CN107694575A - A kind of complex carrier SCR denitration and preparation method - Google Patents

A kind of complex carrier SCR denitration and preparation method Download PDF

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Publication number
CN107694575A
CN107694575A CN201710831172.7A CN201710831172A CN107694575A CN 107694575 A CN107694575 A CN 107694575A CN 201710831172 A CN201710831172 A CN 201710831172A CN 107694575 A CN107694575 A CN 107694575A
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complex carrier
convex rod
concave convex
catalyst
scr denitration
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李倩
王虎
张捷
黄力
纵宇浩
董晓真
严巍
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Datang Nanjing Environmental Protection Technology Co Ltd
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Datang Nanjing Environmental Protection Technology Co Ltd
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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
    • B01J23/70Catalysts 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
    • 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
    • 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
    • B01J23/16Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/20Vanadium, niobium or tantalum
    • B01J23/22Vanadium
    • 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
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/61Surface area
    • B01J35/615100-500 m2/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
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Abstract

The invention discloses a kind of complex carrier SCR denitration, including certain mass than complex carrier, active component, auxiliary agent, lubricant;Complex carrier is the mixture of anatase-type nanometer titanium dioxide and metal ion-modified concave convex rod, and active component is vanadic anhydride.By being acidified concave convex rod, increase specific surface area, increase avtive spot, strengthen the adsorption capacity to element of being easily poisoned in flue gas, make catalyst that there is preferable anti-poisoning capability;Using metal ion-modified concave convex rod and nano titanium oxide as catalyst carrier, catalyst reaction temperatures section is set to widen to 160 DEG C~420 DEG C, efficiency high, stability in the temperature range catalyst denitration are good, selectivity is good, available for all types of industries stove denitration;Using concave convex rod as main material, production cost is effectively reduced;Titanium dioxide nanoparticle can be filled in the space of concave convex rod skeleton so that the stability of catalyst structure is strong, not easy to crack after high-temperature calcination, and wear-resisting intensity is higher.

Description

A kind of complex carrier SCR denitration and preparation method
Technical field
The present invention relates to a kind of complex carrier SCR denitration and preparation method thereof, belong to efficient catalyst and Atmosphere pollution prevention and control field.
Background technology
Pollution of the nitrogen oxides to environment is very serious, and nitrogen oxides is both the basis of nitric acid type acid rain, is to form light again One of chemical fumes, the main matter to damage the ozone layer;Nitrogen oxides also has very strong toxicity, can cause pole to health Macrolesion.In recent years, with the rapid development of economy, the discharge capacity of nitrogen oxides pollution thing increases sharply, life is seriously polluted State environment.
Coal-burning power plant is the main enterprises of discharged nitrous oxides, its discharge capacity account for national nitrogen oxide emission 25~ 40%, country has strictly controlled the discharge capacity of nitrogen oxides in coal-fired plant flue gas.But in increasingly serious pollution control situation In front, the discharged nitrous oxides of other industrial furnaces will be also strictly controlled, such as the industry such as coking, cement, glass, steel Pollutant emission national standard is issued, some key areas have progressively started to carry out nitrogen according to most stringent of index in standard Emissions of oxides controls.
Selective catalytic reduction (SCR) denitration is most widely used, denitrating flue gas skill that technology is most ripe in the world One of art, its technological core are to have used denitrating catalyst have the advantages that purifying rate is high, reliable, flat catalysis Agent is very important one kind in denitrating catalyst, has the higher market share.The denitrating catalyst that coal-burning power plant uses is For many years, technology is more ripe for commercial applications, but the flue gas condition of the industrial furnace such as coking, cement, glass and coal-burning power plant deposit In larger difference, have the characteristics that cigarette temperature is relatively low, dust burdening is high, poisoning constituent content is higher, current business denitrating catalyst without Method meets the denitration demand of industrial furnace.
Therefore, need exploitation one kind badly and have inexpensive, high denitration activity, high mechanical properties, wider reaction temperature section concurrently, together When the denitrating catalyst with preferable anti-poisoning capability, required with meeting that the increasingly strict nitrogen oxides of industrial furnace controls.
The content of the invention
The technical problem to be solved by the invention is to provide a kind of reaction temperature section for widening catalyst, improve Catalyst sulfur resistive, water resistant, anti-As, alkali metal, alkaline-earth metal poisoning capability, while also with denitration efficiency is high, cost is cheap, machine The advantages that tool intensity is high, versatile, complex carrier SCR denitration and its preparation suitable for various industrial furnace denitrations Method.
In order to solve the above technical problems, the technical solution adopted by the present invention is:
A kind of complex carrier SCR denitration, including certain mass than complex carrier, active component, auxiliary agent, lubrication Agent;
The complex carrier is the mixture of anatase-type nanometer titanium dioxide and metal ion-modified concave convex rod,
The active component is vanadic anhydride.
Above-mentioned complex carrier, active component, auxiliary agent, the mass ratio of lubricant are 100:(0.5~5):(1~10):(0.2 ~2).
The mol ratio of Ti, Si element is 1 in above-mentioned complex carrier:(0.1~0.5).
The mol ratio of metallic element and Si elements is (0.05~0.2) in above-mentioned metal ion-modified concave convex rod:1.
Above-mentioned lubricant is one kind or several in stearic acid, odium stearate, zinc stearate, polyvinyl alcohol or Tissuemat E Kind.
A kind of preparation method of above-mentioned complex carrier SCR denitration, comprises the following steps:
S1, concave convex rod is placed in inorganic acid solution, stirred, stood after supersound process and remove upper suspension, washed Solid after centrifugation, drying, grinding obtain acid activation concave convex rod;
S2, above-mentioned acid activation concave convex rod is placed in the solvable saline solution of modified metal element, stirring, after being ultrasonically treated Drying, metal ion-modified concave convex rod powder is made after calcining, grinding;
S3, compound load is made after above-mentioned metal ion-modified concave convex rod powder is well mixed with nano-titanium dioxide powder Body;
S4, vanadate is taken to be dissolved in monoethanolamine solution, stirring and dissolving under certain temperature;
S5, in mass ratio that complex carrier, auxiliary agent, mix lubricant is uniform, addition vanadate solution, ammoniacal liquor and deionization Water, pH to 7~9 is adjusted, lotion catalyst is made;
S6, by catalyst lotion it is coated, it is crimped, shearing, calcining, flat catalyst is prepared.
Inorganic acid in above-mentioned steps S1 is the one or more in hydrochloric acid, sulfuric acid and nitric acid, concentration be 1mol/L~ 5mol/L;
Mixing time is 0.5~2h, and ultrasonic time is 10~30min, is washed to washing lotion pH value to be neutral, oven temperature is 90 DEG C~105 DEG C.
Modified metal element described in upper rapid S2 is one or both of Fe, Zr, Ce, La, Mn, Sn;
Mixing time is 0.5~2h, ultrasonic time is 0.5~1h, and oven temperature is 90 DEG C~105 DEG C, and calcining heat is 400 DEG C, calcination time is 0.5~2h.
Vanadate in above-mentioned steps S4 is positive vanadate, pyrovanadate or metavanadate, and solution temperature is 70 DEG C~85 ℃。
Calcining heat in above-mentioned steps S5 is 420 DEG C~600 DEG C, and calcination time is 1h~3.5h.
The beneficial effect that the present invention is reached:
1st, specific surface area increase, avtive spot increase after concave convex rod is acidified;Concave convex rod duct increases be acidified simultaneously after, right Easy poisoning element adsorption capacity enhancing in flue gas, makes catalyst have preferable anti-poisoning capability.
2nd, using metal ion-modified concave convex rod and nano titanium oxide as catalyst carrier, catalyst reaction temperatures area is made Between widen to 160 DEG C~420 DEG C, catalyst is the temperature range denitration efficiency is high, stability is good, selectivity is good, available for each Class industrial furnace denitration.
3rd, concave convex rod effectively reduces Catalyst Production cost as main raw material(s), and price is more cheap.
4th, titanium dioxide nanoparticle can be filled in the space of concave convex rod skeleton, make the catalyst structure stability strong, Not easy to crack after high-temperature calcination, the wear-resisting intensity of catalyst is higher.
Figure of description
Fig. 1 is the local molten front-end geometry change schematic diagram of acid of concave convex rod octahedral cations of the present invention.
Embodiment
Below in conjunction with the accompanying drawings and specific embodiment the invention will be further described.
The following examples are only intended to illustrate the technical solution of the present invention more clearly, and can not limit the present invention with this Protection domain.
Chemical reagent and equipment and instrument used in embodiments of the invention, are purchased in market.
Wherein, specific surface area test uses full-automatic specific surface area analysis instrument (TriStar II 3020),
Wear-resisting strength test uses rotary abrasion instrument (Taber5135),
The flue gas analyzer model Thermo42i used in denitration performance test.
A kind of complex carrier SCR denitration, is prepared according to following steps:
S1, concave convex rod is placed in 1mol/L~5mol/L inorganic acid solution, stirs 0.5~2h, it is ultrasonically treated 10~ Stood after 30min and remove upper suspension, the solid after washing centrifugation to washing lotion pH value is neutrality, at 90 DEG C~105 DEG C Drying, grinding obtain acid activation concave convex rod;
S2, above-mentioned acid activation concave convex rod is placed in the solvable saline solution of modified metal element, it is 0.5~2h of stirring, super After 0.5~1h of sonication, dried at 90 DEG C~105 DEG C, metal ion is made after 0.5~2h, grinding are then calcined at 400 DEG C Modified attapulgite powder;
S3, compound load is made after above-mentioned metal ion-modified concave convex rod powder is well mixed with nano-titanium dioxide powder Body;
S4, vanadate is taken to be dissolved in monoethanolamine solution, stirring and dissolving at 70 DEG C~85 DEG C;
S5, in mass ratio that complex carrier, auxiliary agent, mix lubricant is uniform, addition vanadate solution, ammoniacal liquor and deionization Water, pH to 7~9 is adjusted, lotion catalyst is made;
S6, by catalyst lotion is coated, crimped, shearing, 1h~3.5h is calcined at 420 DEG C~600 DEG C, be prepared flat Board-like catalyst.
Catalyst performance is tested:
Embodiment 1
Properties of sample:Specific surface area 115m2/ g, wear-resisting intensity 47mg/100U.
Catalyst denitration performance is tested:Reaction temperature is 160 DEG C~420 DEG C, and smoke components are NO (500ppm), NH3 (500ppm)、O2(5%), carrier gas N2, air speed 10000h-1, in the range of reaction temperature, catalyst denitration efficiency is stable More than 93%, N2Selectivity is more than 95%.
Catalyst sulfur resistive water repelling property is tested:On the basis of denitration performance test condition, be continually fed into 1000ppmSO2 and 10% vapor 24h, other test conditions are constant, in the range of reaction temperature, catalyst denitration efficiency it is stable 91% with On, N2Selectivity is more than 90%.
Catalyst alkali resistant earth metal poisoning performance is tested:Load 500 μm of ol/g Ca on a catalyst using infusion process2+, The 4h under 400 DEG C of calcinings, then tests its denitration efficiency (test condition is with above-mentioned catalyst denitration performance test condition), measures Denitration efficiency in 160 DEG C~420 DEG C reaction intervals is stable more than 88%, N2Selectivity is more than 90%.
Embodiment 2
Properties of sample:Specific surface area 128m2/ g, wear-resisting intensity 39mg/100U.
Catalyst denitration performance is tested:Reaction temperature is 160 DEG C~420 DEG C, and smoke components are NO (500ppm), NH3 (500ppm)、O2(5%), carrier gas N2, air speed 10000h-1, in the range of reaction temperature, catalyst denitration efficiency is stable More than 96%, N2Selectivity is more than 95%.
Catalyst sulfur resistive water repelling property is tested:On the basis of denitration performance test condition, be continually fed into 1000ppmSO2 and 10% vapor 24h, other test conditions are constant, in the range of reaction temperature, catalyst denitration efficiency it is stable 92% with On, N2Selectivity is more than 91%.
Catalyst alkali resistant earth metal poisoning performance is tested:Load 800 μm of ol/g K on a catalyst using infusion process+, The lower 4h of 400 DEG C of calcinings, then tests its denitration efficiency (test condition is with above-mentioned catalyst denitration performance test condition), measures Denitration efficiency in 160 DEG C~420 DEG C reaction intervals is stable more than 91%, N2Selectivity is more than 90%.
Embodiment 3
Properties of sample:Specific surface area 109m2/ g, wear-resisting intensity 28mg/100U.
Catalyst denitration performance is tested:Reaction temperature is 160 DEG C~420 DEG C, and smoke components are NO (500ppm), NH3 (500ppm)、O2(5%), carrier gas N2, air speed 10000h-1, in the range of reaction temperature, catalyst denitration efficiency is stable More than 97%, N2Selectivity is more than 95%.
Catalyst sulfur resistive water repelling property is tested:On the basis of denitration performance test condition, be continually fed into 1000ppmSO2 and 10% vapor 24h, other test conditions are constant, in the range of reaction temperature, catalyst denitration efficiency it is stable 90% with On, N2Selectivity is more than 95%.
Catalyst alkali resistant earth metal poisoning performance is tested:Load 1000 μm of ol/g Na on a catalyst using infusion process+, The 4h under 400 DEG C of calcinings, then tests its denitration efficiency (test condition is with above-mentioned catalyst denitration performance test condition), measures Denitration efficiency in 160 DEG C~420 DEG C reaction intervals is stable more than 90%, N2Selectivity is more than 90%.
Accompanying drawing 1 is the local molten front-end geometry change schematic diagram of acid of concave convex rod octahedral cations, and left figure is natural concave convex rod Structural representation, after concave convex rod is acidified, duct significantly increases (right figure), adsorption capacity enhancing.
Described above is only the preferred embodiment of the present invention, it is noted that for the ordinary skill people of the art For member, without departing from the technical principles of the invention, some improvement and deformation can also be made, these are improved and deformation Also it should be regarded as protection scope of the present invention.

Claims (10)

  1. A kind of 1. complex carrier SCR denitration, it is characterised in that including certain mass than complex carrier, active component, Auxiliary agent, lubricant;
    The complex carrier is the mixture of anatase-type nanometer titanium dioxide and metal ion-modified concave convex rod,
    The active component is vanadic anhydride.
  2. 2. a kind of complex carrier SCR denitration according to claim 1, it is characterised in that the complex carrier, work Property component, auxiliary agent, lubricant mass ratio be 100:(0.5~5):(1~10):(0.2~2).
  3. 3. a kind of complex carrier SCR denitration according to claim 1, it is characterised in that in the complex carrier The mol ratio of Ti, Si element is 1:(0.1~0.5).
  4. 4. a kind of complex carrier SCR denitration according to claim 1, it is characterised in that the metal ion changes Property concave convex rod in the mol ratio of metallic element and Si elements be (0.05~0.2):1.
  5. 5. a kind of complex carrier SCR denitration according to claim 1, it is characterised in that the lubricant is hard One or more in resin acid, odium stearate, zinc stearate, polyvinyl alcohol or Tissuemat E.
  6. 6. according to a kind of preparation method of any described complex carrier SCR denitrations of claim 1-5, its feature exists In comprising the following steps:
    S1, concave convex rod is placed in inorganic acid solution, stirred, stood after supersound process and remove upper suspension, washing centrifugation Solid afterwards, drying, grinding obtain acid activation concave convex rod;
    S2, above-mentioned acid activation concave convex rod is placed in the solvable saline solution of modified metal element, stirring, dried after being ultrasonically treated It is dry, metal ion-modified concave convex rod powder is made after calcining, grinding;
    S3, complex carrier is made after above-mentioned metal ion-modified concave convex rod powder is well mixed with nano-titanium dioxide powder;
    S4, vanadate is taken to be dissolved in monoethanolamine solution, stirring and dissolving under certain temperature;
    S5, in mass ratio that complex carrier, auxiliary agent, mix lubricant is uniform, addition vanadate solution, ammoniacal liquor and deionized water, PH to 7~9 is adjusted, lotion catalyst is made;
    S6, by catalyst lotion it is coated, it is crimped, shearing, calcining, flat catalyst is prepared.
  7. 7. the preparation method of a kind of complex carrier SCR denitration according to CLAIM OF BENEFIT 6, it is characterised in that described Inorganic acid in step S1 is the one or more in hydrochloric acid, sulfuric acid and nitric acid, and concentration is 1mol/L~5mol/L;
    Mixing time is 0.5~2h, and ultrasonic time is 10~30min, and it is neutrality to wash to washing lotion pH value, and oven temperature is 90 DEG C ~105 DEG C.
  8. A kind of 8. preparation method of complex carrier SCR denitration according to claim 6, it is characterised in that step Modified metal element described in S2 is one or both of Fe, Zr, Ce, La, Mn, Sn;
    Mixing time is 0.5~2h, ultrasonic time is 0.5~1h, and oven temperature is 90 DEG C~105 DEG C, calcining heat 400 DEG C, calcination time is 0.5~2h.
  9. 9. the preparation method of a kind of complex carrier SCR denitration according to claim 6, it is characterised in that described Vanadate in step S4 is positive vanadate, pyrovanadate or metavanadate, and solution temperature is 70 DEG C~85 DEG C.
  10. 10. the preparation method of a kind of complex carrier SCR denitration according to claim 6, it is characterised in that described Calcining heat in step S5 is 420 DEG C~600 DEG C, and calcination time is 1h~3.5h.
CN201710831172.7A 2017-09-15 2017-09-15 A kind of complex carrier SCR denitration and preparation method Pending CN107694575A (en)

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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109999901A (en) * 2019-05-10 2019-07-12 宫子凡 A kind of porous graphene-molecular sieve complex carries denitrating catalyst and preparation method thereof
CN111330609A (en) * 2020-02-21 2020-06-26 大唐南京环保科技有限责任公司 Anti-alkali metal poisoning denitration catalyst and preparation method thereof
CN112007699A (en) * 2020-10-09 2020-12-01 黄山天之都环保科技有限公司 SCR denitration catalyst with ammoniaphilic membrane and preparation method thereof
CN113019353A (en) * 2021-02-04 2021-06-25 上海大学 Anti-poisoning ion exchange type attapulgite-based denitration catalyst, and preparation method and application thereof
CN113856673A (en) * 2021-10-27 2021-12-31 西安热工研究院有限公司 Catalyst for widening reaction temperature window of SCR (Selective catalytic reduction) catalyst and modification method
CN114433071A (en) * 2021-12-29 2022-05-06 江苏世清环保科技有限公司 Denitration catalyst prepared by taking attapulgite as carrier and preparation method thereof
TWI773475B (en) * 2020-08-04 2022-08-01 日商三菱動力股份有限公司 Denitration catalyst and method for purifying combustion exhaust gas

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103878032A (en) * 2014-03-25 2014-06-25 浙江海亮环境材料有限公司 SCR denitration catalyst with clay
CN104857952A (en) * 2015-05-04 2015-08-26 合肥晨晰环保工程有限公司 Sulfur-resistant nitrogen-oxide-removing attapulgite manganese-based SCR catalyst and preparation method and application thereof
CN105214650A (en) * 2015-09-21 2016-01-06 盐城复华环保产业开发有限公司 Containing the low temperature SCR denitration catalyst and preparation method thereof of zirconium manganese oxide
CN105413705A (en) * 2015-11-11 2016-03-23 福建紫荆环境工程技术有限公司 Catalyst for removing VOCs through photocatalysis in cooperation with thermal catalytic oxidation and preparation method and application of catalyst
JP2016150278A (en) * 2015-02-16 2016-08-22 イビデン株式会社 Honeycomb catalyst
WO2016148535A1 (en) * 2015-03-18 2016-09-22 한국과학기술원 Biomass saccharification method using solid acid catalyst
CN106111118A (en) * 2016-06-20 2016-11-16 浙江三龙催化剂有限公司 A kind of preparation method and applications of denitrating catalyst
CN106492790A (en) * 2016-09-23 2017-03-15 河北工业大学 A kind of low temperature SCR denitration catalyst and preparation method thereof
CN106732537A (en) * 2016-11-24 2017-05-31 北京神雾电力科技有限公司 It is a kind of to add attapulgite modified low-temperature SCR catalyst and preparation method thereof

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103878032A (en) * 2014-03-25 2014-06-25 浙江海亮环境材料有限公司 SCR denitration catalyst with clay
JP2016150278A (en) * 2015-02-16 2016-08-22 イビデン株式会社 Honeycomb catalyst
WO2016148535A1 (en) * 2015-03-18 2016-09-22 한국과학기술원 Biomass saccharification method using solid acid catalyst
CN104857952A (en) * 2015-05-04 2015-08-26 合肥晨晰环保工程有限公司 Sulfur-resistant nitrogen-oxide-removing attapulgite manganese-based SCR catalyst and preparation method and application thereof
CN105214650A (en) * 2015-09-21 2016-01-06 盐城复华环保产业开发有限公司 Containing the low temperature SCR denitration catalyst and preparation method thereof of zirconium manganese oxide
CN105413705A (en) * 2015-11-11 2016-03-23 福建紫荆环境工程技术有限公司 Catalyst for removing VOCs through photocatalysis in cooperation with thermal catalytic oxidation and preparation method and application of catalyst
CN106111118A (en) * 2016-06-20 2016-11-16 浙江三龙催化剂有限公司 A kind of preparation method and applications of denitrating catalyst
CN106492790A (en) * 2016-09-23 2017-03-15 河北工业大学 A kind of low temperature SCR denitration catalyst and preparation method thereof
CN106732537A (en) * 2016-11-24 2017-05-31 北京神雾电力科技有限公司 It is a kind of to add attapulgite modified low-temperature SCR catalyst and preparation method thereof

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109999901A (en) * 2019-05-10 2019-07-12 宫子凡 A kind of porous graphene-molecular sieve complex carries denitrating catalyst and preparation method thereof
CN111330609A (en) * 2020-02-21 2020-06-26 大唐南京环保科技有限责任公司 Anti-alkali metal poisoning denitration catalyst and preparation method thereof
CN111330609B (en) * 2020-02-21 2023-02-24 大唐南京环保科技有限责任公司 Denitration catalyst resistant to alkali metal poisoning and preparation method thereof
TWI773475B (en) * 2020-08-04 2022-08-01 日商三菱動力股份有限公司 Denitration catalyst and method for purifying combustion exhaust gas
CN112007699A (en) * 2020-10-09 2020-12-01 黄山天之都环保科技有限公司 SCR denitration catalyst with ammoniaphilic membrane and preparation method thereof
CN113019353A (en) * 2021-02-04 2021-06-25 上海大学 Anti-poisoning ion exchange type attapulgite-based denitration catalyst, and preparation method and application thereof
CN113856673A (en) * 2021-10-27 2021-12-31 西安热工研究院有限公司 Catalyst for widening reaction temperature window of SCR (Selective catalytic reduction) catalyst and modification method
CN114433071A (en) * 2021-12-29 2022-05-06 江苏世清环保科技有限公司 Denitration catalyst prepared by taking attapulgite as carrier and preparation method thereof

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Application publication date: 20180216