CN106607046A - Preparation method for catalytically active ceramic cotton for flue gas denitration - Google Patents

Preparation method for catalytically active ceramic cotton for flue gas denitration Download PDF

Info

Publication number
CN106607046A
CN106607046A CN201610998338.XA CN201610998338A CN106607046A CN 106607046 A CN106607046 A CN 106607046A CN 201610998338 A CN201610998338 A CN 201610998338A CN 106607046 A CN106607046 A CN 106607046A
Authority
CN
China
Prior art keywords
cellucotton
flue gas
mixed solution
nitrate
catalysis activity
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.)
Granted
Application number
CN201610998338.XA
Other languages
Chinese (zh)
Other versions
CN106607046B (en
Inventor
陆丽芳
朱军
王越超
易佑宁
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.)
JIANGSU PROV CERAMIC RESEARCH INST Co Ltd
Jiangsu Jiuwu Hi Tech Co Ltd
Original Assignee
JIANGSU PROV CERAMIC RESEARCH INST Co Ltd
Jiangsu Jiuwu Hi Tech Co Ltd
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 JIANGSU PROV CERAMIC RESEARCH INST Co Ltd, Jiangsu Jiuwu Hi Tech Co Ltd filed Critical JIANGSU PROV CERAMIC RESEARCH INST Co Ltd
Priority to CN201610998338.XA priority Critical patent/CN106607046B/en
Publication of CN106607046A publication Critical patent/CN106607046A/en
Application granted granted Critical
Publication of CN106607046B publication Critical patent/CN106607046B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • 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
    • B01D53/8621Removing nitrogen compounds
    • B01D53/8625Nitrogen oxides
    • B01D53/8628Processes characterised by a specific catalyst
    • 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
    • B01D53/88Handling or mounting catalysts
    • 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
    • B01J35/50Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
    • B01J35/58Fabrics or filaments
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases
    • 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

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Organic Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

A preparation method for catalytically active ceramic cotton for flue gas denitration is provided; a preparation process comprises the following steps successively: (1) preparing a mixed solution containing a catalytically active ingredient; (2) dipping zirconia ceramic cellucotton in the mixed solution prepared in the step (1); (3) removing excess solution of the cellucotton dipped in the solution in the step (2), and fumigating with ammonia gas; (4) carrying out drying treatment on the cellucotton fumigated in the step (3); and (5) calcining. The prepared catalyst product has the advantages of large specific surface area, high temperature resistance, corrosion resistance and wide use range.

Description

A kind of denitrating flue gas catalysis activity ceramic wool preparation method
Technical field
The invention belongs to chemical stoneware field, more particularly to denitrating flue gas catalysis activity ceramic wool.
Background technology
Nitrogen oxides are one of Air Pollutant Discharge, serious harm ecological environment and human health, and current denitration is commonly used One of technology be ammonia selective catalytic reduction, conventional method is in honeycomb or cellular ceramic substrate by catalyst coated Surface, carrier is placed in container, and when high-temperature flue gas pass through, institute's nitrogen-containing oxide generates nitrogen and water with ammonia reaction.Due to Honeycomb or porous ceramicss are rigid bodies, when catalytic unit geomery changes, need to remake suitable shape and size Catalyst carrier, reduce the convenience of application.Catalyst is coated on ceramic fibre surface and is formed by the present invention has catalysis The ceramic fibre of activity, with resistance less advantage when shape is variable and fluid passes through, can be filled in variously-shaped appearance As catalyst in device and pipeline.
The content of the invention
The present invention is not enough for prior art, there is provided a kind of high temperature resistant, corrosion-resistant, installs simple, and convenient renewal is replaced, section About cost, specific surface area of catalyst is big, and various active composition is mutually promoted, better catalytic activity, and denitration rate is more than 90% Denitrating flue gas catalysis activity ceramic wool manufacture method.
To realize the object of the invention, there is provided technical scheme below:A kind of denitrating flue gas are prepared with catalysis activity ceramic wool Method, it is characterised in that comprise the following steps:
(1) mixed solution containing catalytic active component is prepared;
(2) zirconia ceramicss cellucotton is immersed in mixed solution;
(3) the zirconia ceramicss cellucotton being immersed in mixed solution is taken out, it is stifling with ammonia after removing redundant solution;
(4) the zirconia ceramicss cellucotton with ammonia after stifling is dried;
(5) dried zirconia ceramicss cellucotton is put in electric kiln and is calcined;
The mixed solution contains zirconium nitrate, manganese nitrate, ferric nitrate, cerous nitrate, and with mixed solution gross weight meter, its component includes Zirconium nitrate 25wt% ~ 43wt%, manganese nitrate is 16 wt % ~ 30 wt %, and ferric nitrate is 8 wt % ~ 15 wt %, and cerous nitrate is 18 wt %~26 wt %;
Preferably, the dip time that zirconia ceramicss cellucotton is immersed in mixed solution is 2 ~ 10min, solution temperature is 40 ~60℃。
Preferably, it is that zirconia ceramicss cellucotton is placed on into a closed container full of ammonia that ammonia is fumigated In, standing time is 0.2-1h.
Preferably, calcining heat is 420 ~ 580 DEG C, the programming rate≤3 DEG C/min of calcining heat is heated to from room temperature, The high-temperature calcination time is 5 ~ 18h, cools to room temperature with the furnace.
Preferably, also containing additive triton x-100 (octyl phenyl polyoxyethylene ether) in mixed solution, concentration is The 0.2% ~ 0.8% of mixed solution gross mass.
Preferably, zirconia ceramicss cellucotton fibre diameter is 2 ~ 5 μm, bulk density is 90 ~ 120kg/m3
Preferably, drying meanss are micro-wave drying method, the time is 5 ~ 30min.
Beneficial effect of the present invention:The catalyst high temperature resistant of the present invention, it is corrosion-resistant, install simple, convenient renewal is replaced, and is saved Cost.In addition, the specific surface area of catalyst of the present invention is big, and various active composition is mutually promoted, better catalytic activity.The present invention Catalysis activity ceramic membrane denitration rate more than 90%.
Active component Zr-Mn-Fe-Ce prepared by the present invention is to be supported on ZrO2On ceramic fiber cotton, can integrally use In catalysis membrane tube, solve the detached problem of product and catalyst hardly possible, and be conveniently updated replacement, catalyst activity into MnO in point2With very prominent low-temperature catalyzed characteristic, Mn-Fe combinations have more preferable catalysis activity and N2Selectivity, CeO2 With oxygen ability is preferably stored, the activity of catalyst, more ZrO can be obviously improved2Promotion forms weak acid acid site, strengthens Activity of the catalyst in cold stage, increased absorption NH3Efficiency, strengthen the effect of catalytic purification.
Specific embodiment
The present invention is done with reference to embodiment is further explained, the following example is merely to illustrate the present invention, but It is not used to limit the use range of the present invention.
Embodiment 1:
A kind of denitrating flue gas catalysis activity ceramic wool preparation method, its preparation process is comprised the following steps:
(1) mixed solution containing catalytic active component is prepared;Wherein, with mixture solution gross weight meter, the wt of zirconium nitrate 39 %, manganese nitrate is 28 wt %, and ferric nitrate is 12wt %, and cerous nitrate is 21 wt %;Triton x-100 (octyl phenyl Polyethylene oxide Ether) 0.3%wt %.
(2) zirconia ceramicss cellucotton is immersed in the solution of step (1) preparation;Wherein, dip time is 3min, solution temperature is 45 DEG C;Zirconia ceramicss cellucotton fibre diameter is 3 μm, and bulk density is 95kg/m3
(3) cellucotton of step (2) dipping solution is removed after redundant solution with drier, cellucotton is placed on In one closed container full of ammonia, fumigated;Time is 30min.
(4) cellucotton that Jing steps (3) were fumigated is carried out into microwave drying, the time is 8min.
(5) calcine;Calcining in the step (5), temperature is 430 DEG C, and calcination time is 8h, 1 DEG C of programming rate/ min。
Take the denitration test that the catalyst of the present embodiment enters under rower condition, denitration rate is up to 92.3%.
Embodiment 2:
A kind of denitrating flue gas catalysis activity ceramic wool preparation method, its preparation process is comprised the following steps:
(1) mixed solution containing catalytic active component is prepared;Wherein, with mixture solution gross weight meter, zirconium nitrate 42wt %, manganese nitrate is 26wt %, and ferric nitrate is 8wt %, and cerous nitrate is 24wt %;Triton x-100 (octyl phenyl polyoxyethylene ether) 0.5%wt %。
(2) zirconia ceramicss cellucotton is immersed in the solution of step (1) preparation;Wherein, dip time is 5min, molten Liquid temp is 50 DEG C;Zirconia ceramicss cellucotton fibre diameter is 5 μm, and bulk density is 103kg/m3
(3) cellucotton of step (2) dipping solution is removed after redundant solution with drier, cellucotton is placed on In one closed container full of ammonia, fumigated;Time is 45min.
(4) cellucotton that Jing steps (3) were fumigated is carried out into microwave drying, the time is 12min.
(5) calcine;Calcining in the step (5), temperature is 480 DEG C, and calcination time is 12h, programming rate 1.5 ℃/min。
Take the denitration test that the catalyst of the present embodiment enters under rower condition, denitration rate is up to 95.5%.
Embodiment 3:
A kind of denitrating flue gas catalysis activity ceramic wool preparation method, its preparation process is comprised the following steps:
(1) mixed solution containing catalytic active component is prepared;Wherein, with mixture solution gross weight meter, the wt of zirconium nitrate 36 %, manganese nitrate is 24 wt %, and ferric nitrate is 15wt %, and cerous nitrate is 25 wt %;Triton x-100 (octyl phenyl Polyethylene oxide Ether) 0.6%wt %.
(2) zirconia ceramicss cellucotton is immersed in the solution of step (1) preparation;Wherein, dip time is 8min, Solution temperature is 55 DEG C;Zirconia ceramicss cellucotton fibre diameter is 5 μm, and bulk density is 103kg/m3
(3) cellucotton of step (2) dipping solution is removed after redundant solution with drier, cellucotton is placed on In one closed container full of ammonia, fumigated;Time is 50min.
(4) cellucotton that Jing steps (3) were fumigated is carried out into microwave drying, the time is 18min.
(5) calcine;Calcining in the step (5), temperature is 500 DEG C, and calcination time is 15h, 2 DEG C of programming rate/ min。
Take the denitration test that the catalyst of the present embodiment enters under rower condition, denitration rate is up to 96.2%.

Claims (7)

1. a kind of denitrating flue gas catalysis activity ceramic wool preparation method, it is characterised in that comprise the following steps:
(1) mixed solution containing catalytic active component is prepared;
(2) zirconia ceramicss cellucotton is immersed in mixed solution;
(3) the zirconia ceramicss cellucotton being immersed in mixed solution is taken out, it is stifling with ammonia after removing redundant solution;
(4) the zirconia ceramicss cellucotton with ammonia after stifling is dried;
(5) dried zirconia ceramicss cellucotton is put in electric kiln and is calcined;
The mixed solution contains zirconium nitrate, manganese nitrate, ferric nitrate, cerous nitrate, and with mixed solution gross weight meter, its component includes Zirconium nitrate 25wt% ~ 43wt%, manganese nitrate is 16 wt % ~ 30 wt %, and ferric nitrate is 8 wt % ~ 15 wt %, and cerous nitrate is 18 wt %~26 wt %。
2. a kind of denitrating flue gas according to claim 1 catalysis activity ceramic wool preparation method, it is characterised in that oxidation The dip time that zircon ceramic cellucotton is immersed in mixed solution is 2 ~ 10min, and solution temperature is 40 ~ 60 DEG C.
3. a kind of denitrating flue gas according to claim 1 catalysis activity ceramic wool preparation method, it is characterised in that ammonia Stifling is that zirconia ceramicss cellucotton is placed in a closed container full of ammonia, and standing time is 0.2-1h.
4. a kind of denitrating flue gas according to claim 1 catalysis activity ceramic wool preparation method, it is characterised in that calcining Temperature is 420 ~ 580 DEG C, and from room temperature the programming rate≤3 DEG C/min of calcining heat is heated to, and the high-temperature calcination time is 5 ~ 18h, Cool to room temperature with the furnace.
5. a kind of denitrating flue gas according to claim 1 catalysis activity ceramic wool preparation method, it is characterised in that mixing In solution also contain additive triton x-100 (octyl phenyl polyoxyethylene ether), concentration for mixed solution gross mass 0.2% ~ 0.8%。
6. a kind of denitrating flue gas according to claim 1 catalysis activity ceramic wool preparation method, it is characterised in that oxidation Zircon ceramic cellucotton fibre diameter is 2 ~ 5 μm, and bulk density is 90 ~ 120kg/m3
7. a kind of denitrating flue gas according to claim 1 catalysis activity ceramic wool preparation method, it is characterised in that be dried Method is micro-wave drying method, and the time is 5 ~ 30min.
CN201610998338.XA 2016-11-14 2016-11-14 Preparation method of catalytically active ceramic wool for flue gas denitration Active CN106607046B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610998338.XA CN106607046B (en) 2016-11-14 2016-11-14 Preparation method of catalytically active ceramic wool for flue gas denitration

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610998338.XA CN106607046B (en) 2016-11-14 2016-11-14 Preparation method of catalytically active ceramic wool for flue gas denitration

Publications (2)

Publication Number Publication Date
CN106607046A true CN106607046A (en) 2017-05-03
CN106607046B CN106607046B (en) 2020-02-07

Family

ID=58615315

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610998338.XA Active CN106607046B (en) 2016-11-14 2016-11-14 Preparation method of catalytically active ceramic wool for flue gas denitration

Country Status (1)

Country Link
CN (1) CN106607046B (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0398752A1 (en) * 1989-05-19 1990-11-22 Babcock-Hitachi Kabushiki Kaisha Catalyst for reducing nitrogen oxides
JPH05200310A (en) * 1992-01-16 1993-08-10 Nippon Muki Co Ltd Carrier paper for denitration catalyst
CN1721059A (en) * 2005-05-24 2006-01-18 同济大学 Loaded on glass fiber net TiO 2The preparation method of fixed film photocatalyst
CN102114424A (en) * 2010-12-29 2011-07-06 国电科学技术研究院 Low-temperature smoke denitration SCR (silicon controlled rectifier) catalyst and preparation method
CN102824922A (en) * 2012-09-07 2012-12-19 浙江天蓝环保技术股份有限公司 Integrated honeycomb SCR (selective catalytic reduction) catalyst for low-temperature smoke denitration and preparation method of catalyst
CN104774009A (en) * 2015-03-25 2015-07-15 江苏省陶瓷研究所有限公司 Method for preparation of cerium oxide ceramic fiber board by precursor impregnation process

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0398752A1 (en) * 1989-05-19 1990-11-22 Babcock-Hitachi Kabushiki Kaisha Catalyst for reducing nitrogen oxides
JPH05200310A (en) * 1992-01-16 1993-08-10 Nippon Muki Co Ltd Carrier paper for denitration catalyst
CN1721059A (en) * 2005-05-24 2006-01-18 同济大学 Loaded on glass fiber net TiO 2The preparation method of fixed film photocatalyst
CN102114424A (en) * 2010-12-29 2011-07-06 国电科学技术研究院 Low-temperature smoke denitration SCR (silicon controlled rectifier) catalyst and preparation method
CN102824922A (en) * 2012-09-07 2012-12-19 浙江天蓝环保技术股份有限公司 Integrated honeycomb SCR (selective catalytic reduction) catalyst for low-temperature smoke denitration and preparation method of catalyst
CN104774009A (en) * 2015-03-25 2015-07-15 江苏省陶瓷研究所有限公司 Method for preparation of cerium oxide ceramic fiber board by precursor impregnation process

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
管昊: ""纳米氧化锆基SCR催化剂脱硝性能研究"", 《中国优秀硕士学位论文全文数据库(工程科技Ⅰ辑)》 *

Also Published As

Publication number Publication date
CN106607046B (en) 2020-02-07

Similar Documents

Publication Publication Date Title
CN104226301B (en) A kind of rare earth based complex multi-component denitration, the preparation method taking off two English catalyst
CN105854874B (en) Denitrating catalyst and preparation method thereof and the application in denitrating flue gas
CN106824173B (en) A kind of SCR catalyst for denitrating flue gas and preparation method thereof
CN102500359B (en) Vanadium based SCR catalyst as well as preparation and application thereof in tail gas NOx desorption after acrylonitrile oxidation
CN104338545B (en) A kind of efficient SCR catalyst that is applied to diesel engine vent gas purification of nitrogen oxides
CN104874347B (en) A kind of TiO2Load the preparation method and applications of nitrogen-doped graphene sponge
CN109569587A (en) A kind of manganese-based low-temperature catalyst for denitrating flue gas and preparation method thereof
KR101629483B1 (en) Vanadium-based denitration catalyst and preparing method of the same
CN106179301A (en) A kind of preparation method of cerium-titanium composite oxide low-temperature SCR catalyst
CN107649116A (en) Cerium tin composite oxides denitrating catalyst and its preparation method and application
CN105944713B (en) A kind of tungsten tin manganese-cerium composite oxide denitrating catalyst and its preparation and application
CN106824174A (en) A kind of coccoid catalyst of high-efficient purification nitrogen oxides and preparation method thereof
CN106391009A (en) Preparation method and application of catalyst for catalytic oxidation of VOCs
CN102658155A (en) Preparation method of supported type denitration catalyst
CN102240543A (en) CeO2-ZrO2 based SCR (selective catalytic reduction) catalyst used for denitration and preparation thereof
CN101745394A (en) Catalyst used for decomposing N2O and preparation method and application thereof
CN106268788A (en) A kind of catalyst of Elemental Mercury catalysis oxidation and preparation method thereof in flue gas
CN103769080A (en) Diesel vehicle tail gas purification SCR catalyst and preparation method thereof
CN103816909A (en) Low-temperature denitrification catalyst and preparation method thereof
CN108114742A (en) A kind of composite Ti-Si- molecular sieve coatings entirety denitrating catalyst and preparation method thereof
CN110813072A (en) Novel integrated material for flue gas desulfurization, denitrification and CO removal, and preparation and application thereof
CN108671946A (en) Phosphorus doping cerium titanium catalyst, preparation and its application in selective-catalytic-reduction denitrified
CN110026182A (en) Low-temperature denitration catalyst and its preparation and application in high sulfur resistive
CN105107521A (en) Mn-Fe double metal-doped active carbon-based desulfurization catalyst, and preparation method thereof
CN104128188A (en) Denitration catalyst used in waste incineration power plant and preparation method thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant