CN108686670A - A kind of anti-H for denitrating flue gas2O,SO2, heavy metal and dust poison multicomponent catalyst - Google Patents

A kind of anti-H for denitrating flue gas2O,SO2, heavy metal and dust poison multicomponent catalyst Download PDF

Info

Publication number
CN108686670A
CN108686670A CN201810530813.XA CN201810530813A CN108686670A CN 108686670 A CN108686670 A CN 108686670A CN 201810530813 A CN201810530813 A CN 201810530813A CN 108686670 A CN108686670 A CN 108686670A
Authority
CN
China
Prior art keywords
catalyst
present
soluble
source
preparation
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.)
Pending
Application number
CN201810530813.XA
Other languages
Chinese (zh)
Inventor
张丹
李云飞
张赩
孙晔
李智
孟宪超
何爽
唐云雪
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.)
Jilin Provincial Environmental Protection Department
Electric Power Research Institute of State Grid Jilin Electric Power Co Ltd
Original Assignee
Jilin Provincial Environmental Protection Department
Electric Power Research Institute of State Grid Jilin Electric Power 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 Jilin Provincial Environmental Protection Department, Electric Power Research Institute of State Grid Jilin Electric Power Co Ltd filed Critical Jilin Provincial Environmental Protection Department
Priority to CN201810530813.XA priority Critical patent/CN108686670A/en
Publication of CN108686670A publication Critical patent/CN108686670A/en
Pending legal-status Critical Current

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
    • B01J23/70Catalysts 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
    • B01J23/83Catalysts 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 rare earths or actinides
    • 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
    • B01D53/90Injecting reactants
    • 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
    • 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
    • B01J35/63Pore volume
    • B01J35/633Pore volume less than 0.5 ml/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/34Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation
    • B01J37/341Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation making use of electric or magnetic fields, wave energy or particle radiation
    • B01J37/342Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation making use of electric or magnetic fields, wave energy or particle radiation of electric, magnetic or electromagnetic fields, e.g. for magnetic separation
    • 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)
  • Physics & Mathematics (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • Electromagnetism (AREA)
  • Optics & Photonics (AREA)
  • Plasma & Fusion (AREA)
  • Toxicology (AREA)
  • Catalysts (AREA)

Abstract

The present invention relates to a kind of anti-H for denitrating flue gas2O,SO2, heavy metal and dust poison multicomponent catalyst, belong to multi-element metal oxide technical field of function materials.The present invention provides a kind of Fe-Ce-Ni-Zn/TiO2Five yuan of metal composite oxide catalysts.The polynary denitrating catalyst that the present invention uses has wider denitration temperature window and preferable low-temperature denitration activity, especially anti-H2O,SO2, that heavy metal and dust poison ability is stronger.

Description

A kind of anti-H for denitrating flue gas2O,SO2, heavy metal and dust poison polynary urge Agent
Technical field
The present invention relates to multi-element metal oxide technical field of function materials, and in particular to a kind of for the anti-of denitrating flue gas H2O,SO2, heavy metal and dust poison multicomponent catalyst more particularly to a kind of multicomponent catalyst for SCR denitrating flue gas and its Preparation method.
Background technology
Coal, in occupation of absolute leading role, and long-term accounts for China's primary energy consumption in Chinese national economy construction The ratio of total amount close even higher than 70%.In coal in China consumption, 80% coal is used as steam coal, is directly used in combustion It burns and generates thermal energy and power.But coal is a kind of low-grade fossil fuel, and there are a large amount of oxysulfides, nitrogen oxygen in combustion product gases The pollutants such as compound and carbon dioxide.According to statistics:CO, CO of Discharged form Coal Combustion in China2,SO2, NOX and dust account for total fuel combustion The ratio for burning discharge capacity is followed successively by 71%, 85%, 90%, 70% and 70%.
Although China has obtained significant results to the control of sulfur dioxide and dust, and compared to sulfur dioxide and dust etc. The reduction of gross contamination emission, discharged nitrous oxides total amount is but quickly increasing, according to scholarly forecast, according to current development Trend is up to 35,400,000 tons if not taking effective control measure to the year two thousand thirty nitrogen oxide emission, certainly will give China's ecology Environment and national economy cause huge harm.Meanwhile nitrogen oxides is also in rising trend to the contribution of China's Acid Rain Pollution, acid rain Middle NO3- concentration obviously increases, and the Acid Rain Pollution of China some areas is just gradually from sulfuric acid type to sulfuric acid, the compound transformation of nitric acid. Also, nitrogen oxides also has very strong greenhouse effects.Therefore, the discharge for controlling nitrogen oxides, especially controls coal fired thermal power plant The discharge of nitrogen oxides is trend of the times.
In recent years, in a variety of coal fired thermal power plant denitration technologies, selective catalytic reduction (Selective catalytic Reduction, SCR), relatively cost-effective because of its denitration efficiency height, oneself becomes the mainstream of current China's coal fired thermal power plant denitration Technology.Selective catalytic reduction (SCR) denitration is primarily referred to as under the effect of the catalyst, and (coal fired thermal power plant denitration is also for reducing agent Former agent is mainly urea and NH3, " selective " reacted with NOX in flue gas, generate nontoxic, free of contamination nitrogen and water.
Currently, SCR denitration used in coal-burning power plant of China is vanadium tungsten titanium series, be required for greatly import or Foreign technology is quoted, therefore first this and the renewal cost dressed up of SCR catalyst is all very high.And due to denitration temperature it is higher (300~ 400 DEG C), SCR device can only be arranged between economizer and air preheater.But contain herein there are a large amount of flying dusts in flue gas There are alkali metal, the substances such as arsenic and mercury inevitably to corrode and poison catalyst, catalyst is caused to be easy inactivation, service life It does not grow, and complicated component in flue gas, also be easy to cause catalyst poisoning, lead to life time decay;Meanwhile vanadium tungsten titanium series catalyst Vanadium component is easy to run off in agent, can be caused serious injury to environment and human body.Therefore, catalyst, which has become, restricts China's popularization and application SCR denitration technology, the principal element for controlling coal fired thermal power plant discharged nitrous oxides.
Therefore, research is nontoxic, denitration performance is good, denitration temperature window mouth width, the SCR denitration of inexpensive, especially It is that denitration temperature is low, the strong catalyst for denitrating flue gas of anti-poisoning capability, in China there is important practical application to anticipate Justice, it has also become one of the focus of line research staff's common concern in the industry.
Invention content
The multicomponent catalyst and preparation method thereof that the object of the present invention is to provide a kind of for denitrating flue gas, it is especially a kind of For the catalyst of SCR denitrating flue gas, the polynary denitrating catalyst that the present invention uses, have wider denitration temperature window and Preferable low-temperature denitration activity, especially anti-H2O,SO2, that heavy metal and dust poison ability is stronger.
In order to achieve the above objectives, the present invention provides a kind of multicomponent catalyst for denitrating flue gas, specially a kind of Fe- Ce-Ni-Zn/TiO2Five yuan of metal composite oxide catalysts, wherein
The molar ratio of element of Fe/Ti is (0.2~0.7):1;
The molar ratio of Elements C e/Ti is (0.05~0.8):1;
The molar ratio of element Ni/Ti is (0.2~0.6):1;
The molar ratio of element Zn/Ti is (0.05~0.5):1.
Preferably, the catalyst has porous structure.
Preferably, the granularity of the catalyst is 50~3500 mesh.
Preferably, the porosity of the catalyst is 2.5~1500m2/g。
Preferably, the specific surface area of the catalyst is 0.008~0.48cm3/g。
Invention also provides a kind of preparation methods of above-mentioned multicomponent catalyst for denitrating flue gas, including following step Suddenly:
A soluble source of iron, soluble cerium source, soluble nickel source, soluble Zn source, titanium dioxide) are dissolved in polyvinyl alcohol In aqueous solution, a certain amount of titania powder is added and is mixed, dry after being vigorously stirred, irradiation obtains intermediate powder;
B it) will be ground after intermediate powder calcination that above-mentioned steps obtain, obtain the catalyst for denitrating flue gas.
Preferably, the drying is dried using microwave dryer, and drying time is 10-60 minutes.
Preferably, the irradiation is irradiated using low-energy electronic accelerator irradiation devices, irradiation 0.1-0.3MeV, Irradiation time is 1-3 minutes.
Preferably, the calcination temperature is 400-600 DEG C, and the time is 0.5-2.5 hours.
Preferably, the time being vigorously stirred is 3-5 minutes.
Preferably, the mass concentration of the polyvinyl alcohol water solution is 0.1%-4%.
Preferably, the soluble source of iron includes bivalent soluble source of iron and/or trivalent solubility source of iron.
Preferably, the soluble source of iron includes ferric sulfate, ferrous sulfate, iron chloride, frerrous chloride, ferric nitrate and nitric acid It is one or more in ferrous iron;
The solubility cerium source includes one or more in cerous sulfate, cerium chloride and cerous nitrate;
The solubility nickel source includes one or more in nickel sulfate, nickel chloride and nickel nitrate;
The soluble Zn source includes one or more in zinc sulfate, zinc chloride and zinc nitrate.
The present invention provides a kind of multicomponent catalysts for denitrating flue gas, are Fe-Ce-Ni-Zn/TiO2Five yuan of metals Composite oxide catalysts.Compared with prior art, the present invention is toxic for existing vanadium Titanium series catalyst, denitration temperature is high, The problems such as cost height carry out creative selection and research, it is believed that ferrum-based catalyst has ring in numerous catalyst The advantages that border is nontoxic, denitration is at low cost is a kind of SCR denitration of great exploitation potential, and is carried out in various metals Combination, with preferable catalytic performance and on the basis of stability, temperature window is applied in broadening, especially has preferable low temperature Active and anti-H2O,SO2, heavy metal and dust poison ability, finally obtained the Fe-Ce-Ni-Zn/TiO of the present invention2Five yuan of gold Belong to composite oxide catalysts.Fe-Ce-Ni-Zn/TiO provided by the invention2Five yuan of metal composite oxide catalysts, can be with The advantages of regarding as iron-based, titanium-based or cerium base catalyst, and combining above-mentioned catalyst, each component cooperate, and compensate for original There is the deficiency of single catalyst.The addition of wherein Fe can improve the low temperature active and sulfur poisoning resistance of denitrating catalyst, but SO in flue gas2It is very big to the activity influence of denitrating catalyst, and also not for the influencing mechanism of different catalyst system and catalyzings Together, and middle low-temperature denitration activity is still insufficient, and the multi-element metal oxide of the present invention effectively raises the comprehensive of antitoxinization Conjunction ability;Elements C e is nontoxic, rich reserves, and has excellent redox property, but low temperature active and sulfur poisoning-resistant energy Power is insufficient, and the multi-element metal oxide of the present invention effectively compensates for its drawbacks described above.Fe-Ce-Ni- provided by the invention Zn/TiO2Five yuan of metal composite oxide catalysts have anti-H as SCR catalyst for denitrating flue gas2O,SO2, heavy metal and powder The advantages that toxic dust ability is strong, denitration is at low cost also has higher thermal stability, wider temperature window and preferable low Warm denitration activity.The experimental results showed that Fe-Ce-Ni-Zn/TiO provided by the invention2Five yuan of metal composite oxide catalysts, Catalytic efficiency and catalytic activity temperature are adjustable with synthesis component, and water resistant Sulfur tolerance is preferable, in H2O and SO2Existing a certain range Interior, catalytic efficiency is stablized 91% or more.
Description of the drawings
Fig. 1 is the SEM electromicroscopic photographs of multi-element metal oxide powder prepared by the embodiment of the present invention 1;
Fig. 2 is the EDS energy spectrum diagrams of multi-element metal oxide powder prepared by the embodiment of the present invention 1;
Fig. 3 is the denitration catalyst rate detection figure of multi-element metal oxide powder prepared by the embodiment of the present invention 1.
Specific implementation mode
In order to further appreciate that the present invention, the preferred embodiments of the invention are described with reference to embodiment, but It is it should be appreciated that these descriptions are only the feature and advantage further illustrated the present invention rather than to patent requirements of the present invention Limitation.
All raw materials of the present invention, are not particularly limited its source, buying on the market or according to people in the art It is prepared by conventional method known to member.
All raw materials of the present invention, are not particularly limited its purity, and present invention preferably employs analyze pure or metal composite oxygen The purity of compound field routine.
The present invention provides a kind of multicomponent catalyst for denitrating flue gas, specially a kind of Fe-Ce-Ni-Zn/TiO2Five First metal composite oxide catalyst.
The definition of the multi-element metal oxide is not particularly limited in the present invention, with well known to those skilled in the art more First metal oxide or composite oxide of metal.The present invention is to the ingredient of the multi-metal oxide catalyst without spy It does not limit, those skilled in the art can select and adjust according to practical situations, raw material condition and product requirement.
The present invention is to be more advantageous to SCR denitrating flue gas, is especially more advantageous to the middle low temperature SCR denitration of power-plant flue gas, institute State element of Fe/Ti, i.e., the molar ratio of the described element of Fe and element ti is preferably (0.2~0.7):1, more preferably (0.2~ 0.6):1, more preferably (0.3~0.5):1, most preferably (0.35~0.45):1;The Elements C e/Ti, i.e., the described Elements C e Molar ratio with element ti is preferably (0.05~0.8):1, more preferably (0.2~0.5):1, more preferably (0.3~0.5): 1, most preferably (0.35~0.45):1;The molar ratio of the element Ni/Ti, i.e., the described element Ni and element ti is preferably (0.2 ~0.6):1, more preferably (0.3~0.5):1, more preferably (0.35~0.5):1, most preferably (0.35~0.45):1;Institute State element Zn/Ti, i.e., the molar ratio of the described element Zn and element ti is preferably (0.05~0.5):1, more preferably (0.1~ 0.5):1, more preferably (0.2~0.4):1, most preferably (0.3~0.4):1.
The pattern of the multi-metal oxide catalyst is not particularly limited in the present invention, ripe with those skilled in the art The pattern for the multi-metal oxide catalyst known is not particularly limited, and those skilled in the art can be according to practical application feelings Condition, raw material condition and product requirement are selected and are adjusted, and catalyst of the present invention is preferably nano material, the catalysis The granularity of agent is preferably 50~3500 mesh, more preferably 100~3000 mesh, more preferably 500~3000 mesh, most preferably 1000 ~2000 mesh.Catalyst of the present invention preferably has porous structure;The porosity of the catalyst is preferably 2.5~ 1500m2/ g, more preferably 10~1000m2/ g, more preferably 100~400m2/ g, most preferably 300~400m2/g;It is described to urge The specific surface area of agent is preferably 0.008~0.48cm3/ g, more preferably 0.01~0.30cm3/ g, more preferably 0.06~ 0.25cm3/ g, most preferably 0.15~0.25cm3/g.Catalyst of the present invention for denitrating flue gas is preferred for SCR cigarettes The catalyst of qi exhaustion nitre is more preferably used for the catalyst of middle low-temperature smoke air SCR denitration, is more specifically preferred in power-plant flue gas The catalyst of low temperature SCR denitration.
The present invention is preferably 220~350 DEG C to the temperature in use of the catalyst, more preferably 230~330 DEG C, more excellent It is selected as 250~280 DEG C, most preferably 260~270 DEG C;Wherein low temperature temperature in use can be 200~250 DEG C, or be 210 ~240 DEG C, it is either 220~230 DEG C again or is 220~225 DEG C.
Above-mentioned steps of the present invention provide a kind of Fe-Ce-Ni-Zn/TiO2Five yuan of metal composite oxide catalysts, can be with The advantages of regarding as iron-based, titanium-based or cerium base catalyst, and combining above-mentioned catalyst, each component cooperate, and compensate for original There is the deficiency of single catalyst.The present invention further optimizes combination to component, with TiO2For carrier, low temperature is urged during Fe is used as Change doped body, rare earth metal Ce, transition metal Zn and Ni are prepared for multicomponent Fe-Ce- as enhancing catalytic performance auxiliary agent Ni-Zn/TiO2Five yuan of metal composite oxide catalysts, each component flexible ratio is adjustable, and not only synthesis cost is relatively low, Er Qiegeng Add the low temperature SCR denitration suitable for power-plant flue gas.Fe-Ce-Ni-Zn/TiO provided by the invention2Five yuan of metal composite oxidations Object catalyst has anti-H2O,SO2, heavy metal and dust poison the advantages that ability is strong, denitration is at low cost, also there is higher heat Stability, wider temperature window and preferable low-temperature denitration activity.
The present invention also provides a kind of preparation methods of above-mentioned multicomponent catalyst for denitrating flue gas, including following step Suddenly:
A soluble source of iron, soluble cerium source, soluble nickel source, soluble Zn source, titanium dioxide) are dissolved in polyvinyl alcohol In aqueous solution, a certain amount of titania powder is added and is mixed, dry after being vigorously stirred, irradiation obtains intermediate powder;
B it) will be ground after intermediate powder calcination that above-mentioned steps obtain, obtain the catalyst for denitrating flue gas.
The present invention especially indicates the range of choice and optimum principle of the poly metal oxide nano material, such as nothing, It is consistent with the range of choice and optimum principle of the catalyst nano material that is previously used for denitrating flue gas, it no longer goes to live in the household of one's in-laws on getting married one by one herein It states.
Soluble source of iron, soluble cerium source, soluble nickel source, soluble Zn source, titanium dioxide are dissolved in by the present invention first In polyvinyl alcohol water solution, a certain amount of titania powder is added and is mixed, dry after being vigorously stirred, irradiation obtains centre Powder.
After low concentration polyethylene alcohol is dissolved in the water, aqueous solution has certain stickiness and mobility, a variety of inorganic metal acid Salt, which is added in low concentration polyethylene alcohol solution, preferably to be connect by the stickiness of polyvinyl alcohol itself and functional group Touch reaction.And in high-temperature calcination processing, high molecular polymer polyvinyl alcohol can be completely removed, and not interfere with multi-element metal The generation of oxide catalyst.The mass concentration of the polyvinyl alcohol water solution is preferably 0.1%-4%.The present invention is to described poly- The addition of vinyl alcohol aqueous solution is not particularly limited, using the ratio of final products as standard, pilot process consume or real Border inventory, those skilled in the art can select and adjust according to practical condition, raw material condition and product requirement It is whole.
The soluble source of iron is not particularly limited in the present invention, is with soluble source of iron well known to those skilled in the art Can, those skilled in the art can select and adjust, this hair according to practical situations, raw material condition and product requirement The bright soluble source of iron preferably includes bivalent soluble source of iron and/or trivalent solubility source of iron, more preferably bivalent soluble Source of iron or trivalent solubility source of iron;It is of the present invention solubility source of iron specifically preferably include ferric sulfate, ferrous sulfate, iron chloride, It is one or more in frerrous chloride, ferric nitrate and ferrous nitrate, more specifically preferably ferric sulfate, ferrous sulfate, iron chloride, chlorine Change ferrous, ferric nitrate or ferrous nitrate, most preferably ferric nitrate.The present invention is not special to the addition of the soluble source of iron Limitation, using the ratio of final products as standard, pilot process consume or practical inventory, those skilled in the art can roots It is selected and is adjusted according to practical condition, raw material condition and product requirement.
The soluble cerium source is not particularly limited in the present invention, is with soluble cerium source well known to those skilled in the art Can, those skilled in the art can select and adjust, this hair according to practical situations, raw material condition and product requirement The bright soluble cerium source preferably includes one or more in cerous sulfate, cerium chloride and cerous nitrate, more preferably cerous sulfate, chlorine Change cerium or cerous nitrate, most preferably cerous nitrate.The addition in the soluble cerium source is not particularly limited in the present invention, with final The ratio of product is standard, and pilot process consume or practical inventory, those skilled in the art can be according to actual productions Situation, raw material condition and product requirement are selected and are adjusted.
The soluble nickel source is not particularly limited in the present invention, is with soluble nickel source well known to those skilled in the art Can, those skilled in the art can select and adjust, this hair according to practical situations, raw material condition and product requirement The bright soluble nickel source preferably includes one or more in nickel sulfate, nickel chloride and nickel nitrate, more preferably nickel sulfate, chlorine Change nickel or nickel nitrate, most preferably nickel nitrate.The addition of the soluble nickel source is not particularly limited in the present invention, with final The ratio of product is standard, and pilot process consume or practical inventory, those skilled in the art can be according to actual productions Situation, raw material condition and product requirement are selected and are adjusted.
The soluble Zn source is not particularly limited in the present invention, is with soluble Zn source well known to those skilled in the art Can, those skilled in the art can select and adjust, this hair according to practical situations, raw material condition and product requirement The bright soluble Zn source preferably includes one or more in zinc sulfate, zinc chloride and zinc nitrate, more preferably zinc sulfate, chlorine Change zinc or zinc nitrate, most preferably zinc nitrate.The addition in the soluble Zn source is not particularly limited in the present invention, with final The ratio of product is standard, and pilot process consume or practical inventory, those skilled in the art can be according to actual productions Situation, raw material condition and product requirement are selected and are adjusted.
The addition of the titanium dioxide is not particularly limited in the present invention, using the ratio of final products as standard, Pilot process consumes or practical inventory, those skilled in the art can be according to practical condition, raw material condition and products It is required that being selected and being adjusted.
The mode and condition of the drying is not particularly limited in the present invention, with drying side well known to those skilled in the art Formula and condition, those skilled in the art can select according to practical condition, raw material condition and product requirement And adjustment.The mode of drying of the present invention is preferably dried using microwave dryer.Microwave drying is a kind of novel do Dry mode.When dry, microwave energy directly acts on medium molecule and is converted into thermal energy, since there is microwave penetration performance to make in medium It heats simultaneously outside, heat transfer is not needed, so heating speed is very fast.Simultaneously regardless of object any shape, due to Jie of object Matter is inside and outside to be heated simultaneously, and the internal-external temperature difference of material is small, and homogeneous heating makes dry mass greatly improve.The time of the drying is excellent It is selected as 10~60 minutes, more preferably 20~40 minutes, most preferably 20~30 minutes.
The mode and condition of the irradiation is not particularly limited in the present invention, with irradiation side well known to those skilled in the art Formula and condition, those skilled in the art can select according to practical condition, raw material condition and product requirement And adjustment.The mode of irradiation of the present invention is preferably irradiated using low-energy electronic accelerator irradiation devices.Electron accelerator With room temperature, it is not damaged, without residual hazard, environmental protection, low energy consumption, operation it is easy to operate, high degree of automation, be suitable for large-scale industry The features such as metaplasia is produced.Ultrasound needs 6 hours, and microwave needs 20min (but in fact not enough uniformly effectively, energy or low).It is described Irradiation is 0.1-0.3MeV, more preferably 0.15-0.25MeV, most preferably 0.18-0.22MeV;The irradiation time is 1- 3 minutes;More preferably 1.5-2.5 minutes, most preferably 1.8-2.2 minutes.
The present invention will finally be ground after intermediate powder calcination that above-mentioned steps obtain, obtain the catalysis for denitrating flue gas Agent.
The mode and condition of the calcining is not particularly limited in the present invention, with calcining side well known to those skilled in the art Formula and condition, those skilled in the art can select according to practical condition, raw material condition and product requirement And adjustment, the mode of calcining of the present invention is preferably Muffle furnace, is more preferably calcined in air atmosphere;The temperature of the calcining Preferably 400~600 DEG C of degree, more preferably 500~575 DEG C, most preferably 550~560 DEG C;The time of the calcining is specifically excellent It is selected as 0.5~2.5 hour, more preferably 1~2 hour, most preferably 1.5~1.8 hours.
The mode being vigorously stirred and condition is not particularly limited in the present invention, with play well known to those skilled in the art Strong agitating mode and condition, those skilled in the art can be according to practical condition, raw material condition and product requirements It is selected and is adjusted.The time being vigorously stirred is 3-5 minutes.
The mode and condition of the grinding is not particularly limited in the present invention, with grinding side well known to those skilled in the art Formula and condition, those skilled in the art can select according to practical condition, raw material condition and product requirement And adjustment, the granularity of grinding of the present invention is preferably 50~3800 mesh, more preferably 100~3000 mesh, more preferably 500~ 2500 mesh, most preferably 1000~2000 mesh.
Above-mentioned steps of the present invention provide a kind of multicomponent catalyst for denitrating flue gas, i.e. Fe-Ce-Ni-Zn/TiO2Five The preparation method of first metal composite oxide catalyst.The present invention particularly prepares the catalyst using hydro-thermal method, Fe, Ce, Ni, Good interaction occurs for Zn and Ti groups branch, and the interworking of catalyst components can be made to reach more preferably effect, improved whole The redox property of body metal composite oxide catalyst, low-temperature catalytic oxidation NO are NO2Performance, while helping to be catalyzed The crystal grain refinement of agent, surface area increase, and provide more activity for SCR reactions, finally denitration performance are promoted to be substantially improved, carried simultaneously High low temperature SCR denitration activity so that denitration temperature window is substantially widened, and is effectively extended to low-temperature space, effective solution Low-temperature denitration activity is relatively low in existing ferrum-based catalyst, and preparation process is not mature enough, limit its large-scale industry and answer Inherent shortcoming is more appropriately applied to the removing of the discharged nitrogen oxides of China's coal fired thermal power plant.The experimental results showed that this The multi-element metal oxide provided is provided, catalytic efficiency and catalytic activity temperature are adjustable with synthesis component, and water resistant Sulfur tolerance compared with It is good, anti-H2O,SO2, that heavy metal and dust poison ability is strong, in H2O and SO2In existing a certain range, catalytic efficiency is stablized 91% or more.
In order to further illustrate the present invention, it a kind of is urged with reference to embodiments for denitrating flue gas to provided by the invention Agent and preparation method thereof is described in detail, but it is to be understood that these embodiments are before being with technical solution of the present invention It puts and is implemented, give detailed embodiment and specific operating process, only the spy to further illustrate the present invention It seeks peace advantage, rather than limiting to the claimed invention, protection scope of the present invention are also not necessarily limited to following embodiments.
Embodiment 1
It is 0.2 by molar ratio:0.05:0.2:0.05:1 0.2g iron chloride, 0.09g cerium chlorides, 0.16g nickel chlorides and 0.04g zinc chloride, 0.5g titania powders are dissolved in 30mL polyvinyl alcohol water solutions (mass concentration 0.1%), are added certain Amount titania powder is mixed, and is put into microwave dryer 10 minutes after being vigorously stirred 3 minutes, is then placed in low-energy electron and adds In fast device irradiation devices, irradiation is set as 0.1MeV, and after processing in 1 minute, lower 400 DEG C of air atmosphere is calcined 0.5 hour, is ground into Powder.Quickly, Fe-Ce-Ni-Zn/TiO is efficiently prepared2Five yuan of metal composite oxide catalysts.
The multi-element metal oxide prepared to the embodiment of the present invention 1 characterizes.Fig. 1 is prepared by the embodiment of the present invention 1 The SEM electromicroscopic photographs of multi-element metal oxide powder.Fig. 2 is multi-element metal oxide powder prepared by the embodiment of the present invention 1 EDS energy spectrum diagrams.Fig. 3 is the XRD spectrum of multi-element metal oxide powder prepared by the embodiment of the present invention 1.Table 1 is multi-element metal oxygen The atomic percent of each component is corresponded in compound powder.
The atomic percent of each component is corresponded in 1 multi-element metal oxide powder of table
Element Atomic percent
O 62.08
Ti 20.78
Fe 4.54
Ni 4.26
Zn 1.58
Ce 6.75
Total amount: 100.00
By Fig. 2 and table 1 it is found that the controllable multi-element metal oxide of specific ratio has been prepared in the present invention.
Poly metal oxide nano material prepared by the embodiment of the present invention 1 is carried out using detection.
Test example one
The experimental provision reactor that SCR removes NO uses fixed bed quartz tube reactor, internal diameter 1cm, reaction temperature By the K-type thermocouple measurement in intercalation reaction device.Simulated flue gas condition is supplied using steel cylinder, flue gas includes Ar (with H2O), NO/Ar,O2,SO2/ Ar and NH3The flow of/Ar, gas are controlled and are adjusted by mass flowmenter with composition, steam H2O is by Ar By being taken out of after steam generating means, react using Ar as balanced gas.In the reaction starting stage, it is real first to carry out saturation absorption It tests, i.e., is re-introduced into NH after reactor inlet and outlet NO, concentration reach balance3Carry out SCR reactions.The practical typical flue gas of simulation Distribution composition:500ppmNO/Ar, 500ppmNH3/ Ar, 4%O2, Ar is (with H2O(10-30g/m3)) it is carrier gas.Temperature model It is 75-400 DEG C to enclose, and reaction pressure is normal pressure, and air speed ratio is 10000/h.Wherein NO and NH3Ratio run according to practical power plant When the mix proportion scheme that uses, be 1:1.The results are shown in Table 2.
Table 2Fe-Ce-Ni-Zn/TiO2Five yuan of composite oxide of metal are in different temperatures and SO2NO reduction conversions under concentration Rate
By testing result it is found that multi-element metal oxide prepared by the present invention, has wider denitration temperature window (220- 350 DEG C) and preferable low-temperature denitration activity (91% or more).
Test example two
It is urged since the various metallic elements released when the fuel combustions such as coal can be moved to by dust Agent surface makes to will also result in catalyst poisoning inactivation while catalyst blockage.Denitrating catalyst is urged to investigate dust Change activity influence, carries out antidusting experimental simulation in this project testing, the dust of experiment is derived from coal-fired boiler in power plant, by weight The dust of percentage 1%-10% is placed in quartz reactor leading portion, and control N2 air-flows are 200-2000mL/min, experimental temperature model Enclose is 150-400 DEG C.The SCR catalyst powder for being put among quartz reactor is placed in dust-contained airflow 3-36 hours, then Dust is removed to measure the denitration activity of SCR catalyst again in the typical reaction atmosphere of SCR denitration test device.Mould The distribution composition of quasi- practical typical flue gas:500ppmNO/Ar, 500ppmNH3/ Ar, 4%O2, Ar is (with H2O(10-30g/m3)) For carrier gas.Reaction pressure is normal pressure, and air speed ratio is 10000/h.Wherein NO and NH3Ratio use when being run according to practical power plant Mix proportion scheme, be 1:1.The results are shown in Table 3.
3 Fe-Ce-Ni-Zn/TiO of table2Five yuan of composite oxide of metal are under different weight percentage dust purge time NO restore conversion ratio
By testing result it is found that multi-element metal oxide prepared by the present invention, there is stronger anti-dust to poison ability, High NO conversion ratios can be maintained in 36 hours.
Test example three
China's fire coal ingredient is extremely complex, present in impurity many heavy metals can be discharged in burning, these a huge sum of money Category can be enriched to SCR catalyst surface in catalytic process, and catalyst poisoning is caused to inactivate.The present invention is with regard to several typical cases in flue dust Heavy metal element (Cu, As, Pb) is tested the activity influence of SCR denitration.It is real that this project carries out preventing from heavy metal Test tries:By CuO, PbO, A of incorporation weight percent 0.1%-5% respectivelyS2O3Catalyst afterwards carries out the de- of SCR catalyst The active measurement of nitre simulates the distribution composition of practical typical flue gas:500ppmNO/Ar, 500ppmNH3/ Ar, 4%O2, Ar is (adjoint H2O(10-30g/m3)) it is carrier gas.Reaction pressure is normal pressure, and air speed ratio is 10000/h.Wherein NO and NH3Ratio according to reality The mix proportion scheme that power plant uses when running is 1:1.
4 Fe-Ce-Ni-Zn/TiO of table2Five yuan of composite oxide of metal are under the incorporation of different weight percentage heavy metal NO restores conversion ratio
By testing result it is found that by testing result it is found that multi-element metal oxide prepared by the present invention, has stronger anti- Heavy metal poisons ability.
Embodiment 2
It is 0.7 by molar ratio:0.8:0.6:0.5:1 1.84g iron chloride, 3.64g cerium chlorides, 1.05g nickel chlorides and 1.09g zinc chloride, 1.3g titania powders are dissolved in 75mL polyvinyl alcohol water solutions (mass concentration 1.6%), are added certain Amount titania powder is mixed, and is put into microwave dryer 35 minutes after being vigorously stirred 4 minutes, is then placed in low-energy electron and adds In fast device irradiation devices, irradiation is set as 0.2MeV, and after processing in 2 minutes, lower 550 DEG C of air atmosphere is calcined 2 hours, is pulverized End.Quickly, Fe-Ce-Ni-Zn/TiO is efficiently prepared2Five yuan of metal composite oxide catalysts.
Poly metal oxide nano material prepared by the embodiment of the present invention 2 is carried out using detection.
Method is the same as embodiment 1.
By testing result it is found that multi-element metal oxide prepared by the present invention, anti-H2O,SO2, dust and heavy metal poison energy Power is strong, also has higher thermal stability, wider temperature window (220-350 DEG C) and preferable low-temperature denitration activity (91% or more).
Embodiment 3
It is 0.2 by molar ratio:0.2:0.2:0.2:1 0.44g ferric sulfate, 0.69g cerous sulfates, 0.33g nickel sulfates and 0.54g zinc sulfate, 0.7g titania powders are dissolved in 100mL polyvinyl alcohol water solutions (mass concentration 4%), are added a certain amount of Titania powder is mixed, and is vigorously stirred and is put into microwave dryer after five minutes 60 minutes, and low-energy electron acceleration is then placed in In device irradiation devices, irradiation is set as 0.3MeV, and after processing in 3 minutes, lower 600 DEG C of air atmosphere is calcined 2.5 hours, is pulverized End.Quickly, Fe-Ce-Ni-Zn/TiO is efficiently prepared2Five yuan of metal composite oxide catalysts.
Poly metal oxide nano material prepared by the embodiment of the present invention 3 is carried out using detection.
Method is the same as embodiment 1.
By testing result it is found that multi-element metal oxide prepared by the present invention, anti-H2O,SO2, dust and heavy metal poison energy Power is strong, also has higher thermal stability, wider temperature window (220-350 DEG C) and preferable low-temperature denitration activity (91% or more).
Above to the catalyst provided by the present invention for SCR denitrating flue gas, it to be especially used for low-temperature SCR in power-plant flue gas Catalyst of denitration and preparation method thereof.It is described in detail, specific case used herein is to the principle of the present invention And embodiment is expounded, the explanation of above example is only intended to help to understand that the method for the present invention and its core are thought Think, including best mode, and but also any person skilled in the art can put into practice the present invention, including manufactures and use Any device or system, and implement the method for any combination.It should be pointed out that coming for those skilled in the art It says, without departing from the principle of the present invention, can be with several improvements and modifications are made to the present invention, these improvement and modification It also falls within the protection scope of the claims of the present invention.The range of patent protection of the present invention is defined by the claims, and can Including those skilled in the art it is conceivable that other embodiment.It is not different from right if these other embodiments have and wants The structural element of character express is sought, or if they include and equivalent structure of the character express of claim without essence difference Element, then these other embodiments should also be included in the scope of the claims.

Claims (10)

1. a kind of multicomponent catalyst for denitrating flue gas, which is characterized in that it is Fe-Ce-Ni-Zn/TiO2Five yuan of metal composites Oxide catalyst.
2. multicomponent catalyst according to claim 1, which is characterized in that wherein,
The molar ratio of element of Fe/Ti is (0.2~0.7):1;
The molar ratio of Elements C e/Ti is (0.05~0.8):1;
The molar ratio of element Ni/Ti is (0.2~0.6):1;
The molar ratio of element Zn/Ti is (0.05~0.5):1.
3. multicomponent catalyst according to claim 1, which is characterized in that the catalyst has porous structure, described to urge The granularity of agent is 50~3500 mesh, and the porosity of the catalyst is 2.5~1500m2/ g, the specific surface area of the catalyst For 0.008~0.48cm3/g。
4. a kind of preparation method of the multicomponent catalyst described in claim 1 for denitrating flue gas, which is characterized in that including with Lower step:
A) by soluble source of iron, soluble cerium source, soluble nickel source, soluble Zn source, that titanium dioxide is dissolved in polyvinyl alcohol is water-soluble In liquid, a certain amount of titania powder is added and is mixed, dry after being vigorously stirred, irradiation obtains intermediate powder;
B it) will be ground after intermediate powder calcination that above-mentioned steps obtain, obtain the catalyst for denitrating flue gas.
5. preparation method according to claim 4, which is characterized in that the drying is dried using microwave dryer, Drying time is 10-60 minutes.
6. preparation method according to claim 4, which is characterized in that the irradiation is using low-energy electronic accelerator irradiation dress It sets and is irradiated, irradiation 0.1-0.3MeV, irradiation time is 1-3 minutes.
7. preparation method according to claim 4, which is characterized in that the calcination temperature is 400-600 DEG C, and the time is 0.5-2.5 hours.
8. preparation method according to claim 4, which is characterized in that the time being vigorously stirred is 3-5 minutes.
9. preparation method according to claim 4, which is characterized in that
The solubility source of iron includes one in ferric sulfate, ferrous sulfate, iron chloride, frerrous chloride, ferric nitrate and ferrous nitrate Kind is a variety of;
The solubility cerium source includes one or more in cerous sulfate, cerium chloride and cerous nitrate;
The solubility nickel source includes one or more in nickel sulfate, nickel chloride and nickel nitrate;
The soluble Zn source includes one or more in zinc sulfate, zinc chloride and zinc nitrate.
10. preparation method according to claim 4, which is characterized in that the mass concentration of the polyvinyl alcohol water solution is 0.1%-4%.
CN201810530813.XA 2018-05-29 2018-05-29 A kind of anti-H for denitrating flue gas2O,SO2, heavy metal and dust poison multicomponent catalyst Pending CN108686670A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810530813.XA CN108686670A (en) 2018-05-29 2018-05-29 A kind of anti-H for denitrating flue gas2O,SO2, heavy metal and dust poison multicomponent catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810530813.XA CN108686670A (en) 2018-05-29 2018-05-29 A kind of anti-H for denitrating flue gas2O,SO2, heavy metal and dust poison multicomponent catalyst

Publications (1)

Publication Number Publication Date
CN108686670A true CN108686670A (en) 2018-10-23

Family

ID=63848145

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810530813.XA Pending CN108686670A (en) 2018-05-29 2018-05-29 A kind of anti-H for denitrating flue gas2O,SO2, heavy metal and dust poison multicomponent catalyst

Country Status (1)

Country Link
CN (1) CN108686670A (en)

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102895872A (en) * 2011-07-28 2013-01-30 中国石油化工股份有限公司 Method for removing sulfur oxides and nitrogen oxides in catalytic cracking regeneration flue gas
CN103894185A (en) * 2014-04-01 2014-07-02 北京工业大学 Method for preparing selective catalytic reduction (SCR) denitration catalyst by taking TiO2-ZnO as composite carrier
CN106423197A (en) * 2016-12-05 2017-02-22 吉林省电力科学研究院有限公司 Multi-element catalyst for flue gas denitrification and preparation method thereof
CN106732624A (en) * 2016-12-05 2017-05-31 吉林省电力科学研究院有限公司 A kind of catalyst for denitrating flue gas and preparation method thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102895872A (en) * 2011-07-28 2013-01-30 中国石油化工股份有限公司 Method for removing sulfur oxides and nitrogen oxides in catalytic cracking regeneration flue gas
CN103894185A (en) * 2014-04-01 2014-07-02 北京工业大学 Method for preparing selective catalytic reduction (SCR) denitration catalyst by taking TiO2-ZnO as composite carrier
CN106423197A (en) * 2016-12-05 2017-02-22 吉林省电力科学研究院有限公司 Multi-element catalyst for flue gas denitrification and preparation method thereof
CN106732624A (en) * 2016-12-05 2017-05-31 吉林省电力科学研究院有限公司 A kind of catalyst for denitrating flue gas and preparation method thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
张蕾: "《烟气脱硫脱硝技术及催化剂的研究进展》", 31 July 2016 *

Similar Documents

Publication Publication Date Title
CN106423197A (en) Multi-element catalyst for flue gas denitrification and preparation method thereof
CN103752321B (en) The preparation method of hierarchy bimetallic composite oxide denitrification catalyst
CN101920213B (en) Low temperature SCR denitration catalyst taking organic metal framework as carrier and preparation method thereof
CN104646022B (en) A kind of honeycomb fashion low-temperature denitration catalyst and preparation method thereof
CN101284238B (en) Catalysts for stationary source ammine selective catalytic reduction for nitrous oxides
CN106732624A (en) A kind of catalyst for denitrating flue gas and preparation method thereof
CN102658155B (en) Preparation method of supported type denitration catalyst
CN104722307A (en) Iron-based low-temperature SCR denitration catalyst and preparation method thereof
CN105289644B (en) A kind of flat sulfur resistive low temperature SCR denitration catalyst and preparation method thereof
CN107308944B (en) A kind of TiO 2-based catalyst and its preparation method and application
CN109569587A (en) A kind of manganese-based low-temperature catalyst for denitrating flue gas and preparation method thereof
CN102366722A (en) Denitrition catalyst with mercury removal effect and its preparation method
CN103752322A (en) Preparation method for cobalt-manganese oxide denitrified catalyst with cubic micro nano composite structure
CN102941083A (en) Medium/low-temperature core-shell denitration catalyst and preparation method and application thereof
CN104772014A (en) Combined denitration device for flue gas of cement rotary kiln and denitration technology for flue gas
CN110947394A (en) ZIF-67-Mn/Co-based low-temperature NO oxidation catalyst, and preparation method and application thereof
CN112138725B (en) Catalytic decomposition of N2Preparation method of cobalt-based metal organic framework derivative catalyst of O
CN105879879A (en) High-sulfur-resistant ultralow-temperature SCR (Selective Catalytic Reduction) denitration catalyst and preparation method thereof
CN105618028A (en) Catalyst for coke oven smoke denitration and preparation method thereof
CN106238064A (en) A kind of ferrum cerium red mud composite oxides denitration catalyst agent material and preparation method thereof
CN112718018B (en) Lanthanum cobaltite perovskite catalyst treated by acetic acid and preparation method thereof
CN108607574A (en) A kind of anti-H2O、SO2With the catalyst for denitrating flue gas and preparation method thereof of heavy metal detoxification evil
CN105727965A (en) Copper, zirconium, cerium and titanium composite oxide catalyst for flue gas denitrification and preparation method thereof
CN205995275U (en) A kind of middle low-temperature denitration of flue gas device
CN108579756A (en) One main laminaria shape Mn-Fe bimetallic oxide load Cs eO2Catalyst and preparation method and application

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
RJ01 Rejection of invention patent application after publication

Application publication date: 20181023

RJ01 Rejection of invention patent application after publication