CN106955714A - A kind of bigger serface is without vanadium denitration catalyst and its preparation method and application - Google Patents

A kind of bigger serface is without vanadium denitration catalyst and its preparation method and application Download PDF

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CN106955714A
CN106955714A CN201710185607.5A CN201710185607A CN106955714A CN 106955714 A CN106955714 A CN 106955714A CN 201710185607 A CN201710185607 A CN 201710185607A CN 106955714 A CN106955714 A CN 106955714A
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oxide
salt
catalyst
cobalt
concentration
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唐幸福
高佳逸
黄志伟
刘小娜
陈俊逍
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Fudan University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts 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
    • B01J23/847Vanadium, niobium or tantalum or polonium
    • B01J23/8474Niobium
    • 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
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts 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
    • B01J23/88Molybdenum
    • B01J23/882Molybdenum and cobalt
    • 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
    • B01J23/888Tungsten
    • B01J35/615
    • 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

Abstract

The invention belongs to smoke catalytic purification techniques field, specially a kind of bigger serface is without vanadium denitration catalyst and its production and use.The denitrating catalyst of the present invention, using silica modified titanium dioxide as carrier, with the one or more in nickel oxide, cobalt/cobalt oxide, ferriferous oxide and cerium oxide for active component, with the one or more in tungsten oxide, molybdenum oxide and niobium oxide for auxiliary agent, it is advantageous that on the one hand effectively increasing the specific surface area of catalyst, denitration efficiency is significantly improved, the bio-toxicity of traditional vanadium system denitrating catalyst is on the other hand solved the problems, such as.Denitrating catalyst of the present invention has 100 ~ 150m2/ g specific surface area, can tolerate and contain 0~3000mg/m simultaneously3SO2With the nitrogen oxide containing gas of 0~20% vapor, in 280~450 DEG C and 3,000~100,000h‑1Under conditions of air speed, denitration efficiency is stable more than 90%, N2Selectivity is higher than 92%, with strong water resistant sulfur resistive ability, is particularly suitable for use in the discharged nitrous oxides control of thermal power station's flue gas.

Description

A kind of bigger serface is without vanadium denitration catalyst and its preparation method and application
Technical field
The invention belongs to smoke catalytic purification techniques field, and in particular to a kind of bigger serface is without vanadium denitration catalyst Preparation method and application.
Background technology
Nitrogen oxides(NO x )Main component be nitric oxide(NO)And nitrogen dioxide(NO2), to human eye and breathing Road has strong impulse.Human body sucks nitrogen oxides and may result in lung's structural change for a long time, and serious harm human body is good for Health.In addition nitrogen oxides can also trigger the environmental pollutions such as acid rain, ozone hole and destruction problem, to socio-economic development, life State is balanced and the life production of people causes to have a strong impact on.In recent years, because country puts into effect regulation and the political affairs of nitrogen oxides emission reduction Plan, the strict measure for carrying out discharged nitrous oxides control, national discharged nitrous oxides total amount drops year by year, but total amount still ten Divide huge.According to《Environmental statistics annual report in 2015》, industrial nitrogen oxide emission accounts for national discharged nitrous oxides total amount 63.8%, wherein electric power, the nitrogen oxides of heating power production and supply industry discharge accounts for more than the 50% of industrial nitrogen oxide emission.Cause This, by economical and efficient and environmental protection denitration technology be applied to industrial smoke discharged nitrous oxides control it is imperative.
SCR(Selective Catalytic Reduction, SCR)It is at present in the world using the most One of extensive gas denitrifying technology, its reaction mechanism is using additional urea or ammonia as reducing agent, in denitrating catalyst Catalytic action under by the NO in flue gas x Nontoxic nitrogen and water is reduced into, the performance of its core denitrating catalyst is determined The application conditions and scope of SCR technology, and the ratio table of the denitration efficiency of denitrating catalyst again with catalyst under normal circumstances Area is proportionate.Current industrialized denitrating catalyst is mainly vanadium series catalyst(Such as V2O5/WO3-TiO2And V2O5/MoO3- TiO2), its specific surface area is 50 ~ 60m2/ g, the temperature window of application is 300 ~ 400 DEG C, is widely used in thermal power station's nitrogen oxides Emission control.But, the active component V of vanadium series catalyst2O5With strong bio-toxicity, can to the respiratory system of human body and Skin causes serious injury, and half lethal dose is 10mg/kg.The vanadium series catalyst of inactivation is because regeneration cost is higher and can select Direct landfill disposal, causes secondary pollution.In addition, V2O5With by SO2It is oxidized to SO3Catalytic action.Flue gas is urged by vanadium system The SO generated after agent3With the NH of escape3With vapor reaction generation ammonium sulfate and ammonium hydrogen sulfate, corrosion downstream pipe and equipment. Therefore, need badly exploitation it is a kind of with NO_x Reduction by Effective efficiency without vanadium denitration catalyst, the traditional vanadium system denitrating catalyst of substitution, innovation Thermal power station's gas denitrifying technology.
Publication No. CN103894184A Chinese invention patent discloses a kind of high-specific surface area vanadium zinc system and is modified denitration Catalyst, utilizes metatitanic acid and H2O2Between the chemical process of interionic complexing redisperse improve the specific surface area of catalyst, The denitration efficiency of catalyst is effectively increased, but its specific surface area is still no more than 100m2/ g, and still by extremely toxic substance V2O5 It is used as active component.Publication No. CN103406127A patent document discloses a kind of catalysis of nontoxic low-temperature denitration catalysis Agent, the catalyst has more than 80% denitration efficiency at 120 ~ 250 DEG C using manganese oxide as major catalyst, but the patent is not examined Examine catalyst interval in sulfur-bearing, aqueous and thermal power station's flue-gas temperature(300~400℃)Under the conditions of denitration performance, limit this The practical ranges of catalyst.Therefore, a kind of specific surface area is developed big, denitration efficiency is high, while having strong sulfur resistive water resistant There is performance actual application value to have wide market prospects without vanadium denitration catalyst.
The content of the invention
It is an object of the invention to provide a kind of specific surface area is big, denitration efficiency it is high without vanadium denitration catalyst and its preparation Method, and application of the above-mentioned catalyst in the discharged nitrous oxides control aspect of thermal power station's flue gas is provided.
The bigger serface that the present invention is provided is without vanadium denitration catalyst, using silica modified titanium dioxide as carrier, With the one or more in nickel oxide, cobalt/cobalt oxide, ferriferous oxide and cerium oxide for active component, with tungsten oxide, molybdenum One or more in oxide and niobium oxide are auxiliary agent, i.e., be made up of carrier, active component and the part of auxiliary agent three;Wherein, On the basis of silica modified TiO 2 carrying weight, silica accounts for the 1 ~ 40% of carrier quality, and active component accounts for load The 1 ~ 40% of weight, auxiliary agent accounts for the 0.1 ~ 15% of carrier quality.
Preparation method of the bigger serface that the present invention is provided without vanadium denitration catalyst(That is active component and auxiliary agent dipping is negative Carry), comprise the following steps that:
By one kind in the one or more in a certain amount of nickel salt, cobalt salt, molysite and cerium salt, with tungsten salt, molybdenum salt and niobium salt or It is a variety of, it is dissolved in a certain amount of deionized water, is sufficiently stirred for disperseing to form mixed liquor;By a certain amount of silica modified two Titanium dioxide carrier adds above-mentioned mixed liquor, and 80 ~ 100 DEG C of stirrings are evaporated;Collection is evaporated product and small in 250 ~ 650 DEG C of roastings 3 ~ 8 When, obtain finished catalyst.
Wherein, the nickel salt is the one or more in nickel nitrate, nickel chloride and nickel sulfate, and nickel element is dense in its solution Spend for 0.001 ~ 1.0mol/L;The cobalt salt is cobalt member in the one or more in cobalt nitrate, cobalt chloride and cobaltous sulfate, its solution The concentration of element is 0.001 ~ 1.0mol/L;The molysite be frerrous chloride, ferrous sulfate, iron chloride and ferric nitrate in one kind or A variety of, the concentration of ferro element is 0.001 ~ 1.0mol/L in its solution;The cerium salt is in cerous sulfate, cerous nitrate and cerium chloride The concentration of Ce elements is 0.001 ~ 1.0mol/L in one or more, its solution;The tungsten salt be ammonium metatungstate, ammonium paratungstate, The concentration of wolfram element is 0.001 ~ 1.0mol/L in one or more in sodium tungstate and potassium tungstate, its solution;The molybdenum salt is One or more in ammonium dimolybdate, ammonium tetramolybdate, ammonium heptamolybdate and ammonium octamolybdate, the concentration of its Molybdenum in Solution element is 0.001~1.0mol/L;The niobium salt is the concentration of niobium element in the one or more in niobium oxalate and columbium pentachloride, its solution For 0.001 ~ 1.0mol/L.
Wherein, the preparation method of silica modified titania support is as follows:
A certain amount of titanium salt and Ludox are dissolved in a certain amount of deionized water, stirred scattered, mixed liquor is formed;Continue Ammoniacal liquor is added into the mixed liquor under stirring, pH of mixed=8 ~ 10 are adjusted;After aging 0.5 ~ 12 hour, the above-mentioned mixed liquor of suction filtration, Washing and filtering product is to filtrate pH=7;Filtration product is dried 2 ~ 24 hours at 80 ~ 120 DEG C, is calcined 3 ~ 8 at 400 ~ 650 DEG C afterwards Hour, obtain silica modified titania support;
Wherein, the titanium salt is the one or more in titanium tetrachloride, titanium sulfate, titanyl sulfate and butyl titanate, its solution The concentration of middle titanium elements is 0.1 ~ 1.0mol/L;The Ludox is acidic silicasol, the fraction of quality containing silica 20 ~ 30%; The ammoniacal liquor contains NH3Mass fraction 18 ~ 25%.
The advantage for the denitrating catalyst that the present invention is provided is:Specific surface area is big(100~150m2/g), it is tolerable to contain simultaneously 0~3000mg/m3SO2With the nitrogen oxide containing gas of 0~20% vapor, in 280~450 DEG C and 3,000~100,000h-1 Under conditions of air speed, denitration efficiency is stable more than 90%, N2Selectivity is higher than 92%, with strong water resistant sulfur resistive ability, especially fits Discharged nitrous oxides for thermal power station's flue gas are controlled, i.e., the middle temperature smoke denitrating for sulfur-rich stationary source is handled.
Embodiment
The present invention is described in further detail below by specific embodiment.It should be understood that these embodiments are only used for The bright present invention rather than limitation the scope of the present invention.The experimental method of unreceipted actual conditions, is generally pressed in the following example More solito condition, or according to the condition proposed by manufacturer.
Embodiment 1:
1. the preparation of silica modified titania support:By 0.075mol titanyl sulfates and 16g acidic silicasols (25%)It is dissolved in 100ml deionized waters, stirs scattered, forms mixed liquor;By ammoniacal liquor under lasting stirring(25%)In addition Mixed liquor is stated, pH of mixed=9 are adjusted;After aging 10 hours, the above-mentioned mixed liquor of suction filtration, washing and filtering product to filtrate pH=7;Cross Filter product to dry at 80 DEG C 12 hours, be calcined 3 hours at 550 DEG C afterwards, obtain silica modified titania support.
2. active component and auxiliary agent dip loading:By 0.025mol ferrous sulfate heptahydrates, the water cerous nitrates of 0.003mol six and 0.0017mol niobium oxalates are dissolved in 100ml deionized waters, are sufficiently stirred for disperseing to form mixed liquor;10g is silica modified Titania support adds above-mentioned mixed liquor, and 80 DEG C of stirrings are evaporated;Collection is evaporated product and is calcined 3 hours at 550 DEG C, obtains into Product catalyst.
3. the performance test of catalyst:Specific surface area of catalyst is 133m2/ g, is automatically compared by Tristar II 3020 Surface area and the test of pore analysis instrument are obtained;0.5g catalyst is taken to be put into fixed bed quartz tube reactor, quartzy bore=8mm, Simulated flue gas is by NO, NH3、O2And N2Composition, wherein NO 500ppm, NH3 500ppm、O23%, air speed 40,000h-1, reaction temperature 280 ~ 450 DEG C of degree, reaction end gas Antaris IGS gas analyzer on-line checkings.In this test condition, catalyst is de- Nitre stabilised efficiency is more than 97%, N2Selectivity is more than 98%.
4. sulfur resistive water repelling property is tested:It is extra in simulated flue gas to add SO2And vapor so that SO2Concentration is 2700mg/ m3, vapor volume ratio is 20%, and other test conditions are constant.In this test condition, the denitration efficiency of catalyst is still stablized More than 94%, N2Selectivity is more than 97%.
Embodiment 2:
1. the preparation of silica modified titania support:By 0.01mol titanium tetrachlorides and 8g acidic silicasols(25%) It is dissolved in 100ml deionized waters, stirs scattered, forms mixed liquor;By ammoniacal liquor under lasting stirring(20%)Add above-mentioned mixing Liquid, adjusts pH of mixed=8;After aging 3 hours, the above-mentioned mixed liquor of suction filtration, washing and filtering product to filtrate pH=7;Filtration product Dried at 100 DEG C 8 hours, be calcined 3 hours at 500 DEG C afterwards, obtain silica modified titania support.
2. active component and auxiliary agent dip loading:By the water nickel nitrates of 0.01mol six, 0.01mol CoCL2 6H2Os and 0.0006mol ammonium metatungstates are dissolved in 100ml deionized waters, are sufficiently stirred for disperseing to form mixed liquor;10g is silica modified Titania support add above-mentioned mixed liquor, 90 DEG C of stirrings are evaporated;Collection is evaporated product and is calcined 3 hours at 550 DEG C, obtains Finished catalyst.
3. the performance test of catalyst:Specific surface area of catalyst is 103m2/ g, is automatically compared by Tristar II 3020 Surface area and the test of pore analysis instrument are obtained;0.5g catalyst is taken to be put into fixed bed quartz tube reactor, quartzy bore=8mm, Simulated flue gas is by NO, NH3、O2And N2Composition, wherein NO 1000ppm, NH31000ppm、O23%, air speed 80,000h-1, reaction 280 ~ 450 DEG C of temperature, reaction end gas Antaris IGS gas analyzer on-line checkings.In this test condition, catalyst Denitration efficiency is stable more than 95%, N2Selectivity is more than 94%.
4. sulfur resistive water repelling property is tested:It is extra in simulated flue gas to add SO2And vapor so that SO2Concentration is 1300mg/ m3, vapor volume ratio is 20%, and other test conditions are constant.In this test condition, the denitration efficiency of catalyst is still stablized More than 92%, N2Selectivity is more than 92%.
Embodiment 3:
1. the preparation of silica modified titania support:By 0.087mol butyl titanates and 12g acidic silicasols (25%)It is dissolved in 100ml deionized waters, stirs scattered, forms mixed liquor;By ammoniacal liquor under lasting stirring(18%)In addition Mixed liquor is stated, pH of mixed=10 are adjusted;After aging 2 hours, the above-mentioned mixed liquor of suction filtration, washing and filtering product to filtrate pH=7;Cross Filter product to dry at 110 DEG C 6 hours, be calcined 3 hours at 600 DEG C afterwards, obtain silica modified titania support.
2. active component and auxiliary agent dip loading:By the water ferric nitrates of 0.02mol nine, 0.012mol cobalt nitrate hexahydrates and 0.001mol ammonium heptamolybdates are dissolved in 100ml deionized waters, are sufficiently stirred for disperseing to form mixed liquor;10g is silica modified Titania support add mixed liquor in, 100 DEG C of stirrings are evaporated;Collection is evaporated product and is calcined 3 hours at 500 DEG C, obtains Finished catalyst.
3. the performance test of catalyst:Specific surface area of catalyst is 108m2/ g, is automatically compared by Tristar II 3020 Surface area and the test of pore analysis instrument are obtained;0.5g catalyst is taken to be put into fixed bed quartz tube reactor, quartzy bore=8mm, Simulated flue gas is by NO, NH3、O2And N2Composition, wherein NO 1000ppm, NH31000ppm、O23%, air speed 40,000h-1, reaction 280 ~ 450 DEG C of temperature, reaction end gas Antaris IGS gas analyzer on-line checkings.In this test condition, catalyst Denitration efficiency is stable more than 98%, N2Selectivity is more than 97%.
4. sulfur resistive water repelling property is tested:It is extra in simulated flue gas to add SO2And vapor so that SO2Concentration is 2700mg/ m3, vapor volume ratio is 10%, and other test conditions are constant.In this test condition, the denitration efficiency of catalyst is still stablized More than 96%, N2Selectivity is more than 95%.
Embodiment 4:
1. the preparation of silica modified titania support:By 0.075mol titanyl sulfates and 16g acidic silicasols (25%)It is dissolved in 100ml deionized waters, stirs scattered, forms mixed liquor;By ammoniacal liquor under lasting stirring(25%)In addition Mixed liquor is stated, pH of mixed=9 are adjusted;After aging 10 hours, the above-mentioned mixed liquor of suction filtration, washing and filtering product to filtrate pH=7;Cross Filter product to dry at 80 DEG C 12 hours, be calcined 3 hours at 550 DEG C afterwards, obtain silica modified titania support.
2. active component and auxiliary agent dip loading:By 0.02mol Iron trichloride hexahydrates, the water cerium chlorides of 0.005mol six and The water nickel chlorides of 0.015mol six, 0.0003mol ammonium metatungstates and 0.0007mol niobium oxalates are dissolved in 100ml deionized waters, fully Dispersed with stirring formation mixed liquor;Titania support silica modified 10g is added into above-mentioned mixed liquor, 80 DEG C of stirrings are steamed It is dry;Collection is evaporated product and is calcined 3 hours at 450 DEG C, obtains finished catalyst.
3. the performance test of catalyst:Specific surface area of catalyst is 145m2/ g, is automatically compared by Tristar II 3020 Surface area and the test of pore analysis instrument are obtained;0.5g catalyst is taken to be put into fixed bed quartz tube reactor, quartzy bore=8mm, Simulated flue gas is by NO, NH3、O2And N2Composition, wherein NO 500ppm, NH3 500ppm、O23%, air speed 100,000h-1, reaction 280 ~ 450 DEG C of temperature, reaction end gas Antaris IGS gas analyzer on-line checkings.In this test condition, catalyst Denitration efficiency is stable more than 99%, N2Selectivity is more than 99%.
4. sulfur resistive water repelling property is tested:It is extra in simulated flue gas to add SO2And vapor so that SO2Concentration is 1300mg/ m3, vapor volume ratio is 10%, and other test conditions are constant.In this test condition, the denitration efficiency of catalyst is still stablized More than 95%, N2Selectivity is more than 97%.
All documents referred in the present invention are all incorporated as reference in this application, independent just as each document It is incorporated as with reference to such.In addition, it is to be understood that after the above-mentioned instruction content of the present invention has been read, those skilled in the art can To be made various changes or modifications to the present invention, these equivalent form of values equally fall within the model that the application appended claims are limited Enclose.

Claims (6)

1. a kind of bigger serface is without vanadium denitration catalyst, it is characterised in that the catalyst is by carrier, active component and auxiliary agent Composition, wherein, the carrier is silica modified titanium dioxide, and the active component is nickel oxide, cobalt/cobalt oxide, iron One or more in oxide and cerium oxide, the auxiliary agent is one kind in tungsten oxide, molybdenum oxide and niobium oxide Or it is a variety of;On the basis of silica modified TiO 2 carrying weight, silica accounts for the 1 ~ 40% of carrier quality, activity Component accounts for the 1 ~ 40% of carrier quality, and auxiliary agent accounts for the 0.1 ~ 15% of carrier quality.
2. preparation method of the bigger serface as claimed in claim 1 without vanadium denitration catalyst, it is characterised in that specific steps It is as follows:
By one kind in the one or more in a certain amount of nickel salt, cobalt salt, molysite and cerium salt, with tungsten salt, molybdenum salt and niobium salt or It is a variety of, it is dissolved in a certain amount of deionized water, is sufficiently stirred for disperseing to form mixed liquor;By a certain amount of silica modified two Titanium dioxide carrier adds above-mentioned mixed liquor, and 80 ~ 100 DEG C of stirrings are evaporated;Collection is evaporated product and small in 250 ~ 650 DEG C of roastings 3 ~ 8 When, obtain finished catalyst.
3. preparation method of the bigger serface as claimed in claim 2 without vanadium denitration catalyst, it is characterised in that the nickel salt For the one or more in nickel nitrate, nickel chloride and nickel sulfate, the concentration of nickel element is 0.001 ~ 1.0mol/L in its solution;Institute State cobalt salt be the concentration of cobalt element in the one or more in cobalt nitrate, cobalt chloride and cobaltous sulfate, its solution for 0.001 ~ 1.0mol/L;The molysite is iron in the one or more in frerrous chloride, ferrous sulfate, iron chloride and ferric nitrate, its solution The concentration of element is 0.001 ~ 1.0mol/L;The cerium salt is the one or more in cerous sulfate, cerous nitrate and cerium chloride, and its is molten The concentration of Ce elements is 0.001 ~ 1.0mol/L in liquid;The tungsten salt is in ammonium metatungstate, ammonium paratungstate, sodium tungstate and potassium tungstate One or more, the concentration of wolfram element is 0.001 ~ 1.0mol/L in its solution;The molybdenum salt is ammonium dimolybdate, four molybdic acids One or more in ammonium, ammonium heptamolybdate and ammonium octamolybdate, the concentration of its Molybdenum in Solution element is 0.001 ~ 1.0mol/L;It is described Niobium salt is that the concentration of niobium element in the one or more in niobium oxalate and columbium pentachloride, its solution is 0.001 ~ 1.0mol/L.
4. preparation method of the bigger serface as claimed in claim 2 without vanadium denitration catalyst, it is characterised in that the dioxy The preparation method of titania support that SiClx is modified is:
A certain amount of titanium salt and Ludox are dissolved in a certain amount of deionized water, stirred scattered, mixed liquor is formed;Continue Ammoniacal liquor is added into above-mentioned mixed liquor under stirring, pH of mixed=8 ~ 10 are adjusted;After aging 0.5 ~ 12 hour, the above-mentioned mixed liquor of suction filtration, Washing and filtering product is to filtrate pH=7;Filtration product is dried 2 ~ 24 hours at 80 ~ 120 DEG C, is calcined 3 ~ 8 at 400 ~ 650 DEG C afterwards Hour, obtain silica modified titania support.
5. preparation method of the bigger serface as claimed in claim 4 without vanadium denitration catalyst, it is characterised in that:In titanium dioxide In the preparation of the titania support of Si modification, the titanium salt is in titanium tetrachloride, titanium sulfate, titanyl sulfate and butyl titanate One or more, the concentration of titanium elements is 0.1 ~ 1.0mol/L in its solution;The Ludox is acidic silicasol, containing dioxy SiClx mass fraction 20 ~ 30%;The ammoniacal liquor contains NH3Mass fraction 18 ~ 25%.
6. a kind of bigger serface as claimed in claim 1 without vanadium denitration catalyst thermal power station's flue gas discharged nitrous oxides Application in control.
CN201710185607.5A 2017-03-26 2017-03-26 A kind of bigger serface is without vanadium denitration catalyst and its preparation method and application Pending CN106955714A (en)

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Cited By (12)

* Cited by examiner, † Cited by third party
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CN107497465A (en) * 2017-08-31 2017-12-22 复旦大学 Support type low temperature sulfuric-resisting hydrogen ammonium SCR denitration and its preparation method and application
CN107913716A (en) * 2017-10-30 2018-04-17 复旦大学 A kind of nontoxic high temperature alkali resistant metal denitrating catalyst and its preparation method and application
CN108097235A (en) * 2017-11-27 2018-06-01 南京工业大学 A kind of preparation method of the compound denitrating catalyst of layer structure
CN108554462A (en) * 2018-05-14 2018-09-21 南京工业大学 A kind of cerium tungsten titanium denitrating catalyst and its preparation method and application
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CN111530448A (en) * 2020-04-08 2020-08-14 上海大学 High-sulfur-resistance nonmetal-doped metal oxide denitration catalyst and preparation method thereof
CN112495370A (en) * 2020-12-17 2021-03-16 东北大学 Quaternary rare earth-based SCR denitration catalyst and preparation method thereof
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CN113976094A (en) * 2021-11-15 2022-01-28 复旦大学 High-activity vanadium-free denitration catalyst and preparation method and application thereof
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CN107233880B (en) * 2017-08-01 2020-10-09 清华大学 Non-vanadium-based catalyst for high-temperature flue gas denitration and preparation method thereof
CN107233880A (en) * 2017-08-01 2017-10-10 清华大学 A kind of high-temperature flue gas denitration non-catalytic component based on vanadium and preparation method thereof
CN107497465A (en) * 2017-08-31 2017-12-22 复旦大学 Support type low temperature sulfuric-resisting hydrogen ammonium SCR denitration and its preparation method and application
CN107913716A (en) * 2017-10-30 2018-04-17 复旦大学 A kind of nontoxic high temperature alkali resistant metal denitrating catalyst and its preparation method and application
CN108097235A (en) * 2017-11-27 2018-06-01 南京工业大学 A kind of preparation method of the compound denitrating catalyst of layer structure
CN108097235B (en) * 2017-11-27 2021-04-20 南京工业大学 Preparation method of composite denitration catalyst with layered structure
CN108554462A (en) * 2018-05-14 2018-09-21 南京工业大学 A kind of cerium tungsten titanium denitrating catalyst and its preparation method and application
CN109261162A (en) * 2018-10-16 2019-01-25 大唐南京环保科技有限责任公司 Denitrating catalyst and preparation with alkali resistant metal and water resistant sulfur resistance, application
WO2020103330A1 (en) * 2018-11-21 2020-05-28 华电青岛环保技术有限公司 Honeycomb type low-temperature scr denitration catalyst and preparation method therefor
WO2021109571A1 (en) * 2019-12-06 2021-06-10 启源(西安)大荣环保科技有限公司 Small-aperture corrugated catalyst for fuel gas denitration and preparation method therefor
CN111530448A (en) * 2020-04-08 2020-08-14 上海大学 High-sulfur-resistance nonmetal-doped metal oxide denitration catalyst and preparation method thereof
CN111530448B (en) * 2020-04-08 2023-07-18 上海大学 Non-metal doped metal oxide denitration catalyst with strong sulfur resistance and preparation method thereof
CN112495370A (en) * 2020-12-17 2021-03-16 东北大学 Quaternary rare earth-based SCR denitration catalyst and preparation method thereof
CN113976094A (en) * 2021-11-15 2022-01-28 复旦大学 High-activity vanadium-free denitration catalyst and preparation method and application thereof
CN115430289A (en) * 2022-10-13 2022-12-06 清华大学 Method for removing nitrogen oxides and dioxins in flue gas, catalyst and preparation method of catalyst
CN115430289B (en) * 2022-10-13 2024-03-05 清华大学 Method for removing nitrogen oxides and dioxins in flue gas, catalyst and preparation method of catalyst

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Application publication date: 20170718