CN110404543A - The VOC catalyst and preparation method thereof that metal composite oxide and ferroso-ferric oxide ordered arrangement are characterized - Google Patents

The VOC catalyst and preparation method thereof that metal composite oxide and ferroso-ferric oxide ordered arrangement are characterized Download PDF

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CN110404543A
CN110404543A CN201910627336.3A CN201910627336A CN110404543A CN 110404543 A CN110404543 A CN 110404543A CN 201910627336 A CN201910627336 A CN 201910627336A CN 110404543 A CN110404543 A CN 110404543A
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metal composite
ferroso
composite oxide
reagent
electroplating sludge
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CN110404543B (en
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张佳
黄文忠
顾焱
崔耀文
吴健忠
钱光人
周吉峙
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University of Shanghai for Science and Technology
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/864Removing carbon monoxide or hydrocarbons
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8678Removing components of undefined structure
    • B01D53/8687Organic components
    • 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
    • B01J23/755Nickel
    • 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
    • B01J23/85Chromium, molybdenum or tungsten
    • B01J23/86Chromium
    • B01J23/862Iron and chromium
    • 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
    • B01J35/40Catalysts, in general, characterised by their form or physical properties characterised by dimensions, e.g. grain size
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/008Sludge treatment by fixation or solidification
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/10Treatment of sludge; Devices therefor by pyrolysis
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/70Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
    • B01D2257/708Volatile organic compounds V.O.C.'s
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/16Nature of the water, waste water, sewage or sludge to be treated from metallurgical processes, i.e. from the production, refining or treatment of metals, e.g. galvanic wastes

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Electroplating And Plating Baths Therefor (AREA)
  • Catalysts (AREA)
  • Compounds Of Iron (AREA)

Abstract

A kind of VOC catalyst and preparation method thereof that metal composite oxide is characterized with ferroso-ferric oxide ordered arrangement.The present invention is using electroplating sludge as synthetic material, in acidic environment down conversion temperature, pressure, the metallic element dissolution calcined in electroplating sludge under air and the nitrogen alternately atmosphere of variation sufficiently reacts into solution, forms the nano material of stable metal composite oxide and ferroso-ferric oxide ordered arrangement.The processing method minimizing that this method compares traditional electroplating sludge is obvious, and Leaching is extremely low;Calcination time is shorter, and temperature is lower, relatively large number of saving energy consumption;The amount of consumed metal salt reduces nearly half, it is reacted in acid condition, the metal ion for being easy to leach loss can be made sufficiently to react, in addition process flow is relatively simple, and reaction condition is more mild, the treatment process as hazardous solid waste, while guaranteeing innoxious, minimizing is obvious, and resource therein is greatly utilized, and reduces enterprise operation cost.

Description

The VOC catalyst that metal composite oxide and ferroso-ferric oxide ordered arrangement are characterized And preparation method thereof
Technical field
It is special the present invention relates to a kind of synthesized with electroplating sludge with metal composite oxide and ferroso-ferric oxide ordered arrangement VOC catalyst of sign and preparation method thereof belongs to solid waste control technology field.
Background technique
Electroplating sludge is the emission for being handled in plating production process the waste water containing heavy metal and being generated.Plating, Electronics industry generates a large amount of Cu, Ni, Cr, Fe, and due to electroplate technology, plating piece type, the difference of waste water treatment process is each Variant, composition is sufficiently complex.
Final state object of the electroplating sludge as electroplating wastewater, although its amount much less than waste water, due in waste water The heavy metals such as Cu, Ni, Cr, Zn, Fe are shifted and are enriched in sludge, in a sense, harm of the electroplating sludge to environment It is more serious than electroplating wastewater.If not making any disposition to the great electroplating sludge of this harmfulness, ecological environment is broken It badly will be even more serious.On the other hand, it if the heavy metal substance high to grade in electroplating sludge is not recycled, also anticipates Taste the huge waste of resource.
The characteristics of for electroplating sludge and its harmfulness, from the point of view of environmental pollution prevention and control and resource circulation utilization, Following two processing mode is mainly used, first is that after treatment, making sludge not cause secondary pollution and abandon and store, i.e., Harmlessness disposing;Second is that making to carry out synthetical recovery, i.e. resource utilization to the heavy metal resources in sludge.
The recycling treatment of electroplating sludge is broadly divided into solution leaching beneficiation technologies, and Ferrite method is handled, at composting organisms Three kinds of reason, the above two need to add a large amount of medicament, and compost then occupies biggish space, and resource utilization is relatively low in preceding two Person.Therefore it is badly in need of a kind of method of inexpensive high usage, while minimizing that electroplating sludge is innoxious, to greatest extent Utilize resource therein.
Summary of the invention
One of the objects of the present invention is to provide a kind of metal composite oxides and ferroso-ferric oxide ordered arrangement to be characterized VOC catalyst.
The second object of the present invention is to provide what the metal composite oxide was characterized with ferroso-ferric oxide ordered arrangement The preparation method of VOC catalyst.
In order to achieve the above objectives, the present invention adopts the following technical scheme:
A kind of VOC catalyst that metal composite oxide is characterized with ferroso-ferric oxide ordered arrangement, it is characterised in that the catalysis The structure of agent are as follows: the metal composite oxide and the equally distributed nano material of ferroso-ferric oxide of spinel structure, composition metal The particle size of oxide is between 200-500nm, and the particle size of ferroso-ferric oxide is between 20-90nm, wherein four oxidations Three weight of iron accountings are the 5~20% of totality.
A kind of side preparing the VOC catalyst that above-mentioned metal composite oxide and ferroso-ferric oxide ordered arrangement are characterized Method, it is characterised in that:
A. by 0.2~0.25mol/L glacial acetic acid solution, 0.1~0.2mol/L citric acid solution according to 1:1~1:1.5 volume Than being mixed and made into reagent a;Again by 0.025~-0.05mol/L potassium sodium tartrate solution and 0.01~0.02mol/L ethylenediamine tetraacetic Acetic acid solution is mixed and made into reagent b according to the volume ratio between 1:1~1:2;Again by the reagent a and the reagent b according to 1: The volume ratio of 0.2~1:0.5 uniformly mixes, and dehydrated alcohol is added after mixing, and dehydrated alcohol volume is less than mixed liquor volume 2%, structure-forming agent is made;
B. electroplating sludge and step a resulting structures forming agent mixed according to the ratio of solid-to-liquid ratio 1g:10ml~1g:12ml and, Prepare metal composite oxide idiosome;
C. 0.1-0.15mol/L sodium carbonate liquor, 0.05-0.075mol/L sodium sulfite solution, by above two solution are prepared Reagent c is mixed and made into according to the volume ratio of 1:0.2~1:0.5;
D. a kind of iron content electroplating sludge is taken, metal member of the iron content therein in 20g/100g or more, in addition to iron and calcium Cellulose content in 10g/100g hereinafter, later by reagent c obtained by the iron content electroplating sludge and step c according to solid-to-liquid ratio 1g:7.5ml~ The ratio of 1g:10ml mixes, and is cooled to room temperature after being stirred and heated to 80~100 DEG C of heat preservations 30~45 minutes, and crystal form guiding is made Agent;
E. by crystal form directed agents obtained by metal composite oxide idiosome obtained by step b and step d according to 1:1.5g~1:1.75g's Ratio uniform mixing is warming up to 190 DEG C~220 DEG C under the atmosphere of the air under the pressure of 120-150KPa and calcines 60~90 points Clock is warming up to 400~450 DEG C later and calcines 60~90 minutes under nitrogen atmosphere under normal pressure, heating rate controls when calcining In 1~5 DEG C/min, the VOC catalyst that metal composite oxide and ferroso-ferric oxide ordered arrangement are characterized is obtained after cooling.
The present invention compared with prior art, has obvious prominent substantive distinguishing features and remarkable advantage:
(1) general curing/stabilizing technology is compared, the minimizing of this technique is obvious, and Leaching is extremely low;
(2) general heat treatment technics is compared, the control of this technique calcination temperature is at 450 DEG C hereinafter, calcination time is shorter, relatively More saving energy consumptions;
(3) various electroplating sludge Ferrite method technologies are compared, the amount of metal salt consumed by this technique reduces nearly half, in acidity Under the conditions of reacted, can make be easy leach be lost metal ion sufficiently react, in addition process flow is relatively simple, Reaction condition is more mild;
It can be seen that the present invention has breakthrough advantage, it is innoxious in guarantee as the treatment process of hazardous solid waste Meanwhile minimizing is obvious, and resource therein is greatly utilized, and reduces enterprise operation cost.
Detailed description of the invention
Fig. 1: the XRD characterization figure of material synthesized by embodiment 1.
Fig. 2: material synthesized by embodiment 1 is to the catalytic effect diagram of toluene, and toluene concentration is 1000ppm, air speed in figure GHSV=9600h-1
Specific embodiment
Embodiment 1
A method of metal composite oxide being synthesized using chromium containing electroplating sludge, wherein the content of Cr element is 25.40g/ 100g, iron content electroplating sludge iron content are 23.16 g/100g, are comprised the following steps that
A. 0.2mol/L glacial acetic acid solution and 0.1mol/L citric acid solution are prepared, both solution 1:1 is mixed, is mixed Reagent a, then 0.025mol/L potassium sodium tartrate solution and 0.01mol/L edta solution are prepared, according to the ratio of 1:2 It is mixed and made into reagent b, inwardly adds dehydrated alcohol later, structure-forming agent is made.
B. 5g chromium containing electroplating sludge is taken, is mixed with the structure-forming agent of 50ml, metal composite oxide idiosome is prepared.
C. 7.5g iron content electroplating sludge is weighed, and prepares 0.125mol/L sodium carbonate liquor, 0.05mol/L sodium sulfite is molten Above two solution is mixed and made into reagent c according to the ratio of 1:0.25 by liquid, by the reagent of this iron content electroplating sludge and 57ml C mixing, is cooled to room temperature after being stirred and heated to 100 DEG C, crystal form directed agents is made.
D. it takes the idiosome of 20ml uniformly to mix with the crystal form directed agents of 35ml, mixed slurries is placed in transformation program liter In warm device, 200 DEG C of calcinings 90 minutes are warming up under the atmosphere of the air under the pressure of 140KPa, later nitrogen under normal pressure Atmosphere is warming up to 450 DEG C and calcines 90 minutes under enclosing, heating rate is 2 DEG C/min when calcining, and electroplating sludge solidification is obtained after cooling Object.
Embodiment 2
A method of metal composite oxide being synthesized using nickeliferous electroplating sludge, wherein the content of Ni element is 24.18g/ 100g, iron content electroplating sludge iron content are 23.16 g/100g, are comprised the following steps that
A. 0.25mol/L glacial acetic acid solution and 0.1mol/L citric acid solution are prepared, both solution 1:1.5 is mixed, mixing Reagent a is made, then prepares 0.04mol/L potassium sodium tartrate solution and 0.02mol/L edta solution, according to 1:1's Ratio is mixed and made into reagent b, inwardly adds dehydrated alcohol later, structure-forming agent is made.
B. 10g copper-contained electroplating sludge is taken, is mixed with the structure-forming agent of 100ml, metal composite oxide idiosome is prepared.
C. 15g iron content electroplating sludge is weighed, and prepares 0.75mol/L sodium carbonate liquor, 0.05mol/L sodium sulfite is molten Above two solution is mixed and made into reagent c according to the ratio of 1:0.4 by liquid, by the examination of this iron content electroplating sludge and 112.5ml Agent c mixing, is cooled to room temperature after being stirred and heated to 80 DEG C, crystal form directed agents is made.
D. it takes the idiosome of 40ml uniformly to mix with the crystal form directed agents of 70ml, mixed slurries is placed in transformation program liter In warm device, 200 DEG C of calcinings 90 minutes are warming up under the atmosphere of the air under the pressure of 120KPa, later nitrogen under normal pressure Atmosphere is warming up to 450 DEG C and calcines 60 minutes under enclosing, heating rate is 5 DEG C/min when calcining, and electroplating sludge solidification is obtained after cooling Object.
Embodiment 3
A method of metal composite oxide being synthesized using copper-contained electroplating sludge, wherein the content of Cu element is 39.84g/ 100g, iron content electroplating sludge iron content are 23.16 g/100g, are comprised the following steps that
A. 0.2mol/L glacial acetic acid solution and 0.1mol/L citric acid solution are prepared, both solution 1:1 is mixed, is mixed Reagent a, then 0.025mol/L potassium sodium tartrate solution and 0.01mol/L edta solution are prepared, according to the ratio of 1:1 It is mixed and made into reagent b, inwardly adds dehydrated alcohol later, structure-forming agent is made.
B. 5g copper-contained electroplating sludge is taken, is mixed with the structure-forming agent of 50ml, metal composite oxide idiosome is prepared.
C. 7.5g iron content electroplating sludge is weighed, and prepares 0.1mol/L sodium carbonate liquor, 0.05mol/L sodium sulfite is molten Above two solution is mixed and made into reagent c according to the ratio of 1:0.2 by liquid, by the reagent c of this iron content electroplating sludge and 57ml Mixing, is cooled to room temperature after being stirred and heated to 80 DEG C, crystal form directed agents is made.
D. it takes the idiosome of 20ml uniformly to mix with the crystal form directed agents of 30ml, mixed slurries is placed in transformation program liter In warm device, 200 DEG C of calcinings 60 minutes are warming up under the atmosphere of the air under the pressure of 120KPa, later nitrogen under normal pressure Atmosphere is warming up to 400 DEG C and calcines 60 minutes under enclosing, heating rate is 5 DEG C/min when calcining, and electroplating sludge solidification is obtained after cooling Object.
The embodiment of the present invention is illustrated above, but the present invention is not limited to the above embodiments, it can also be according to this hair The purpose of bright innovation and creation makes a variety of variations, and that does under the Spirit Essence and principle of all technical solutions according to the present invention changes Become, modification, substitution, combination or simplified, should be equivalent substitute mode, as long as meeting goal of the invention of the invention, as long as not Away from the method and technology principle and inventive concept of electroplating wastewater modified activated carbon of the present invention, protection scope of the present invention is belonged to.

Claims (2)

1. the VOC catalyst that a kind of metal composite oxide and ferroso-ferric oxide ordered arrangement are characterized, it is characterised in that this is urged The structure of agent are as follows: the metal composite oxide and the equally distributed nano material of ferroso-ferric oxide of spinel structure, compound gold Belong to the particle size of oxide between 200-500nm, the particle size of ferroso-ferric oxide is between 20-90nm, wherein four oxygen Changing three weight of iron accountings is overall 5-20%.
2. a kind of prepare what metal composite oxide according to claim 1 was characterized with ferroso-ferric oxide ordered arrangement The method of VOC catalyst, it is characterised in that:
A. by 0.2~0.25mol/L glacial acetic acid solution, 0.1~0.2mol/L citric acid solution according to 1:1~1:1.5 volume Than being mixed and made into reagent a;Again by 0.025~-0.05mol/L potassium sodium tartrate solution and 0.01~0.02mol/L ethylenediamine tetraacetic Acetic acid solution is mixed and made into reagent b according to the volume ratio between 1:1~1:2;Again by the reagent a and the reagent b according to 1: The volume ratio of 0.2~1:0.5 uniformly mixes, and dehydrated alcohol is added after mixing, and dehydrated alcohol volume is less than mixed liquor volume 2%, structure-forming agent is made;
B. electroplating sludge and step a resulting structures forming agent mixed according to the ratio of solid-to-liquid ratio 1g:10ml~1g:12ml and, Prepare metal composite oxide idiosome;
C. 0.1-0.15mol/L sodium carbonate liquor, 0.05-0.075mol/L sodium sulfite solution, by above two solution are prepared Reagent c is mixed and made into according to the volume ratio of 1:0.2~1:0.5;
D. a kind of iron content electroplating sludge is taken, metal member of the iron content therein in 20g/100g or more, in addition to iron and calcium Cellulose content in 10g/100g hereinafter, later by reagent c obtained by the iron content electroplating sludge and step c according to solid-to-liquid ratio 1g:7.5ml~ The ratio of 1g:10ml mixes, and is stirred and heated to 80~100 DEG C of heat preservations 30~be cooled to room temperature after forty minutes, crystal form guiding is made Agent;
E. by crystal form directed agents obtained by metal composite oxide idiosome obtained by step b and step d according to 1:1.5g~1:1.75g's Ratio uniform mixing is warming up to 190 DEG C~220 DEG C under the atmosphere of the air under the pressure of 120-150KPa and calcines 60~90 points Clock is warming up to 400~450 DEG C later and calcines 60~90 minutes under nitrogen atmosphere under normal pressure, heating rate controls when calcining In 1~5 DEG C/min, the VOC catalyst that metal composite oxide and ferroso-ferric oxide ordered arrangement are characterized is obtained after cooling.
CN201910627336.3A 2019-07-12 2019-07-12 VOC catalyst with characteristic of ordered arrangement of composite metal oxide and ferroferric oxide and preparation method thereof Active CN110404543B (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112958110A (en) * 2021-02-26 2021-06-15 上海大学材料基因组工程(萍乡)研究院 Method for preparing efficient VOC catalyst by step-by-step activation method

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101722004A (en) * 2009-10-15 2010-06-09 清华大学 CrXCo3-XO4 spinel type catalyst and preparation method thereof
CN103950987A (en) * 2014-04-11 2014-07-30 南京理工大学 Recycling method of pickling sludge
CN104549301A (en) * 2013-10-13 2015-04-29 西北大学 Synthesis method of Fe2O3@MFe2O4 with kernel-shell structure
JP2016087587A (en) * 2014-11-10 2016-05-23 トヨタ自動車株式会社 EXHAUST GAS PURIFYING CATALYST FOR NOx SELECTIVE REDUCTION AND EXHAUST GAS PURIFYING METHOD
CN108295866A (en) * 2018-03-21 2018-07-20 大连理工大学 A kind of nano flower spinelle CoMn for VOCs catalysis oxidations2O4Catalyst, preparation method and application
CN109046446A (en) * 2018-08-30 2018-12-21 河北科技大学 A kind of metal oxide/HTS-1 titanium-silicon molecular sieve catalyst and its preparation method and application
CN109894124A (en) * 2017-12-08 2019-06-18 中国科学院上海硅酸盐研究所 A kind of copper mangenese spinel oxide and its preparation method and application

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101722004A (en) * 2009-10-15 2010-06-09 清华大学 CrXCo3-XO4 spinel type catalyst and preparation method thereof
CN104549301A (en) * 2013-10-13 2015-04-29 西北大学 Synthesis method of Fe2O3@MFe2O4 with kernel-shell structure
CN103950987A (en) * 2014-04-11 2014-07-30 南京理工大学 Recycling method of pickling sludge
JP2016087587A (en) * 2014-11-10 2016-05-23 トヨタ自動車株式会社 EXHAUST GAS PURIFYING CATALYST FOR NOx SELECTIVE REDUCTION AND EXHAUST GAS PURIFYING METHOD
CN109894124A (en) * 2017-12-08 2019-06-18 中国科学院上海硅酸盐研究所 A kind of copper mangenese spinel oxide and its preparation method and application
CN108295866A (en) * 2018-03-21 2018-07-20 大连理工大学 A kind of nano flower spinelle CoMn for VOCs catalysis oxidations2O4Catalyst, preparation method and application
CN109046446A (en) * 2018-08-30 2018-12-21 河北科技大学 A kind of metal oxide/HTS-1 titanium-silicon molecular sieve catalyst and its preparation method and application

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
王永强等: ""尖晶石型AFe2O4催化剂的制备及其催化燃烧甲苯的研究"", 《无机材料学报》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112958110A (en) * 2021-02-26 2021-06-15 上海大学材料基因组工程(萍乡)研究院 Method for preparing efficient VOC catalyst by step-by-step activation method
CN112958110B (en) * 2021-02-26 2022-09-06 上海大学材料基因组工程(萍乡)研究院 Method for preparing efficient VOC catalyst by step-by-step activation method

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