CN104549231B - A kind of preparation method of catalyst of catalytic decomposition garbage incinerating tail gas Zhong bioxin - Google Patents

A kind of preparation method of catalyst of catalytic decomposition garbage incinerating tail gas Zhong bioxin Download PDF

Info

Publication number
CN104549231B
CN104549231B CN201510053040.7A CN201510053040A CN104549231B CN 104549231 B CN104549231 B CN 104549231B CN 201510053040 A CN201510053040 A CN 201510053040A CN 104549231 B CN104549231 B CN 104549231B
Authority
CN
China
Prior art keywords
catalyst
preparation
bioxin
tail gas
honeycomb
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN201510053040.7A
Other languages
Chinese (zh)
Other versions
CN104549231A (en
Inventor
王国忠
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Wang Guozhong
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to CN201510053040.7A priority Critical patent/CN104549231B/en
Publication of CN104549231A publication Critical patent/CN104549231A/en
Application granted granted Critical
Publication of CN104549231B publication Critical patent/CN104549231B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/30Capture or disposal of greenhouse gases of perfluorocarbons [PFC], hydrofluorocarbons [HFC] or sulfur hexafluoride [SF6]

Abstract

The invention discloses the Catalysts and its preparation method producing bioxin in a kind of catalytic degradation garbage incinerating tail gas, adopt extrinsion pressing to prepare honeycomb type catalyst, then carry out obtained by drying and activation.Catalyst is main carriers with CNT, with VOx, WOx, MnOx, TiO 2for main active catalytic component, this catalyst is vanadium-tungsten-manganese-titanium catalyst system.This catalyst is applicable to the catalytic cracking reaction of dioxins materials.Catalyst of the present invention, improves the specific area of catalyst effectively, improves the activity of catalyst, and enhances the intensity of catalyst.

Description

A kind of preparation method of catalyst of catalytic decomposition garbage incinerating tail gas Zhong bioxin
Technical field
The present invention relates to the manufacture method producing the catalyst of bioxin in a kind of catalytic decomposition garbage incinerating tail gas.
Background technology
The removal technology of current , bioxin has following several: high-temperature process (high-temp combustion, motlten metal pyrolytic, molten salt oxidation, pyrolytic etc.); Oxidation non-burning technology (catalytic oxidation, supercritical water oxidation, electrochemical oxidation etc.); Reduction technique (carrier catalysis degradation process, metal and metal oxide oxidation catalyst, ball milling, sodium reduction etc.); Photocatalyst (sunshine is degraded, photochemical degradating, UV degradation, photocatalysis), biodegradation etc.
The method of conventional removal bioxin is as follows: utilize at monoblock reactor and divest N0x catalytic elimination/oxidation; Catalytic elimination and degraded is carried out at catalytic filter; Carbon fibre, compression bed or moving bed use active carbon to remove or fluidization technique; Adsorb comprising on the compression bed detesting water zeolite, sepiolite or carbon micro-nano mitron; Wet-cleaned is carried out with acid or alkali; Carry out half-dried cleaning fluid with pulverized limestone and can remove a part of bioxin.
Utilize catalysis technique process bioxin to be a kind of newer method, allow the flue gas containing bioxin flow in Catalytic Layer, bioxin can be oxidized by oxygen at low temperatures, generate CO 2, the inorganic harmless object such as water and HCl.Catalyst mostly is titanium oxide and carries the noble metal catalyst such as the transition-metal catalysts such as vanadium, tungsten, molybdenum and year gold, palladium, the platinum such as silica gel, active carbon.
Be a technology being proved to be feasible to the catalytic oxidation of the PCDD/Fs in flue gas, the PCDD/Fs concentration in flue gas can be reduced to lower than 0.1 ng TEQ/Nm by it 3, Hagenmaier and people such as grade prove TiO 2for the V of carrier 2o 5/ WO 3it is highly effective at the same temperature that catalyst removes nitrogen oxide (NOx) through SCR (SCR), and main cause is that they can be oxidized PCDD/Fs and become oxycarbide, water and hydrogen chloride.
Summary of the invention
The invention provides a kind of hydrogenation catalyst, compared with prior art in this catalyst, activity component load quantity is low, and has the catalytic activity of catalyst known in the state of the art.
Technical scheme of the present invention realizes by the following method:
A) take the ammonium metavanadate of 125g respectively, the ammonium metatungstate of 250g, the titanium sulfate of 130g, the manganese nitrate of 130g, the Ludox of 800-1200g, constantly stir at the temperature of 25 DEG C, be dissolved in the deionized water of 1000ml;
B) CNT is put in the mixed solution of red fuming nitric acid (RFNA) and hydrofluoric acid, high pressure hydration under ar gas environment, maintain 10-15 hour at 120-150 DEG C after, be cooled to room temperature, then take out CNT and spend deionized water filtration, for subsequent use;
C) step b) taking 2000g cleans CNT for subsequent use, the activated clay of 50g and the tung oil of 40g, and add in the solution that step a) configures, import in mixing roll and carry out uniform stirring, mixing time is 0.5-1.5h;
Obtain pottery pureed blank, add in hydraulic press, extruded, obtained aperture is the honeycomb catalyst of 1mm;
D) by step c) obtained honeycomb type catalyst is immersed in 4, in the acetone soln of 4 '-methyl diphenylene diisocyanate, then a small amount of 2 are added, 4-dichlorobenzoperoxide, 1-METHYLPYRROLIDONE, flavonols, trimethylhexamethylenediamine, 50 DEG C are soaked 4-16 hour, then filter out honeycomb type catalyst, replace washing 4 times with deionized water and ethanol;
E) by steps d) clean honeycomb type catalyst is placed in micro-wave oven and heats at air atmosphere, and the moisture making it remove a part is hardening, and the power of micro-wave oven is 1500W;
F) by step e) in obtained dried honeycomb catalyst carry out the cutting of physics, obtain long 10mm, diameter is the small-sized honeycomb catalyst of 20mm, then being placed in internal diameter is 21mm, length is in the quartz reactor of 750mm, quartz reactor is placed in the isothermal reaction stove that internal diameter is 35mm, under oxygen atmosphere, progressively be warming up to 550 DEG C, heating rate need control at 10-20 DEG C/minute, carry out the activation of catalyst, soak time is 0.5h-1h, thus produces the catalyst of bioxin in obtained catalytic degradation garbage incinerating tail gas.
The BET specific surface area of obtained catalyst is 800-1000 m 2/ g.
The pore volume of obtained catalyst is 0.1-0.3cm 3/ g, aperture is 50-150.
Obtained catalyst is at the temperature of 250 DEG C, and 10000h -1air speed under, the catalysis degradation modulus of Dui bioxin is 99.9%.
beneficial effect of the present invention
(1) catalyst of the present invention is vanadium-tungsten-manganese-titanium System Catalyst, is HCl and SO wherein to waste incineration 2there is good anti-toxic effects;
(2) honeycomb catalyst and add carbon nanotube powder, there is good adaptive capacity in the duct of its rule to the impurity in tail gas, increases specific area simultaneously, improves the activity of catalyst, under high-speed, reaction rate is also higher, can reduce the cost of catalyst; Greatly improve the intensity of catalyst, be easier to realize industrialization, advantage is more obvious in actual applications simultaneously.
(3) CNT is immersed in 4, in 4 '-methyl diphenylene diisocyanate, the carrier of catalyst defines one deck overlay film, improve the resistance to elevated temperatures of catalyst carrier and the bulk strength of active component and carrier.2, a small amount of interpolation of 4-dichlorobenzoperoxide, 1-METHYLPYRROLIDONE, flavonols, trimethylhexamethylenediamine, achieve and introduce active function groups in carbon nano tube surface, improve the catalytic activity of catalyst and the selective of Dui bioxin, create synergy simultaneously, improve the ageing resistace of carrier.The absorption property of catalyst significantly promotes simultaneously, and the BET specific surface area of obtained catalyst reaches 800-1000 m 2/ g, is much higher than the absorption property of existing catalyst.
(4) experimental result shows, catalyst of the present invention is at the temperature of 250 DEG C, and 10000h -1air speed (SV) under, the catalysis degradation modulus of its Dui bioxin is 99.9%.
Detailed description of the invention
embodiment 1
A) take the ammonium metavanadate of 125g respectively, the ammonium metatungstate of 250g, the titanium sulfate of 130g, the manganese nitrate of 130g, the Ludox of 800-1200g, constantly stir at the temperature of 25 DEG C, be dissolved in the deionized water of 1000ml;
B) CNT is put in the mixed solution of red fuming nitric acid (RFNA) and hydrofluoric acid, high pressure hydration under ar gas environment, maintain 10-15 hour at 120-150 DEG C after, be cooled to room temperature, then take out CNT and spend deionized water filtration, for subsequent use;
C) step b) taking 2000g cleans CNT for subsequent use, the activated clay of 50g and the tung oil of 40g, and add in the solution that step a) configures, import in mixing roll and carry out uniform stirring, mixing time is 0.5-1.5h;
Obtain pottery pureed blank, add in hydraulic press, extruded, obtained aperture is the honeycomb catalyst of 1mm;
D) by step c) obtained honeycomb type catalyst is immersed in 4, in the acetone soln of 4 '-methyl diphenylene diisocyanate, then a small amount of 2 are added, 4-dichlorobenzoperoxide, 1-METHYLPYRROLIDONE, flavonols, trimethylhexamethylenediamine, 50 DEG C are soaked 4-16 hour, then filter out honeycomb type catalyst, replace washing 4 times with deionized water and ethanol;
E) by steps d) clean honeycomb type catalyst is placed in micro-wave oven and heats at air atmosphere, and the moisture making it remove a part is hardening, and the power of micro-wave oven is 1500W;
F) by step e) in obtained dried honeycomb catalyst carry out the cutting of physics, obtain long 10mm, diameter is the small-sized honeycomb catalyst of 20mm, then being placed in internal diameter is 21mm, length is in the quartz reactor of 750mm, quartz reactor is placed in the isothermal reaction stove that internal diameter is 35mm, under oxygen atmosphere, progressively be warming up to 550 DEG C, heating rate need control at 10-20 DEG C/minute, carry out the activation of catalyst, soak time is 0.5h-1h, thus produces the catalyst of bioxin in obtained catalytic degradation garbage incinerating tail gas.
comparative example 1
A) take the ammonium metavanadate of 125g respectively, the ammonium metatungstate of 250g, the titanium sulfate of 130g, the manganese nitrate of 130g, the Ludox of 800-1200g, constantly stir at the temperature of 25 DEG C, be dissolved in the deionized water of 1000ml;
B) take the aluminium oxide of 2000g, the activated clay of 50g and the tung oil of 40g, add in the solution that step a) configures, import in mixing roll and carry out uniform stirring, mixing time is 0.5-1.5h; Obtain pottery pureed blank, add in hydraulic press, extruded, obtained aperture is the honeycomb catalyst of 1mm;
C) by step b) honeycomb type catalyst be placed in micro-wave oven and heat at air atmosphere, the moisture making it remove a part is hardening, and the power of micro-wave oven is 1500W;
D) by step c) in obtained dried honeycomb catalyst carry out the cutting of physics, obtain long 10mm, diameter is the small-sized honeycomb catalyst of 20mm, then being placed in internal diameter is 21mm, length is in the quartz reactor of 750mm, quartz reactor is placed in the isothermal reaction stove that internal diameter is 35mm, under oxygen atmosphere, progressively be warming up to 550 DEG C, heating rate need control at 10-20 DEG C/minute, carry out the activation of catalyst, soak time is 0.5h-1h, thus produces the catalyst of bioxin in obtained catalytic degradation garbage incinerating tail gas.
comparative example 2
A) take the ammonium metavanadate of 125g respectively, the ammonium metatungstate of 250g, the titanium sulfate of 130g, the manganese nitrate of 130g, the Ludox of 800-1200g, constantly stir at the temperature of 25 DEG C, be dissolved in the deionized water of 1000ml;
B) take the silica of 2000g, the activated clay of 50g and the tung oil of 40g, add in the solution that step a) configures, import in mixing roll and carry out uniform stirring, mixing time is 0.5-1.5h; Obtain pottery pureed blank, add in hydraulic press, extruded, obtained aperture is the honeycomb catalyst of 1mm;
C) by step b) honeycomb type catalyst be placed in micro-wave oven and heat at air atmosphere, the moisture making it remove a part is hardening, and the power of micro-wave oven is 1500W;
D) by steps d) in obtained dried honeycomb catalyst carry out the cutting of physics, obtain long 10mm, diameter is the small-sized honeycomb catalyst of 20mm, then being placed in internal diameter is 21mm, length is in the quartz reactor of 750mm, quartz reactor is placed in the isothermal reaction stove that internal diameter is 35mm, under oxygen atmosphere, progressively be warming up to 550 DEG C, heating rate need control at 10-20 DEG C/minute, carry out the activation of catalyst, soak time is 0.5h-1h, thus produces the catalyst of bioxin in obtained catalytic degradation garbage incinerating tail gas.
Produce in the reaction of bioxin by the catalyst application that embodiment 1 and comparative example 1,2 obtain in catalytic degradation garbage incinerating tail gas, catalyst loading amount is 500ml.Be 250 DEG C in reaction temperature, the gas space velocity containing bioxin is 10000h -1, the reaction time is 4h, sample analysis.Result is as table 1.
The test result of bioxin is produced in table 1 catalytic degradation garbage incinerating tail gas
Sample Reaction temperature (DEG C) Reaction time (dividing) Bioxin clearance (%)
Embodiment 1 250 240 99.9
Comparative example 1 250 240 58.9
Comparative example 2 250 240 54.6

Claims (4)

1. the preparation method of the catalyst of bioxin in catalytic degradation garbage incinerating tail gas, it is characterized in that, concrete preparation process is as follows:
A) take the ammonium metavanadate of 125g respectively, the ammonium metatungstate of 250g, the titanium sulfate of 130g, the manganese nitrate of 130g, the Ludox of 800-1200g, constantly stir at the temperature of 25 DEG C, be dissolved in the deionized water of 1000ml;
B) CNT is put in the mixed solution of red fuming nitric acid (RFNA) and hydrofluoric acid, high pressure hydration under ar gas environment, maintain 10-15 hour at about 120-150 DEG C after, be cooled to room temperature, then take out CNT and spend deionized water filtration, for subsequent use;
C) take 2000g step b) and clean CNT for subsequent use, the activated clay of 50g and the tung oil of 40g, add in the solution that step a) configures, import in mixing roll and carry out uniform stirring, mixing time is 0.5-1.5h,
Obtain pottery pureed blank, add in hydraulic press, extruded, obtained aperture is the honeycomb catalyst of 1mm;
D) by step c) obtained honeycomb type catalyst is immersed in 4, in the acetone soln of 4 '-methyl diphenylene diisocyanate, then a small amount of 2 are added, 4-dichlorobenzoperoxide, 1-METHYLPYRROLIDONE, flavonols, trimethylhexamethylenediamine, 50 DEG C are soaked 4-16 hour, then filter out honeycomb type catalyst, replace washing 4 times with deionized water and absolute ethyl alcohol;
E) by steps d) clean honeycomb type catalyst is placed in micro-wave oven and heats at air atmosphere, and the moisture making it remove a part is hardening, and the power of micro-wave oven is 1500W;
F) by step e) in obtained dried honeycomb catalyst carry out the cutting of physics, obtain long 10mm, diameter is the small-sized honeycomb catalyst of 20mm, then being placed in internal diameter is 21mm, length is in the quartz reactor of 750mm, quartz reactor is placed in the isothermal reaction stove that internal diameter is 35mm, under oxygen atmosphere, progressively be warming up to 550 DEG C, heating rate need control at 10-20 DEG C/minute, carry out the activation of catalyst, soak time is 0.5h-1h, thus produces the catalyst of bioxin in obtained catalytic degradation garbage incinerating tail gas.
2. preparation method as claimed in claim 1, is characterized in that: the BET specific surface area of obtained catalyst is 800-1000 m 2/ g.
3. preparation method as claimed in claim 1, is characterized in that: the pore volume of obtained catalyst is 0.1-0.3cm 3/ g, aperture is 50-150.
4. preparation method as claimed in claim 1, is characterized in that: obtained catalyst is at the temperature of 250 DEG C, and 10000h -1air speed under, the catalysis degradation modulus of Dui bioxin is 99.9%.
CN201510053040.7A 2015-02-02 2015-02-02 A kind of preparation method of catalyst of catalytic decomposition garbage incinerating tail gas Zhong bioxin Expired - Fee Related CN104549231B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510053040.7A CN104549231B (en) 2015-02-02 2015-02-02 A kind of preparation method of catalyst of catalytic decomposition garbage incinerating tail gas Zhong bioxin

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510053040.7A CN104549231B (en) 2015-02-02 2015-02-02 A kind of preparation method of catalyst of catalytic decomposition garbage incinerating tail gas Zhong bioxin

Publications (2)

Publication Number Publication Date
CN104549231A CN104549231A (en) 2015-04-29
CN104549231B true CN104549231B (en) 2015-10-28

Family

ID=53066937

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510053040.7A Expired - Fee Related CN104549231B (en) 2015-02-02 2015-02-02 A kind of preparation method of catalyst of catalytic decomposition garbage incinerating tail gas Zhong bioxin

Country Status (1)

Country Link
CN (1) CN104549231B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110479078A (en) * 2019-09-09 2019-11-22 广州派安环保科技有限公司 A kind of production of dioxin restraining agent and technique for applying
CN111185200B (en) * 2020-03-12 2022-08-02 青岛理工大学 Preparation method of hydrogenation catalyst for treating dioxin in garbage gasification tail gas
CN112902193B (en) * 2021-02-23 2022-05-17 山东大学 Garbage incinerator system and catalytic removal method for garbage incineration flue gas purification hearth

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101607203A (en) * 2009-07-16 2009-12-23 浙江大学 Be used to remove the Catalysts and its preparation method of dioxin-type halogenated aromatic compounds

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003080275A (en) * 2001-09-13 2003-03-18 Nippon Shokubai Co Ltd Method for treating organic halogen compound in water

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101607203A (en) * 2009-07-16 2009-12-23 浙江大学 Be used to remove the Catalysts and its preparation method of dioxin-type halogenated aromatic compounds

Also Published As

Publication number Publication date
CN104549231A (en) 2015-04-29

Similar Documents

Publication Publication Date Title
CN100395028C (en) Porous catalytic filtering metal material and its prepn
CN109126773B (en) Catalyst for purifying waste incineration flue gas and preparation method thereof
JP5844457B2 (en) Method for producing surface-deposited honeycomb flue gas denitration catalyst
CN101380574A (en) Catalyst for complete oxidation of formaldehyde at room temperature
CN104549231B (en) A kind of preparation method of catalyst of catalytic decomposition garbage incinerating tail gas Zhong bioxin
CN103736484A (en) Supported integrated catalyst for formaldehyde purification and preparation method thereof
CN103691461A (en) Method for applying gold hydroxyapatite loaded catalyst to catalytic oxidation reaction of formaldehyde at room temperature
CN104415755A (en) Denitration catalyst adopting modified active carbon as matrix material, and preparation method thereof
CN112973785B (en) Catalyst for synergistically removing VOCs and NOx and preparation method thereof
CN106669668A (en) Catalyst for ammonia odor gas purification as well as preparation method and application of catalyst
CN103861581A (en) Perovskite-type substance La<1-x>Sr<x>CrO<3>, heat-engine plant denitration composite catalyst, and preparation methods of perovskite-type substance La<1-x>Sr<x>CrO<3> and heat-engine plant denitration composite catalyst
CN104923213B (en) A kind of nontoxic rare-earth type denitrating catalyst and its preparation method and application
CN106824174A (en) A kind of coccoid catalyst of high-efficient purification nitrogen oxides and preparation method thereof
CN107413350A (en) Mischmetal denitrating catalyst and preparation method thereof
CN104549230B (en) A kind of preparation method of catalyst of catalytic decomposition non-ferrous metal metallurgy Wei gas Zhong bioxin
CN106111124A (en) A kind of denitrating catalyst with modified activated carbon as matrix material and preparation method thereof
BR112019019508A2 (en) catalyst composition, catalytic coating, catalyst article, exhaust system, automotive internal combustion engine, automotive vehicle, and method for treating an exhaust gas.
CN106238070B (en) The regeneration method of regenerated liquid of denitrating catalyst and preparation method thereof and denitrating catalyst
CN101143335B (en) Plasma reactor catalyst and its preparation method and use
CN104415756A (en) Modified active carbon and preparation method thereof
KR100668926B1 (en) Method of regenerating scr catalyst
CN102039129B (en) Honeycomb catalyst for catalytically incinerating sulfur containing gases and preparation method
CN109985663A (en) The method that the Cu-SSZ-13 molecular sieve of a kind of pair of one kettle way fabricated in situ is post-processed
CN110013858B (en) Preparation method of cobaltosic oxide monolithic catalyst for carbon monoxide purification
CN114917753B (en) Use of a support for selectively catalyzing ammonia

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
C41 Transfer of patent application or patent right or utility model
CB03 Change of inventor or designer information

Inventor after: Wang Guozhong

Inventor before: Ye Cheng

COR Change of bibliographic data
GR01 Patent grant
TA01 Transfer of patent application right

Effective date of registration: 20150925

Address after: 311805 Zhejiang city of Shaoxing province Zhuji city Zhoucun Town, No. 185 Jieting

Applicant after: Ye Cheng

Applicant after: Wang Guozhong

Address before: 311805 Zhejiang city of Shaoxing province Zhuji city Zhoucun Town, No. 185 Jieting

Applicant before: Ye Cheng

C41 Transfer of patent application or patent right or utility model
TR01 Transfer of patent right

Effective date of registration: 20151102

Address after: 318054 ten village, 3 District, Feng Jiang Street, Luqiao District, Zhejiang City, Taizhou province 41

Patentee after: Wang Guozhong

Address before: 311805 Zhejiang city of Shaoxing province Zhuji city Zhoucun Town, No. 185 Jieting

Patentee before: Ye Cheng

Patentee before: Wang Guozhong

CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20151028

Termination date: 20170202