CN106111156A - Efficient class Fenton magnetic catalyst based on clay mineral and preparation method and application - Google Patents

Efficient class Fenton magnetic catalyst based on clay mineral and preparation method and application Download PDF

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CN106111156A
CN106111156A CN201610470204.0A CN201610470204A CN106111156A CN 106111156 A CN106111156 A CN 106111156A CN 201610470204 A CN201610470204 A CN 201610470204A CN 106111156 A CN106111156 A CN 106111156A
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clay mineral
class fenton
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magnetic catalyst
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CN106111156B (en
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龙明策
金明杰
苏寒瑞
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Shanghai Jiaotong University
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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
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/74Iron group metals
    • B01J23/745Iron
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/74Iron group metals
    • B01J23/75Cobalt
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/889Manganese, technetium or rhenium
    • B01J23/8892Manganese
    • 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
    • B01J35/33Electric or magnetic 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts
    • 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
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols
    • 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
    • C02F2305/02Specific form of oxidant
    • C02F2305/026Fenton's reagent

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
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Abstract

The present invention relates to a kind of efficient class Fenton magnetic catalyst based on clay mineral and preparation method and application.Preparation process is: clean clay mineral is added in the iron salt solutions prepared in advance by (1), makes mixed suspension be warmed up to 60 100 DEG C and continuously stirred 0.5 5 hours reach stable;(2) adding alkali liquor in suspension makes solution ph rise to 8 11, and continuously stirred 0.5 6 hours, the processes such as solid precipitation is scrubbed, dry obtained Precursor Powder;(3) during Precursor Powder impregnated in the solution containing other nonferrous metal salt, uniformly it is evaporated, heat treatment, i.e. obtains efficient class Fenton magnetic catalyst based on clay mineral.Compared with prior art, the catalyst of the present invention has Magneto separate, it is possible to reclaims and recycles, and has efficient class Fenton catalysis activity and stability under near neutral pH simultaneously.The preparation technology of this catalyst is simple, and cost is relatively low and ecological compatibility good, has broad prospect of application in difficult degradation toxic organic pollutant process field.

Description

Efficient class Fenton magnetic catalyst based on clay mineral and preparation method and application
Technical field
The invention belongs to inorganic nanometer functional material and environmental pollution control technique field, especially relate to a kind of based on viscous The soil efficient class Fenton magnetic catalyst of mineral and preparation method and application.
Background technology
The situation is tense in the pollution of surface water, subsoil water and soil that China is current, wherein with pesticide, Antibiotique composition, The difficult degradation persistence organic pollutant such as polycyclic aromatic hydrocarbon, azo dye is the polluter of representative, at the ring that we depend on for existence , irreversible potential threat will be there is to the health of ecological environment and people in the medium-term and long-term existence in border.Develop effective organic contamination Soil or water recovery technique become the vital task of field of environment pollution control.
High-level oxidation technology, including photocatalysis, plasma, supercritical water oxidation, ozone oxidation, Fenton and class Fenton oxygen The methods such as change, occupy critical role in terms of persistency toxic organic pollutant in removing environment.Wherein, heterogeneous class Fenton Chemical oxidization method, by utilizing heterogeneous catalysis material catalytic activation hydrogen peroxide or persulfate etc. to produce the hydroxyl of Strong oxdiative certainly By base, thus the toxic organic pollutant thoroughly decomposing and eliminating in environment, it is a kind of more practical persistency organic contaminant Control technology.Such as, the Chinese patent of Publication No. CN103230796A discloses a kind of attapulgite load ferroso-ferric oxide Preparation method, this Magneto separate material may be used for class Fenton's reaction degradable organic pollutant, and reclaimed by Magneto separate and urge Formed material.But the catalysis activity of the catalyst based on ferroso-ferric oxide is more weak.The most also there is other burning of employing Thing discloses a kind of nanometer as the Chinese patent of the report of carrier loaded iron oxides, such as Publication No. CN105536812A Fe3O4/Mn3O4Composite, and there is Magneto separate and the feature of class Fenton catalytic degradation organic pollution.But these are with ferrum Oxide is main catalyst, and its effective range is narrower, generally can play significantly catalysis in the pH scope less than 4 Degradation effect, and once pH value of solution is more than 4, is little to produce any catalytic action.Because asking in view of the corrosion-resistant of reactor Topic, ferrum dissolution problem under acid condition and add the problems such as increase technical costs that soda acid causes, exploitation can be in relatively Under the conditions of property pH and the efficient heterogeneous class Fenton oxidation technology that can be recycled is current facing challenges, and advanced catalysis material The development of material is the key of break-through skill bottleneck.
The Chinese patent of Publication No. CN105405567A discloses the magnetic of a kind of layered clay mineral supported ferriferous oxide Property material for the soil of Organic Pollution or the reparation of water, the method can be controlled the composition of magnetic iron oxide by roasting With structure keep the magnetic characteristic that material is good, and the method proposes to add mixing of non-ferric while preparing iron oxides Miscellaneous metallic element so that magnetic material also has obvious catalytic effect pH value is close to 4 when.But this method can be drawn The doping metals entered is the lowest, only the 0.1-5% of ferrum, because the content of higher-doped metal will cause doping metals and ferrum oxygen The interaction of compound forms nonmagnetic metal composite oxide, causes the disappearance of final catalysis material magnetic.The most how It is very important skill that raising nonferrous metal content, enhancing near neutral pH are catalyzed active, simultaneously to keep catalysis material magnetic Art problem.
Summary of the invention
Defect that the purpose of the present invention is contemplated to overcome above-mentioned prior art to exist and provide a kind of based on clay mineral Efficient class Fenton magnetic catalyst and preparation method and application.
Present invention thought based on " take from soil, be used for soil ", uses the layered clay mineral that environment compatibility is good Based on material, introduce thereon and there is the iron oxides of superparamagnetic performance, reclaim and recycle reaching quick Magneto separate Purpose;Meanwhile, the present invention passes through after iron oxides is stablized in formation, before heat treatment, introduces higher containing by infusion process The preferred nonferrous metal salt of amount, is allowed to deposit and in heat treatment process at the clay mineral of substrate and the surface of iron oxides Being decomposed to form metal-oxide, maintain the crystal phase structure of magnetic iron oxide, final acquisition catalysis activity is high, having can Magneto separate recycles feature and has the catalyst of efficient catalytic performance in wide ph range.
The purpose of the present invention can be achieved through the following technical solutions:
A kind of efficient class Fenton magnetic catalyst based on clay mineral, including clay mineral, magnetic iron oxide and Other metal-oxide, wherein magnetic iron oxide is 0.05-2 with the mass ratio of clay mineral, other metal-oxide and magnetic The mol ratio of property iron oxides is 0.1-1, and other described metal-oxide is in manganese metal, cobalt, aluminum, copper, zirconium or tungsten Plant or two oxides.
Described clay mineral has layer structure, in bentonite, illite or montmorillonite one or both Combination.
The preparation method of described based on clay mineral efficient class Fenton magnetic catalyst, comprises the following steps:
(1) clean clay mineral is added in the iron salt solutions prepared in advance, makes mixed suspension be warmed up to Reach stable for 60-100 DEG C and continuously stirred 0.5-5 hour;
(2) adding alkali liquor in suspension makes solution ph rise to 8-11, continuously stirred 0.5-6 hour, solid precipitation The process such as scrubbed, dry obtains Precursor Powder;
(3) during Precursor Powder impregnated in the solution containing other slaine, uniformly it is evaporated, heat treatment, i.e. obtains based on clay The efficient class Fenton magnetic catalyst of mineral.
Described iron salt is the mixture of any solubility divalent iron salt or bivalence and trivalent iron salt, wherein preferred ferrous iron Being 0.3-3 with ferric iron mol ratio, total concentration of iron is 0.1-5 mol/L.
Other slaine described is one or both the water solublity in metallic element manganese, cobalt, aluminum, copper, zirconium or tungsten or alcohol Soluble, the most preferably nitrate, sulfate, hydrochlorate or the complex containing ammonium root, the molar concentration of other slaine is 0.05-2 mol/L, other metallic element is 0.1-1 with the mol ratio of ferrum.
Described being evaporated operates into the heating evaporation less than 100 DEG C.
The heating rate of described heat treatment is 1-20 DEG C/min, and the temperature of heat treatment is 200-600 DEG C, the time of heat treatment For 1-48 hour, the atmosphere of heat treatment was air.
Described based on clay mineral efficient class Fenton magnetic catalyst can be used for efficient catalytic and decomposes hydrogen peroxide generation Poisonous persistent organic pollutants in water or soil are decomposed and are removed, can be reclaimed by Magneto separate simultaneously by class Fenton's reaction Utilize.
Compared with prior art, the present invention has the following advantages and beneficial effect:
(1) containing magnetic iron oxide in the catalyst of the present invention, therefore, catalyst has Magneto separate, it is possible to return Receive and recycle.
(2) in the catalyst of the present invention, possibly together with the oxide of manganese metal, cobalt, aluminum, copper, zirconium or the tungsten of other non-ferric, this The metal-oxide of a little non-ferric, with under iron oxides compound action, can have under the conditions of near neutral pH and urge efficiently Change and decompose hydrogen peroxide generation high activity hydroxyl radical free radical, play the effect of class Fenton's reaction, this is because these metal-oxides Surface isoelectric point, IP is caused to decline after compound with iron oxides, namely near neutral pH lower surface with higher nagative potential, Catalyst surface forms the region of rich proton so that absorbability and catalytic decomposition ability to hydrogen peroxide improve, thus play Purifying organic polluted water or the function of soil.
The present invention strictly controls the proportioning of clay mineral, iron oxides and nonferrous metal oxides, and by a large amount of Experimental verification clay mineral, the content of iron oxides, the selection of nonferrous metal element and addition etc. are for catalyst performance Impact, finally draws the magnetic heterogeneous class fenton catalyst of the present invention.
Synthesis technique of the present invention is simple, and equipment requirements is low, with low cost, and catalyst eco-compatibility is good;Use catalyst Carry out heterogeneous class Fenton's reaction and can efficiently remove the organic pollution in environment in wide pH scope, react non-secondary pollution, Economically feasible, the difficult degradation toxic organic pollutant process field at waste water and soil has broad application prospects.
Detailed description of the invention
Below in conjunction with specific embodiment, the present invention is described in detail.
The catalysis activity experiment measuring by degradation of phenol.Phenol concentration employing chromatograph of liquid (HPLC-2010A, Shimadzu) measure, total organic carbon employing total organic carbon analyzer (TOC-V-TN analyzer, multi N/C 3000, Analytic Jena, Germany) measure.
Embodiment 1
(1) clean Kaolin is added in ferrous sulfate and ferrum sulfuricum oxydatum solutum, by iron oxides and kaolinic reason Opinion mass ratio is 0.05, ferrous sulfate and iron sulfate mol ratio are 0.3, total iron content is that 0.1 mol/L carries out iron salt solutions Preparation.Suspension is warmed up to 60 DEG C and continuously stirred 0.5 hour reach stable;
(2) adding the sodium hydroxide of 5 mol/L in suspension makes solution ph rise to 8, continuously stirred 0.5 hour; The processes such as solid precipitation is scrubbed, dry obtain Precursor Powder;
(3), during Precursor Powder impregnated in the manganese nitrate aqueous solution of 0.05 mol/L, wherein manganese is 0.1 with the mol ratio of ferrum, Agitating solution is also evaporated, and dried mixed-powder is placed in air atmosphere, is warmed up in 200 DEG C of air at heat with 1 DEG C/min Manage 1 hour, efficient class Fenton magnetic catalyst can be obtained.
(4) above-mentioned catalyst treatment is contained the wastewater test performance of phenol.It is 100 mg/litre, initial pH at initial concentration It is that the phenol solution of 4.5 adds the catalyst of 0.1 grams per liter and the hydrogen peroxide of 30 mM/ls, after stirring reaction 30 minutes, Phenol concentration declines 80%, and total organic carbon declines 50%.Use Magneto separate reclaim catalyst and recycle three times, be finally catalyzed Activity is more than the 90% of first use activity.
Embodiment 2
(1) clean bentonite is added in ferrous chloride and ferric chloride solution, by iron oxides and kaolinic reason Opinion mass ratio is 2, ferrous chloride and iron chloride mol ratio are 3, total iron content is the preparation that 5 mol/L carry out iron salt solutions.Outstanding Turbid liquid is warmed up to 100 DEG C and continuously stirred 5 hours reach stable;
(2) adding the sodium hydroxide of 2 mol/L in suspension makes solution ph rise to 11, continuously stirred 6 hours; The processes such as solid precipitation is scrubbed, dry obtain Precursor Powder;
(3) during Precursor Powder impregnated in the copper nitrate aqueous solution of 2 mol/L, wherein copper is 1 with the mol ratio of ferrum, stirring Solution is also evaporated, and dried mixed-powder is placed in air atmosphere, is warmed up to heat treatment 48 in 600 DEG C of air with 20 DEG C/min Hour, efficient class Fenton magnetic catalyst can be obtained.
(4) catalyst treatment test performance of waste water containing phenol: initial concentration be 50 mg/litre, initial pH be 5 Phenol solution adds the catalyst of 1 grams per liter and the hydrogen peroxide of 50 mM/ls, after stirring reaction 60 minutes, under phenol concentration Fall 92%, total organic carbon declines 60%.Using Magneto separate reclaim catalyst and recycle three times, final catalysis activity is first Use more than the 95% of activity.
Embodiment 3
(1) clean illite is added in ferrous chloride and ferrum sulfuricum oxydatum solutum, by iron oxides and kaolinic reason Opinion mass ratio is 1, ferrous chloride and iron sulfate mol ratio are 2, total iron content is the preparation that 1 mol/L carries out iron salt solutions.Outstanding Turbid liquid is warmed up to 80 DEG C and continuously stirred 2 hours reach stable;
(2) adding the sodium hydroxide of 1 mol/L in suspension makes solution ph rise to 9, continuously stirred 2 hours;Gu The processes such as body precipitation is scrubbed, dry obtain Precursor Powder;
(3) during Precursor Powder impregnated in copper nitrate and the aluminum nitrate aqueous solution of 1 mol/L, Qi Zhongtong: aluminum: ferrum mole Ratio is 1:1:5, and agitating solution is also evaporated, and dried mixed-powder is placed in air atmosphere, is warmed up to 450 DEG C with 10 DEG C/min Heat treatment 24 hours in air, can obtain efficient class Fenton magnetic catalyst.
(4) catalyst treatment test performance of waste water containing phenol: initial concentration be 60 mg/litre, initial pH be 4.8 Phenol solution in add the catalyst of 0.5 grams per liter and the hydrogen peroxide of 40 mM/ls, after stirring reaction 30 minutes, phenol is dense Degree decline 96%, total organic carbon declines 70%.Using Magneto separate reclaim catalyst and recycle three times, final catalysis activity is More than the 96% of first use activity.
Embodiment 4
(1) clean bentonite is added in ferrous chloride and ferric chloride solution, by iron oxides and kaolinic reason Opinion mass ratio is 0.5, ferrous chloride and iron chloride mol ratio are 1, total iron content is that 0.5 mol/L carries out joining of iron salt solutions System.Suspension is warmed up to 90 DEG C and continuously stirred 3 hours reach stable;
(2) adding the sodium hydroxide of 3 mol/L in suspension makes solution ph rise to 10, continuously stirred 2 hours; The processes such as solid precipitation is scrubbed, dry obtain Precursor Powder;
(3) during Precursor Powder impregnated in the alcoholic solution of nitrification cobalt hexamine complex of 2 mol/L, wherein cobalt and ferrum Mol ratio is 0.5, and agitating solution is also evaporated, and dried mixed-powder is placed in air atmosphere, is warmed up to 500 with 5 DEG C/min In DEG C air, heat treatment 12 hours, can obtain efficient class Fenton magnetic catalyst.
(4) catalyst treatment test performance of waste water containing phenol: initial concentration be 100 mg/litre, initial pH be 6 Phenol solution in add the catalyst of 0.5 grams per liter and the hydrogen peroxide of 30 mM/ls, after stirring reaction 20 minutes, phenol is dense Degree decline 99%, total organic carbon declines 70%.Using Magneto separate reclaim catalyst and recycle three times, final catalysis activity is More than the 98% of first use activity.
The above-mentioned description to embodiment is to be understood that for ease of those skilled in the art and use invention. These embodiments obviously easily can be made various amendment by person skilled in the art, and described herein typically Principle is applied in other embodiments without through performing creative labour.Therefore, the invention is not restricted to above-described embodiment, ability Field technique personnel should be the present invention's according to the announcement of the present invention, the improvement made without departing from scope and amendment Within protection domain.

Claims (8)

1. an efficient class Fenton magnetic catalyst based on clay mineral, it is characterised in that include clay mineral, magnetic ferrite Compound and other metal-oxide, wherein magnetic iron oxide is 0.05-2 with the mass ratio of clay mineral, other metal oxygen The mol ratio of compound and magnetic iron oxide is 0.1-1, other described metal-oxide be manganese metal, cobalt, aluminum, copper, zirconium or One or both oxides in tungsten.
A kind of efficient class Fenton magnetic catalyst based on clay mineral the most according to claim 1, it is characterised in that institute The clay mineral stated has layer structure, one or both the combination in bentonite, illite or montmorillonite.
3. a preparation method for efficient class Fenton magnetic catalyst based on clay mineral as claimed in claim 1, it is special Levy and be, comprise the following steps:
(1) clean clay mineral is added in the iron salt solutions prepared in advance, makes mixed suspension be warmed up to 60- Reach stable for 100 DEG C and continuously stirred 0.5-5 hour;
(2) adding alkali liquor in suspension makes solution ph rise to 8-11, and continuously stirred 0.5-6 hour, solid precipitation was through washing The process such as wash, be dried obtains Precursor Powder;
(3) during Precursor Powder impregnated in the solution containing other slaine, uniformly it is evaporated, heat treatment, i.e. obtains based on clay mineral Efficient class Fenton magnetic catalyst.
The preparation method of efficient class Fenton magnetic catalyst based on clay mineral the most according to claim 3, its feature Being, described iron salt is the mixture of any solubility divalent iron salt or bivalence and trivalent iron salt, wherein preferably ferrous iron with Ferric iron mol ratio is 0.3-3, and total concentration of iron is 0.1-5 mol/L.
The preparation method of efficient class Fenton magnetic catalyst based on clay mineral the most according to claim 3, its feature Being, other slaine described is one or both the water solublity in metallic element manganese, cobalt, aluminum, copper, zirconium or tungsten or alcohol-soluble Salt, the most preferably nitrate, sulfate, hydrochlorate or the complex containing ammonium root, the molar concentration of other slaine is 0.05- 2 mol/L, other metallic element is 0.1-1 with the mol ratio of ferrum.
The preparation method of efficient class Fenton magnetic catalyst based on clay mineral the most according to claim 3, its feature Be, described in be evaporated into less than 100 DEG C heating evaporation operate.
The preparation method of efficient class Fenton magnetic catalyst based on clay mineral the most according to claim 3, its feature Being, the heating rate of described heat treatment is 1-20 DEG C/min, and the temperature of heat treatment is 200-600 DEG C, and the time of heat treatment is 1-48 hour, the atmosphere of heat treatment was air.
8. an application for efficient class Fenton magnetic catalyst based on clay mineral as claimed in claim 1, its feature exists In, described based on clay mineral efficient class Fenton magnetic catalyst can be used for efficient catalytic and decomposes hydrogen peroxide generation class Fenton Poisonous persistent organic pollutants in water or soil are decomposed and are removed, can be recycled by Magneto separate simultaneously by reaction.
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CN106495369A (en) * 2016-12-05 2017-03-15 中国农业科学院农业环境与可持续发展研究所 The method and apparatus that a kind of electro-fenton process processes organic wastewater
CN106809921A (en) * 2017-01-17 2017-06-09 广西大学 A kind of preparation method of kaolinite soil matrix three dimensional particles electrode
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CN113713770A (en) * 2021-09-08 2021-11-30 江西省科学院微生物研究所 Composite adsorption material, preparation method and application thereof, and recycling method of composite adsorption material
CN113976117A (en) * 2021-10-28 2022-01-28 南京大学 Preparation method and application of zero-valent aluminum/iron-containing clay composite material for catalyzing persulfate to oxidize organic matters
CN113976140A (en) * 2021-11-23 2022-01-28 山东华城城建设计工程有限公司 Heterogeneous Fenton-like catalyst and preparation method thereof

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