CN1101730C - Photocatalyst capable of magnetic separating and preparation therefor - Google Patents
Photocatalyst capable of magnetic separating and preparation therefor Download PDFInfo
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- CN1101730C CN1101730C CN98101176A CN98101176A CN1101730C CN 1101730 C CN1101730 C CN 1101730C CN 98101176 A CN98101176 A CN 98101176A CN 98101176 A CN98101176 A CN 98101176A CN 1101730 C CN1101730 C CN 1101730C
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Abstract
The present invention belongs to the technical field of a photocatalyst, particularly belongs to magnetic separable photocatalyst and a preparation method thereof. The photocatalyst is composed of magnetic carriers and semiconductor nanometer particles, and has the proportion by weight: the magnetic carriers: the semiconductor nanometer particles is equal to 3: 1 to 1: 4, wherein the magnetic carriers is provided with substances with ferromagnetism; the semiconductor nanometer particles are semiconductor substances with photocatalytic activity. The present invention utilizes a sol-gel method or a solid particle mixing method to load the semiconductor nanometer particles on the magnetic substances, and enables the semiconductor nanometer photocatalyst to be effectively separated from a solution after the reaction through an external magnetic field for repeated use. The present invention solves the problem that the nanometer photocatalyst is difficult to separate in a photocatalytic reaction system at present.
Description
Technical field under the present invention is a photochemical catalyst, particularly belongs to photochemical catalyst capable of magnetic separating and method for making thereof.
As everyone knows, along with industrial expansion, problem of environmental pollution is very serious.In China, nearly 1/2 river is polluted, and 1.64 hundred million people drink the serious water of organic contamination.The wherein difficult proportion that decomposes toxic organic pollutant is also in rapid increase, and many toxic organic pollutants can't be handled with existing microbial technique, or can't thoroughly remove.
In recent years, the Nano semiconductor photocatalysis technology has been obtained very big progress, and many nano semiconductor materials are as titanium dioxide (TiO
2), tin ash (SnO
2), zinc oxide (ZnO), cadmium sulfide (CdS), tungstic acid (WO
3) wait and all be found this type of difficult toxic organic pollutant that decomposes of can degrading effectively, this type of document has " colloid and surface " magazine, 1992,67, the article of delivering on the 165-182 " light degradation of the surfactant of titanium dioxide semiconductor catalysis " (H.Hidaka, J.Zhao, Photodegradation of surfactants catalyzed by a TiO
2Semiconductor, Colloids and Surfaces), " environmental science and technology " magazine, 1991,25, the article of delivering on the 1523-1529 " processing of water pollutant " (D.F.Ollis, E.Pellizzetti, N.Serpone, Destruction of Water Contaminants, Environ.Sci.Technol.), " chemistry summary " magazine, 1995,95, the article of delivering on the 69-96 " environmental applications of conductor photocatalysis " (M.R.Hoffmann, S.T.Martin, W.Choi, D.W.Bahnemann, Environmental Application ofSemiconductor Photocatalysis, Chem.Rev.).But the semi-conductor nano particles dispersion that extensively adopts in the reported in literature exists a very big problem to need to be resolved hurrily at present: how the nano particle photochemical catalyst is separated from reacted solution and reused.Because semiconductor nano photocatalyst particles very little (being generally a few to tens of nanometers) uses separation technology such as centrifugation or hyperfiltration will greatly increase equipment investment and running expense.Some researchers have taked the semiconductor nano photochemical catalyst is loaded on the method for glass sheet surface, and this type of document has " physical chemistry magazine ", and 1995,99, " surfactant is at TiO for the article of delivering on the 8244-8248
2Optical Electro-Chemistry on the/TCO membrane electrode is decomposed " (H.Hidaka, γ .Asai, J.Zhao, K.Nohara, E.Pelizzetti, N.Serpone, Photoelectrochemical Decomposition of Surfactants on a TiO
2/ TCOParticulate Film Electrode Assembly, J.Phys.Chem..) or the semiconductor nano photochemical catalyst is loaded on the method on glass fabric surface, this type of document has " light catalytic purifying of water and air and processing ", 1993, the article of delivering on the pp783-788 " chloroform is at the photocatalytic degradation that scribbles titanium dioxide glass fabric surface " (M.Murabayashi, K.Itoh, K.Kawashima, R.Masuda, S.Suzuki, Photocatalyticdegradation of chloroform with TiO
2Coated glass fiber cloth, " PhotocatalyticPurification and Treatment of water and air " Ed.D.F.Ollis and H.Al-Ekabi; Elsevier).Though these methods have been avoided the separation difficult problem of Nano semiconductor photochemical catalyst, also greatly reduce effective contact area on reactant and semiconductor nano photocatalyst granular surface, influenced the efficient of light-catalyzed reaction.
The objective of the invention is to overcome the shortcoming of semiconductor nano photochemical catalyst in the past, a kind of segregative semiconductor nano photochemical catalyst is provided, it can be effectively and liquid phase separation, can keep decentralization and the photocatalysis performance of semiconductor nano photochemical catalyst in solution again.
Photochemical catalyst capable of magnetic separating of the present invention is made up of magnetic carrier and semi-conductor nano particles.Its weight ratio is a magnetic carrier: semi-conductor nano particles=3: 1～1: 4.
Wherein magnetic carrier is that tri-iron tetroxide, γ-di-iron trioxide, chromium dioxide, cobalt improved γ-di-iron trioxide, barium ferrite etc. have ferromagnetic material, and its particle diameter is between 5 nanometer to 10 microns.Semi-conductor nano particles is titanium dioxide (TiO
2), tin ash (SnO
2), zinc oxide (ZnO), cadmium sulfide (CdS), tungstic acid (WO
3) wait material with photocatalytic activity; Its particle diameter is between 1 nanometer to 1 micron.
(1) preparation of magnetic carrier
Magnetic carrier described in the present invention can use laboratory products or commercially available magnetic material, as: tri-iron tetroxide, γ-di-iron trioxide, chromium dioxide, cobalt improved γ-di-iron trioxide, barium ferrite etc.Wherein the laboratory preparation of tri-iron tetroxide, γ-di-iron trioxide is as follows:
To be added to the metal salt solution that is made into 0.1～1 mol in the hydrochloric acid solution of 0.01 mol with the corresponding soluble metallic salt of magnetic carrier (for example ferrous sulfate and ferric trichloride); according to different requirements; under the nitrogen protection condition; add fast the solution that contains 0.1～1 mol hydroxide ion (for example potassium hydroxide etc.) and make its precipitation to pH=9～12; product spends deionised water to pH=7～9, promptly gets the magnetic carrier tri-iron tetroxide after the oven dry or continue to obtain magnetic carrier γ-di-iron trioxide in 0.5～3 hour through roasting down at 400 ℃～900 ℃.
(2) preparation of semi-conductor nano particles
Semi-conductor nano particles described in the present invention can directly use commercially available semi-conductor nano particles, as the P25 type TiO of DeggusaCo.
2, the titanium dioxide of 404 factories of China Nuclear Industry Corporation and tin ash, zinc oxide, cadmium sulfide, tungstic acid etc.; But also prepared in laboratory.Wherein the prepared in laboratory of titanium dioxide is as follows:
The preparation of titanium dioxide semiconductor nano particle utilizes sol-gel process.Preparation titanium dioxide semiconductor nano material required compound 0.01～0.5 mole (for example isopropyl titanate and isopropyl alcohol etc.) was added in 10 minutes～30 minutes under vigorous stirring contains hydrolysis in 500 milliliters of salpeter solutions of 0～0.1 mol, stirred 1～8 hour down at 50 ℃～90 ℃, obtain the titanium dioxide semiconductor Nano sol at last.After the oven dry, roasting gets the titanium dioxide semiconductor nanoparticle powder under 400 ℃～900 ℃ air atmospheres of high temperature.
Photochemical catalyst capable of magnetic separating of the present invention is prepared as follows:
Semi-conductor nano particles and magnetic material compound:
The magnetic carrier particle is mixed by weight 3: 1～1: 4 with semi-conductor nano particles (or its Nano sol), but the photochemical catalyst of drying and 400 ℃～900 ℃ high-temperature roasting preparation Magnetic Isolation.Two different preparation technologies are as follows:
A, sol-gel process
In semiconductor nano colloidal sol, add the solution that is made into 0.1～1 mol with the corresponding soluble metallic salt of magnetic carrier; under the nitrogen protection condition; add logical nitrogen fast and removed the solution (for example potassium hydroxide solution) of the hydroxide ion that contains 0.1～1 mol of air in 1 hour; make itself and semi-conductor nano particles co-precipitation to pH=9～12 of solution; product spends deionised water to pH=7～9, promptly gets the former powder of magnetic photocatalyst composite after the oven dry.Wherein the particle diameter of magnetic carrier is between 5 nanometer to 10 microns; The particle diameter of semi-conductor nano particles is between 1 nanometer to 1 micron; its weight ratio is a magnetic carrier: semi-conductor nano particles=3: 1～1: 4; 400 ℃ of-900 ℃ of roastings 0.5～3 hour under air or nitrogen protection of this former powder just make photochemical catalyst capable of magnetic separating.
The used soluble metallic salt of this method is divalent iron salt and trivalent iron salt (for example ferrous sulfate and ferric trichloride).
B, solids mixing method
The magnetic carrier particle is mixed by weight 3: 1～1: 4 with the semi-conductor nano particles powder, and wherein the particle diameter of magnetic carrier is between 5 nanometer to 10 microns; The particle diameter of semi-conductor nano particles adds low amounts of water furnishing pasty state after the grinding between 1 nanometer to 1 micron, and with ultrasonic wave that both further grinding dispersion are even, just makes the former powder of magnetic photocatalyst composite after the drying.This former powder through 400 ℃ of-900 ℃ of roastings 0.5～3 hour, just makes photochemical catalyst capable of magnetic separating after the cooling under air or nitrogen protection.
Wherein said magnetic carrier is tri-iron tetroxide, γ-di-iron trioxide, chromium dioxide, cobalt improved γ-di-iron trioxide, barium ferrite.Described semi-conductor nano particles is titanium dioxide, tin ash, zinc oxide, cadmium sulfide, tungstic acid.
The purposes of photochemical catalyst capable of magnetic separating of the present invention:
The photocatalysis treatment of photochemical catalyst capable of magnetic separating of the present invention organic pollution, heavy metal ion etc. in can be used for waste water, surface water and drinking water, also can be used for light-catalyzed reactions such as photocatalysis is synthetic, photocatalysis fixed nitrogen.
Photochemical catalyst capable of magnetic separating of the present invention can be evenly dispersed in the reaction system under stirring or importing air conditions, the highlight catalytic active that had both kept dispersion, can utilize externally-applied magnetic field at an easy rate photochemical catalyst to be separated from reacted solution again, promote light-catalyzed reaction further to push practicability to.
Specify effect of the present invention below in conjunction with accompanying drawing:
Description of drawings:
Fig. 1, fluorescein(e) dye (1 * 10
-5M) the photocatalytic degradation reaction result under UV-irradiation
Curve 1-does not have photochemical catalyst,
Curve 2-1 grams per liter sample 1 (magnetic carrier is by preparation among the embodiment 1),
Curve 3-2 grams per liter sample 3b (photochemical catalyst capable of magnetic separating is by preparation among the embodiment 4).
Fig. 2, fluorescein(e) dye (1 * 10
-5M) the photocatalytic degradation reaction result under UV-irradiation
Curve 1-does not have photochemical catalyst,
Curve 2-1 grams per liter sample 2 (magnetic carrier is by preparation among the embodiment 2),
Curve 3-2 grams per liter sample 4b (photochemical catalyst capable of magnetic separating is by preparation among the embodiment 5).
Fig. 3, Acid Red G dyestuff (5 * 10
-5M) the photocatalytic degradation reaction result under UV-irradiation
Curve 1-does not have photochemical catalyst,
Curve 2-1 grams per liter sample 1 (magnetic carrier is by preparation among the embodiment 1),
Curve 3-2 grams per liter sample 3b (photochemical catalyst capable of magnetic separating is by preparation among the embodiment 4).
Fig. 4, Acid Red G dyestuff (5 * 10
-5M) the photocatalytic degradation reaction result under UV-irradiation
Curve 1-does not have photochemical catalyst,
Curve 2-1 grams per liter sample 2 (magnetic carrier is by preparation among the embodiment 2),
Curve 3-2 grams per liter sample 4b (photochemical catalyst capable of magnetic separating is by preparation among the embodiment 5).
Curve 1 and curve 2 are respectively blank assay among Fig. 1, and the light degradation reaction does not almost take place in the blank assay.In the presence of 2 grams per liter sample 3b, use UV-irradiation, in 45 minutes, almost all (96%) fluoresceins be degraded (Fig. 1. curve 3).The reaction back is under the externally-applied magnetic field effect, and sample 3b photochemical catalyst is easy to be separated from solution.
Curve 1 and curve 2 are respectively blank assay among Fig. 2, and the light degradation reaction does not almost take place in the blank assay.In the presence of 2 grams per liter sample 4b, use UV-irradiation, in 1 hour, almost all (98%) fluoresceins be degraded (Fig. 2. curve 3).The reaction back is under the externally-applied magnetic field effect, and sample 4b photochemical catalyst is easy to be separated from solution.
Curve 1 and curve 2 are respectively blank assay among Fig. 3, and the light degradation reaction does not almost take place in the blank assay.In the presence of 2 grams per liter sample 3b, use UV-irradiation, in 2.5 hours, 56% Acid Red G dyestuff be degraded (Fig. 3. curve 3).The reaction back is under the externally-applied magnetic field effect, and sample 3b photochemical catalyst is easy to be separated from solution.
Curve 1 and curve 2 are respectively blank assay among Fig. 4, and the light degradation reaction does not almost take place in the blank assay.In the presence of 2 grams per liter sample 4b, use UV-irradiation, in 2.5 hours, 70% Acid Red G dyestuff be degraded (Fig. 4. curve 3).The reaction back is under the externally-applied magnetic field effect, and sample 4b photochemical catalyst is easy to be separated from solution.
Prepare 1 * 10 respectively
-4The fluorescein(e) dye solution and 1 * 10 of mol
-4The Acid Red G dye solution of mol, the sample 4b that adds preparation among the embodiment 4, being incident upon dye solution through ultraviolet lighting fades, measure its total COD (COD) value in order to characterize organic photocatalytic degradation mineralization degree in the solution, the COD rate of removing of fluorescein is 96%, and the COD rate of removing of Acid Red G is 83%.
Embodiment:
Magnetic carrier prepares embodiment 1
In the hydrochloric acid solution of 500 milliliter of 0.01 mol, add 15 gram FeSO
47H
2O (0.11 mol) and 27 gram FeCl
3(0.2 mol), it dissolves the logical nitrogen in back fully removed air in 1 hour.Under the vigorous stirring, in system, add the 1 mol KOH solution that logical nitrogen was removed air in 1 hour, to the pH=11 of solution, it is precipitated immediately.Under nitrogen protection, continue to stir 2 hours, last suction filtration, and spend the deionised water solid repeatedly to the pH=8.Promptly get black Fe after the drying
3O
4Powder (sample 1).
Magnetic carrier prepares embodiment 2
The method for making for preparing embodiment 1 by magnetic carrier is prepared sample 1, with sample 1 500 ℃ of roastings 0.5 hour in air, γ-ferric oxide powder (sample 2).
Semi-conductor nano particles prepares embodiment 1
In dropping funel, add 15 milliliters of isopropyl alcohols (0.2 mole) and 80 milliliters of isopropyl titanates (0.29 mole), about 20 fens clock times, under the vigorous stirring, slowly be added drop-wise in the salpeter solution of 500 milliliter of 0.1 mol.Solution stirred 8 hours down at 80 ℃, obtained TiO at last
2The hydrosol (colloidal sol 1).
Semi-conductor nano particles prepares embodiment 2
In dropping funel, add 15 milliliters of isopropyl alcohols (0.2 mole) and 10 milliliters of isopropyl titanates (0.036 mole), about 20 fens clock times, under the vigorous stirring, slowly be added drop-wise in the salpeter solution of 500 milliliter of 0.1 mol.Solution stirred 5 hours down at 80 ℃, obtained TiO at last
2The hydrosol (colloidal sol 2).
Photochemical catalyst capable of magnetic separating prepares embodiment 1
Prepare adding 6.0 gram ferrous sulfate hydrates (0.044 mol) and 10.8 gram ferric trichlorides (0.08 mol) in the titania hydrosol (colloidal sol 2) for preparing among the embodiment 2 to 500 milliliters at semi-conductor nano particles; The logical nitrogen in dissolving back was removed air in 1 hour fully.Vigorous stirring adds the 1 mol KOH solution that logical nitrogen was removed air in 1 hour again in system, to the pH=11 of solution, make slaine and titanium dioxide co-precipitation.Under nitrogen protection, continue to stir 2 hours, last suction filtration, and repeatedly wash solid to the pH=8 with deionized water.Promptly get the former powder of magnetic photocatalyst composite (former powder 1) after the drying; Magnetic carrier wherein: semi-conductor nano particles=1.66: 1, the tube furnace of the former powder 1 that obtains being put into logical nitrogen protection heats, and 500 ℃ of insulations 30 minutes down, makes photochemical catalyst capable of magnetic separating (sample 3a) after the cooling.
Photochemical catalyst capable of magnetic separating prepares embodiment 2
Prepare embodiment 1 method by photochemical catalyst capable of magnetic separating and prepare the former powder 1 of magnetic photocatalyst composite, with the 500 ℃ of following roastings 30 minutes in air atmosphere of former powder 1, make photochemical catalyst capable of magnetic separating (sample 4a) after the cooling then.
Photochemical catalyst capable of magnetic separating prepares embodiment 3
Prepare embodiment 1 method by photochemical catalyst capable of magnetic separating and prepare the former powder 1 of magnetic photocatalyst composite, with the 500 ℃ of following roastings 2 hours in air atmosphere of former powder 1, make photochemical catalyst capable of magnetic separating (sample 5a) after the cooling then.
Photochemical catalyst capable of magnetic separating prepares embodiment 4
Prepare embodiment 1 method by magnetic carrier and prepare sample 1, get 2.0 gram samples 1 and 2.0 gram titanium dioxide nano-particles (Deggusa Co. product, P25 type) mixing.Grind, add low amounts of water furnishing pasty state then, with ultrasonic wave with both further grinding dispersion evenly, after the drying the former powder 2 of magnetic photocatalyst composite.The tube furnace of the former powder 2 that obtains being put into logical nitrogen protection heats, and is incubated 30 minutes down at 500 ℃, makes photochemical catalyst capable of magnetic separating (sample 3b) after the cooling.
Photochemical catalyst capable of magnetic separating prepares embodiment 5
The method for preparing embodiment 4 by photochemical catalyst capable of magnetic separating prepares the former powder 2 of magnetic photocatalyst, with the roasting to 500 ℃ in air atmosphere of the former powder 2 of photochemical catalyst, is incubated 30 minutes, makes photochemical catalyst capable of magnetic separating (sample 4b) after the cooling.
Photochemical catalyst capable of magnetic separating prepares embodiment 6
The method for preparing embodiment 4 by photochemical catalyst capable of magnetic separating prepares the former powder 2 of magnetic photocatalyst, with the roasting to 500 ℃ in air atmosphere of the former powder 2 of photochemical catalyst, is incubated 2 hours, makes photochemical catalyst capable of magnetic separating (sample 5b) after the cooling.
Photochemical catalyst capable of magnetic separating prepares embodiment 7
Get the 2.0 commercially available γ-di-iron trioxides of gram (Shanghai Iron Oxide Pigment Factory) and mix, grind, add low amounts of water furnishing pasty state then with 1.0 gram titanium dioxide nano-particles, with ultrasonic wave that both further grinding dispersion are even.After the drying the former powder 3 of magnetic photocatalyst composite, with the roasting to 500 ℃ in air atmosphere of the former powder 3 that obtains, be incubated 45 minutes, make photochemical catalyst capable of magnetic separating (sample 6) after the cooling.
Photochemical catalyst capable of magnetic separating prepares embodiment 8
Getting the 1.0 commercially available γ-di-iron trioxides of gram (Shanghai Iron Oxide Pigment Factory) mixes with 4.0 gram titanium dioxide nano-particles, grind, add low amounts of water furnishing pasty state then, with ultrasonic wave with both further grinding dispersion evenly, after the drying the former powder 4 of magnetic photocatalyst composite.With the roasting to 500 ℃ in air atmosphere of the former powder 4 that obtains, be incubated 45 minutes, make photochemical catalyst capable of magnetic separating (sample 7) after the cooling.
Claims (5)
1, a kind of photochemical catalyst capable of magnetic separating, it is characterized in that forming with semi-conductor nano particles with photocatalytic activity by having ferromagnetic magnetic carrier, its weight ratio is a magnetic carrier: semi-conductor nano particles=3: 1～1: 4, and wherein the particle diameter of magnetic carrier is between 5 nanometer to 10 microns; The particle diameter of semi-conductor nano particles is between 1 nanometer to 1 micron;
It is described that to have ferromagnetic magnetic carrier be tri-iron tetroxide, γ-di-iron trioxide, chromium dioxide, cobalt improved γ-di-iron trioxide or barium ferrite;
Described semi-conductor nano particles with photocatalytic activity is titanium dioxide, tin ash, zinc oxide, cadmium sulfide or tungstic acid.
2, a kind of method for making of photochemical catalyst capable of magnetic separating as claimed in claim 1 is characterized in that
A, use sol-gel process:
In semiconductor nano colloidal sol, add the solution that is made into 0.1～1 mol with the corresponding soluble metallic salt of magnetic carrier, under the nitrogen protection condition, add logical nitrogen fast and remove the solution of the hydroxide ion that contains 0.1～1 mol of air, pH=9～12 to solution, make itself and semi-conductor nano particles co-precipitation, product is washed to pH=7～9, promptly get the former powder of magnetic photocatalyst composite after the oven dry, wherein the particle diameter of magnetic carrier is between 5 nanometer to 10 microns; The particle diameter of semi-conductor nano particles is between 1 nanometer to 1 micron, its weight ratio is a magnetic carrier: semi-conductor nano particles=3: 1～1: 4,400 ℃ of-900 ℃ of roastings 0.5～3 hour under air or nitrogen protection of this former powder just make photochemical catalyst capable of magnetic separating;
Or
B, solids mixing method:
The magnetic carrier particle is mixed by weight 3: 1～1: 4 with the semi-conductor nano particles powder, and wherein the particle diameter of magnetic carrier is between 5 nanometer to 10 microns; The particle diameter of semi-conductor nano particles is between 1 nanometer to 1 micron; add low amounts of water furnishing pasty state after the grinding; and it is both further grinding dispersion are even with ultrasonic wave; just make the former powder of magnetic photocatalyst composite after the drying; this former powder is under air or nitrogen protection; through 400 ℃ of-900 ℃ of following roastings 0.5～3 hour, just make photochemical catalyst capable of magnetic separating after the cooling.
3, the method for making of photochemical catalyst capable of magnetic separating as claimed in claim 2 is characterized in that described and the corresponding soluble metallic salt of magnetic carrier is solubility divalent iron salt and trivalent iron salt.
4, the method for making of photochemical catalyst capable of magnetic separating as claimed in claim 2 is characterized in that described magnetic carrier is tri-iron tetroxide, γ-di-iron trioxide, chromium dioxide, cobalt improved γ-di-iron trioxide or barium ferrite.
5, the method for making of photochemical catalyst capable of magnetic separating as claimed in claim 2 is characterized in that described semi-conductor nano particles is titanium dioxide, tin ash, zinc oxide, cadmium sulfide or tungstic acid.
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|---|---|---|---|
| CN98101176A CN1101730C (en) | 1998-04-10 | 1998-04-10 | Photocatalyst capable of magnetic separating and preparation therefor |
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|---|---|---|---|
| CN98101176A CN1101730C (en) | 1998-04-10 | 1998-04-10 | Photocatalyst capable of magnetic separating and preparation therefor |
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| CN1200959A CN1200959A (en) | 1998-12-09 |
| CN1101730C true CN1101730C (en) | 2003-02-19 |
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| CN98101176A Expired - Fee Related CN1101730C (en) | 1998-04-10 | 1998-04-10 | Photocatalyst capable of magnetic separating and preparation therefor |
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN100486690C (en) * | 2005-10-25 | 2009-05-13 | 中国科学院过程工程研究所 | Optical catalyst capable of magnetic separated and its preparation method |
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| AUPP972299A0 (en) * | 1999-04-13 | 1999-05-06 | Unisearch Limited | A photocatalyst |
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| CN1180881C (en) * | 2002-07-23 | 2004-12-22 | 北京化工大学 | Magnetic nano solid base catalyst and its preparnig method |
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| CN108928881A (en) * | 2018-08-02 | 2018-12-04 | 四川大学 | Magnetic agglomerates photo catalysis reactor and photocatalysis sewage treatment equipment and method |
| CN109499591B (en) * | 2018-11-15 | 2021-02-12 | 江苏大学 | Preparation method and application of magnetically-recoverable photo-Fenton-like catalyst |
| CN111298795A (en) * | 2020-03-19 | 2020-06-19 | 六盘水师范学院 | Performance optimization method of strontium titanate magnetic photocatalyst |
| CN111974407A (en) * | 2020-07-13 | 2020-11-24 | 重庆大学 | Method for preparing magnetic tungsten trioxide composite photocatalyst |
| CN112079408A (en) * | 2020-09-03 | 2020-12-15 | 施晓晨 | Novel water treatment material, preparation method thereof and application thereof in water treatment |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6154620A (en) * | 1984-08-25 | 1986-03-18 | Fujitsu Ltd | Manufacture of semiconductor device |
| JPH0975746A (en) * | 1995-09-08 | 1997-03-25 | Okaya Electric Ind Co Ltd | Magnetic photocatalyst material, water treatment the same and water treating device using |
| JPH09290165A (en) * | 1996-04-30 | 1997-11-11 | Fuji Electric Co Ltd | Photocatalyst and water treatment using the same |
-
1998
- 1998-04-10 CN CN98101176A patent/CN1101730C/en not_active Expired - Fee Related
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6154620A (en) * | 1984-08-25 | 1986-03-18 | Fujitsu Ltd | Manufacture of semiconductor device |
| JPH0975746A (en) * | 1995-09-08 | 1997-03-25 | Okaya Electric Ind Co Ltd | Magnetic photocatalyst material, water treatment the same and water treating device using |
| JPH09290165A (en) * | 1996-04-30 | 1997-11-11 | Fuji Electric Co Ltd | Photocatalyst and water treatment using the same |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN100486690C (en) * | 2005-10-25 | 2009-05-13 | 中国科学院过程工程研究所 | Optical catalyst capable of magnetic separated and its preparation method |
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