtering out solids, cleaning and drying to obtain modified pyrite powder 1 with photocatalytic performance, namely P-1.
Example 2
Ultrasonically dispersing 1 part of pyrite powder with the average particle size of 15 mu m in 100 parts of absolute ethyl alcohol, uniformly coating the mixture on a glass substrate to form a thin layer, heating and drying the thin layer, bonding the powder by using a single-sided transparent adhesive tape, placing the single-sided transparent adhesive tape in the absolute ethyl alcohol, ultrasonically treating the mixture, and drying the mixture to bond the pyrite powder on the bonding surface of the adhesive tape; placing the adhesive tape bonded with the powder in the silane hydrolysate 2 for reacting for 3 hours, taking out, cleaning and drying the adhesive tape, placing the adhesive tape in acetone for soaking for 0.5 hour, filtering out solids, cleaning and drying the solids to obtain silane-treated pyrite 2;
placing 1 part of the silane-treated pyrite 2 in 70 parts of absolute ethyl alcohol, performing ultrasonic dispersion, adding 0.1 part of 2-aminoanthraquinone and 0.012 part of 2-methylimidazole, stirring and reacting at 30 ℃ for 3 hours, filtering out solids, cleaning and drying to obtain modified pyrite powder 2 with photocatalytic performance, and marking P-2.
Example 3
Ultrasonically dispersing 1 part of pyrite powder with the average particle size of 20 mu m in 90 parts of absolute ethyl alcohol, uniformly coating the mixture on a glass substrate to form a thin layer, heating and drying the thin layer, adhering the powder on two sides by using a double-sided adhesive tape, then placing the powder in deionized water for ultrasonic treatment, and drying to adhere the pyrite powder on the adhesive surface of the adhesive tape; placing the double-sided tape bonded with the powder in the silane hydrolysate 2 for reacting for 3.5 hours, taking out, cleaning and drying, placing in acetone for soaking for 0.5 hour, filtering out solids, cleaning and drying to obtain silane-treated pyrite 3;
placing 1 part of the silane-treated pyrite 3 in 90 parts of absolute ethyl alcohol, performing ultrasonic dispersion, adding 0.2 part of 2-aminoanthraquinone and 0.03 part of 2-methylimidazole, stirring and reacting at 25 ℃ for 2.5 hours, filtering out solids, cleaning and drying to obtain modified pyrite powder 3 with photocatalytic performance, and marking P-3.
Example 4
Ultrasonically dispersing 1 part of pyrite powder with the average particle size of 30 mu m in 100 parts of absolute ethyl alcohol, uniformly coating the mixture on a glass substrate to form a thin layer, heating and drying the thin layer, bonding the powder by using a single-sided transparent adhesive tape, placing the single-sided transparent adhesive tape in deionized water, ultrasonically treating the mixture, and drying the mixture to bond the pyrite powder on the bonding surface of the adhesive tape; placing the adhesive tape bonded with the powder in the silane hydrolysate 1 for reacting for 3 hours, taking out, cleaning and drying, placing in acetone for soaking for 0.5 hour, filtering out solids, cleaning and drying to obtain silane-treated pyrite 4;
placing 1 part of the silane-treated pyrite 4 into 95 parts of butyl acetate, performing ultrasonic dispersion, adding 0.13 part of 1-amino-2-methylanthraquinone and 0.012 part of 2-methylimidazole, stirring and reacting at 30 ℃ for 2 hours, filtering out solid, cleaning and drying to obtain modified pyrite powder 4 with photocatalytic performance, and marking P-4.
Example 5
Ultrasonically dispersing 1 part of pyrite powder with the average particle size of 5 mu m in 100 parts of absolute ethyl alcohol, uniformly coating the mixture on a glass substrate to form a thin layer, heating and drying the thin layer, bonding the powder by using a single-sided transparent adhesive tape, placing the single-sided transparent adhesive tape in deionized water, ultrasonically treating the mixture, and drying the mixture to bond the pyrite powder on the bonding surface of the adhesive tape; placing the adhesive tape bonded with the powder in the silane hydrolysate 1 for reacting for 3 hours, taking out, cleaning, drying, placing in a baking oven at 60 ℃ for baking for 2 minutes, taking out, and scraping the powder to obtain silane-treated pyrite 5;
placing 1 part of the silane-treated pyrite 5 in 95 parts of absolute ethyl alcohol, performing ultrasonic dispersion, adding 0.16 part of 1-amino-2-methylanthraquinone and 0.012 part of 2-methylimidazole, stirring and reacting at 20 ℃ for 5 hours, filtering out solid, cleaning and drying to obtain modified pyrite powder 5 with photocatalytic performance, and marking P-5.
Example 6
Ultrasonically dispersing 1 part of pyrite powder with the average particle size of 2 mu m in 95 parts of absolute ethyl alcohol, uniformly coating the pyrite powder on a glass substrate to form a thin layer, heating and drying, bonding the pyrite powder by using a double-sided adhesive tape, placing the double-sided adhesive tape in deionized water for ultrasonic treatment, and drying, wherein the pyrite powder is bonded on 2 bonding surfaces of the double-sided adhesive tape; placing the adhesive tape bonded with the powder in the silane hydrolysate 2 for reacting for 2 hours, taking out, cleaning and drying the adhesive tape, placing the adhesive tape in ethyl acetate for soaking for 1 hour, filtering out solids, cleaning and drying the solids to obtain silane-treated pyrite 6;
placing 1 part of the silane-treated pyrite 6 into 90 parts of absolute ethyl alcohol, performing ultrasonic dispersion, adding 0.1 part of 1-amino-2-methylanthraquinone and 0.015 part of 2-methylimidazole, stirring and reacting for 1 hour at 30 ℃, filtering out solids, cleaning and drying to obtain modified pyrite powder 6 with photocatalytic performance, and marking P-6.
Comparative example 1
Ultrasonically dispersing 1 part of pyrite powder with the average particle size of 15 mu m in the silane hydrolysate 2, reacting for 3 hours, taking out, cleaning and drying to obtain silane-treated pyrite 7;
placing 1 part of the silane-treated pyrite 7 in 70 parts of absolute ethyl alcohol, performing ultrasonic dispersion, adding 0.1 part of 2-aminoanthraquinone and 0.012 part of 2-methylimidazole, stirring and reacting at 30 ℃ for 3 hours, filtering out solids, cleaning and drying to obtain modified pyrite powder 7, and marking P-7.
Comparative example 2
Ultrasonically dispersing 1 part of pyrite powder with the average particle size of 5 mu m in the silane hydrolysate 2, reacting for 2.5 hours, taking out, cleaning and drying to obtain silane-treated pyrite 8;
placing 1 part of the silane-treated pyrite 8 into 80 parts of absolute ethyl alcohol, performing ultrasonic dispersion, adding 0.1 part of 2-aminoanthraquinone and 0.012 part of 2-methylimidazole, stirring and reacting at 30 ℃ for 3 hours, filtering out solids, cleaning and drying to obtain modified pyrite powder 8, and marking P-8.
Comparative example 3
Ultrasonically dispersing 1 part of solid glass microspheres with the average particle size of 15 mu m in 95 parts of absolute ethyl alcohol, uniformly coating the mixture on a glass substrate to form a thin layer, heating and drying the thin layer, bonding the powder by using a double-sided tape, placing the powder in deionized water, ultrasonically treating the powder, and drying the powder to bond the solid glass microspheres on 2 bonding surfaces of the double-sided tape; placing the adhesive tape bonded with the solid glass microspheres in the silane hydrolysate 2 for reacting for 2 hours, taking out, cleaning and drying, placing in ethyl acetate for soaking for 1 hour, filtering out solids, cleaning and drying to obtain silane-treated solid glass microspheres;
placing 1 part of the silane-treated solid glass microspheres in 90 parts of absolute ethyl alcohol, performing ultrasonic dispersion, adding 0.5 part of 1-amino-2-methylanthraquinone and 0.06 part of 2-methylimidazole, stirring at 30 ℃ for reaction for 1 hour, filtering out solids, cleaning and drying to obtain modified solid glass microspheres marked with P-9.
Comparative example 4
Untreated pyrite powder with an average particle size of 15 μm, labeled as P-10.
Performance testing
Photocatalytic degradation test of heavy metals and organic matters: adjusting pH of water containing 20mg/L heavy metal Cr (VI) and 30mg/L organic matter malachite green to 3.0 at intensity of 15W/cm2Under the irradiation of ultraviolet light, 1g/L of samples to be tested are respectively added, stirred and reacted for 120 minutes, and the concentrations of Cr (VI) and malachite green are tested, and the results are shown in Table 1.
TABLE 1
Figure BDA0002774881300000061
As can be seen from Table 1, the modified pyrite powder of the present invention has a good photocatalytic degradation effect on Cr (VI) and malachite green.
Photocatalytic degradation testing of azo dyes: at an intensity of 15W/cm2Under the irradiation of ultraviolet light, 2g of a sample to be tested is respectively washed by physiological saline for 3 times, and then added into 200ml of 120mg/L acid red B containing azo dye degradation strain GYZ (staphylococcus sp) in logarithmic growth phase for decolorization test, and the change of the concentration of the acid red B along with the time is measured. The results are shown in Table 2.
TABLE 2
Figure BDA0002774881300000062
Figure BDA0002774881300000071
Therefore, as can be seen from the results in table 2, the modified pyrite obtained by the preparation method of the present invention has a good microbial degradation promoting effect on azo dyes under the irradiation of ultraviolet light, and can significantly increase the microbial degradation rate of azo dyes.
Degradation testing of azo dyes: after 2g of a sample to be tested is respectively washed by physiological saline for 3 times, the sample is added into 200ml of 120mg/L acid red B containing azo dye degradation strain GYZ (staphylococcus sp.) in logarithmic growth phase for decolorization test, and the change of the concentration of the acid red B along with time is determined. The results are shown in Table 3.
TABLE 3
Figure BDA0002774881300000072
Therefore, as can be seen from the results in table 3, the modified pyrite obtained by the preparation method of the present invention has a good microbial degradation promoting effect on azo dyes without ultraviolet light irradiation, and can increase the microbial degradation rate of azo dyes.
Photocatalytic degradation testing of nitrates: at an intensity of 15W/cm2Under the irradiation of ultraviolet light, 2g of samples to be tested are respectively washed by physiological saline for 3 times, and then added into 200ml of nitrate wastewater containing 150mg/L of denitrifying microorganisms in logarithmic growth phase for testing, and the change of the nitrate concentration along with the time is measured. The results are shown in Table 4.
TABLE 4
Figure BDA0002774881300000073
Figure BDA0002774881300000081
Therefore, as can be seen from the results in table 4, the modified pyrite obtained by the preparation method of the present invention has a good microbial degradation promoting effect on the nitrate under the irradiation of the ultraviolet light, and can significantly increase the microbial degradation rate of the nitrate.
Degradation tests on nitrates: after 2g of samples to be tested are respectively washed by physiological saline for 3 times, the samples are added into 200ml of nitrate wastewater containing denitrifying microorganisms in logarithmic growth phase and 150mg/L for testing, and the change of the nitrate concentration along with time is measured. The results are shown in Table 5.
TABLE 5
Figure BDA0002774881300000082
Therefore, as can be seen from the results in table 5, the modified pyrite obtained by the preparation method of the present invention has a better microbial degradation promoting effect on nitrate in the absence of ultraviolet light irradiation, and can increase the microbial degradation rate of nitrate.
And (3) stability testing: after 2g of samples to be tested are respectively washed 3 times by physiological saline, the samples are added into 200ml of 120mg/L acid red B containing azo dye degradation strain GYZ (staphylococcus sp.) in logarithmic growth phase for decolorization test (the test is carried out at the intensity of 15W/cm)2Under uv irradiation) was performed, and the concentration of acid red B was measured after 6 hours. And cleaning and drying a sample to be tested by using clear water and absolute ethyl alcohol, then carrying out photocatalytic degradation and decoloration test for 6 hours by using acid red B according to the method, and repeatedly testing for 12 times. The results are shown in Table 6.
TABLE 6
Figure BDA0002774881300000091
The results in table 6 show that the modified pyrite obtained by the preparation method of the present invention has good stability in promoting the rate of improving the microbial degradation of azo dyes under the irradiation of ultraviolet light.
In conclusion, the modified pyrite obtained by the preparation method has better effects on promoting degradation of heavy metal ions and malachite green and promoting microbial degradation of azo dyes and nitrates under the irradiation of ultraviolet light.
The foregoing has shown and described the fundamental principles, principal features and advantages of the invention. It should be understood by those skilled in the art that the present invention is not limited by the foregoing embodiments, which are merely preferred embodiments of the present invention, and the scope of the present invention should not be limited thereby, and that equivalent changes and modifications made within the scope of the present invention and the specification should be covered thereby. The scope of the invention is defined by the appended claims and equivalents thereof.

Claims (10)

1. The preparation method of the modified pyrite powder with photocatalytic performance is characterized by comprising the following steps,
s1, bonding the pyrite powder to the bonding surface of the adhesive tape, placing the tape in silane hydrolysate for reaction for 0.5-5 hours, taking out, cleaning, drying, and removing the adhesive tape to obtain silane-treated pyrite;
s2, placing the silane-treated pyrite in the step S1 in an organic solvent, performing ultrasonic dispersion, adding an anthraquinone compound and an auxiliary agent, stirring and reacting for 1-5 hours at the temperature of 20-50 ℃, filtering out solids, cleaning and drying to obtain the modified pyrite powder with photocatalytic performance.
2. The method according to claim 1, wherein the pyrite powder in step S1 has an average particle size of 0.5 to 100 μm.
3. The method of claim 1, wherein the silane in step S1 is selected from epoxy silanes.
4. The method of claim 3, wherein the silane hydrolysate in step S1 is obtained by: adding 1 part by weight of epoxy silane into 30-100 parts by weight of a mixed solvent of anhydrous ethanol and water in a volume ratio of 80: 20-90: 10, adjusting the pH value to be acidic, and stirring for 0.5-5 hours to obtain a silane hydrolysate.
5. The method according to claim 1, wherein the weight ratio of the silane-treated pyrite, the organic solvent, and the anthraquinone compound in step S2 is 1:10 to 100:0.05 to 0.2.
6. The production method according to claim 1, wherein the anthraquinone compound in step S2 is selected from the group consisting of aminoanthraquinone-containing compounds selected from at least one of 1-amino-2-bromo-4-hydroxyanthraquinone, 2-aminoanthraquinone, 1, 2-diaminoanthraquinone, 1, 4-diaminoanthraquinone, 2, 6-diaminoanthraquinone, 1, 8-diaminoanthraquinone, 1, 5-diaminoanthraquinone, 1-amino-2-methylanthraquinone, 1, 5-dihydroxy-4, 8-diaminoanthraquinone and 1-aminoanthraquinone.
7. The method according to claim 7, wherein the organic solvent in step S2 comprises absolute ethanol, tetrahydrofuran, ethyl acetate, and butyl acetate.
8. The method according to claim 1, wherein the auxiliary in step S2 is an accelerator selected from one or more of 2-methylimidazole, 1-methylimidazole, 2-ethyl-4-methylimidazole, 2-phenylimidazole, 2-undecylimidazole and 2-phenyl-4-methylimidazole.
9. A modified pyrite having photocatalytic properties, characterized by being obtained by the preparation method according to any one of claims 1 to 8.
10. Use of the modified pyrite of claim 9 in wastewater treatment.
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