[go: up one dir, main page]

CN109158108A - A kind of catalyst and its preparation method and application for low-temperature denitration of flue gas - Google Patents

A kind of catalyst and its preparation method and application for low-temperature denitration of flue gas Download PDF

Info

Publication number
CN109158108A
CN109158108A CN201811057578.5A CN201811057578A CN109158108A CN 109158108 A CN109158108 A CN 109158108A CN 201811057578 A CN201811057578 A CN 201811057578A CN 109158108 A CN109158108 A CN 109158108A
Authority
CN
China
Prior art keywords
catalyst
flue gas
low
temperature
antimony
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
CN201811057578.5A
Other languages
Chinese (zh)
Inventor
郭瑞堂
王�忠
王忠一
柳星宇
施旭
秦浩
孙晓
刘帅伟
刘健
潘卫国
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.)
Shanghai University of Electric Power
Original Assignee
Shanghai University of Electric Power
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 Shanghai University of Electric Power filed Critical Shanghai University of Electric Power
Priority to CN201811057578.5A priority Critical patent/CN109158108A/en
Publication of CN109158108A publication Critical patent/CN109158108A/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
    • B01J23/84Catalysts 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
    • B01J23/843Arsenic, antimony or bismuth
    • B01J23/8435Antimony
    • 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
    • B01J35/61Surface area
    • 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)
  • Environmental & Geological Engineering (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Catalysts (AREA)

Abstract

本发明涉及一种用于低温烟气脱硝的催化剂及其制备方法和应用,该催化剂以二氧化钛为载体,以氧化铜为活性组分,氧化锑为助剂,其中,锑、铜和钛的摩尔比分别为0.1~0.6:1:10,制备方法包括以下步骤:将铜源和锑源混合溶于溶剂中,并加入钛源溶液,搅拌;搅拌过程中滴加乙醇水溶液,直到混合液形成透明胶状固体为止,然后室温下静置,直到胶状固体出现明显裂纹;当胶状固体干裂后,干燥得到透明晶状前驱体,然后将前驱体高温煅烧,研磨后,即得到产品。与现有技术相比,本发明催化剂在250‑350℃低温段内能达到90%的脱除NOx效率,具有较高的抗硫性能,抗水性能,具备一定抗毒化能力,具有较强的工业应用价值,可广泛应用于烟气中NOx的脱除。

The invention relates to a catalyst for low-temperature flue gas denitration, a preparation method and application thereof. The catalyst uses titanium dioxide as a carrier, copper oxide as an active component, and antimony oxide as an auxiliary agent, wherein the molar ratio of antimony, copper and titanium is The ratios are 0.1-0.6:1:10, respectively. The preparation method includes the following steps: mixing and dissolving the copper source and the antimony source in the solvent, adding the titanium source solution, and stirring; adding the ethanol aqueous solution dropwise during the stirring process until the mixed solution becomes transparent. After the colloidal solid is dry and cracked, the transparent crystalline precursor is obtained by drying, and then the precursor is calcined at high temperature and ground to obtain the product. Compared with the prior art, the catalyst of the invention can achieve 90% removal efficiency of NOx in the low temperature range of 250-350°C, has high sulfur resistance, water resistance, certain anti-poisoning ability, and has strong anti-toxicity. It has industrial application value and can be widely used in the removal of NOx from flue gas.

Description

A kind of catalyst and its preparation method and application for low-temperature denitration of flue gas
Technical field
The present invention relates to catalyst technical fields, and in particular to a kind of catalyst and its preparation for low-temperature denitration of flue gas Methods and applications.
Background technique
NOx is one of the important atmosphere pollution of coal fired thermal power plant discharge, is the important origin cause of formation of acid rain and photochemical fog, The improvement of NOx becomes the focus that atmosphere pollution is administered.NH3SCR technology (SCR) be with NH3For also Former agent reacts with NO under the effect of the catalyst and generates N2And H20, the research of catalysts is the key content of SCR research. The catalyst applied to the mainstream in SCR reaction is V at present2O5-WO3/TiO2Although this catalyst has high activity and height Sulfur resistance, but still there are some problems: first is that catalyst higher cost, second is that operation temperature necessarily is greater than 623K, it is higher Catalyst operation temperature must be necessarily arranged at SCR reaction bed before air preheater, deduster and desulfurizer, and this cloth Catalyst will necessarily be exposed to high concentration SO by the mode of setting2Under the flue gas of particle dusty, there is very strong poison to catalyst Change effect seriously affects catalyst efficiency and service life, therefore it is necessary to develop cheap effective low-temperature SCR catalyst.
Copper oxide is widely used in low-temperature SCR in past research due to having quite high reproducibility at low temperature The exploitation of denitrating technique catalyst.It is not high for the copper titanium catalyst activity of low-temperature denitration of flue gas in the prior art, especially Low-temperature catalyzed efficiency is relatively low, and water resistant, anti-sulfur dioxide ability are poor, and the economy of production run is poor, when practical application, especially It is in the SCR reaction unit of traditional coal-burning power plant, catalyst life cannot ensure.If it is anti-to develop efficient water resistant Sulphur SCR low temperature catalyst, then can be very good to solve the above problems.
Summary of the invention
The purpose of the present invention is to solve the above-mentioned problems and provide a kind of catalyst for low-temperature denitration of flue gas and Preparation method and application.
The purpose of the present invention is achieved through the following technical solutions:
A kind of catalyst for low-temperature denitration of flue gas, the catalyst are activity with copper oxide using titanium dioxide as carrier Component, antimony oxide are auxiliary agent, wherein the molar ratio of antimony, copper and titanium is respectively 0~0.6:1:10, it is preferable that the antimony, copper and The molar ratio of titanium is respectively 0.4~0.6:1:10, most preferably 0.4:1:10.
A kind of preparation method of the catalyst for low-temperature denitration of flue gas, comprising the following steps:
(1) copper source and antimony source are mixed and is dissolved in solvent, and titanium source solution is added, stirred;
(2) ethanol water is added dropwise in whipping process, until mixed liquor forms clear gummy solid, then at room temperature It stands, until obvious crackle occurs in colloidal solid;
(3) after colloidal solid is dry and cracked, it is dried to obtain transparent crystalline presoma, then by presoma high-temperature calcination, grinding Afterwards to get arrive product.
Preferably, step (1) copper source is nitrate trihydrate copper, and the antimony source is antimony acetate, and the solvent is anhydrous second The mixed liquor that alcohol and ethylene glycol molar ratio are 10:3.
Preferably, step (1) the titanium source solution is the solution of tetrabutyl titanate for being dissolved in dehydrated alcohol.
Preferably, step (2) ethanol water is the ethanol water of mass fraction 20%.
Preferably, the dry temperature of step (3) is 100 DEG C, and the processing time is 72~96h.
Preferably, the temperature of step (3) high-temperature calcination is 550 DEG C, and calcination time is 4~6h.
The catalyst is used for denitrating flue gas, includes the following steps:
(1) before denitration experiment starts, it is first passed through argon gas 5min, catalyst and gas piping is purged under room temperature, removes residual Residual air body and impurity;
(2) it is passed through NO, i.e., makes NO gas by catalyst at normal temperature, achievees the purpose that pre- absorption, so that catalyst To the close saturation of the physical absorption of NO, the subsequent error for calculating denitration efficiency is avoided;
(3) when pre- absorption reaches saturation, opening program is passed through O2And NH3And vapor, fixed bed reactors are sent to, Controlling reaction temperature is 100 DEG C -350 DEG C, flow velocity 1000ml/min.Air speed is 108000h-1, under the effect of the catalyst, will NO is reduced to as N2
(4) flue gas by denitrating catalyst reaction front and back NO concentration by ThermoNicoletiS50 flue gas analyzer Lai It is recorded, catalyst is calculated to the denitration efficiency of flue gas according to NO amount variation in flue gas.
The simulated flue gas composition: NO 600ppm, NH3For 500ppm, oxygen 4%, H2O content is 5%, residual air Body is as Balance Air.
For the present invention using titanium dioxide as carrier, in addition copper oxide adds a certain amount of antimony oxide as active component, catalysis The preparation of agent uses sol-gal process, and titanium dioxide, copper oxide, antimony oxide are flocked together by gel, enables active component Sufficiently it is supported on above carrier.XRD characterization the result shows that, the doping of antimony element can inhibit the growth of CuO crystallite dimension, enhancing member Element is conducive to the suction of gas in reaction process to increase the specific surface area of catalyst surface in the dispersibility of catalyst surface It is attached.XPS characterization result shows that the antimony element in catalyst is mainly embodied with pentavalent, and in active that best catalyst Hydroxyl pentavalent antimony content is especially more, and hydroxyl quinquevalence antimony is conducive to NH4+- Bronsted acid site is increased, by In-situ Infrared into Row Analysis on Mechanism, the results showed that optimal catalyst low-temperature zone NH4+- Bronsted acid site increased significantly, the conclusion one with XPS It causes, in addition, the cupric in optimal catalyst also increases on year-on-year basis, this shows increasing doped with conducive to cupric for antimony element, It is easily reduced when carrying out SCR reaction.In addition, carrying out the oxidation experiment of NO, optimal catalyst shows best oxidation susceptibility, this May with antimony element adulterate promote it is cupric increase it is related.Also along with the oxidation of NO in SCR reaction process, and aoxidize Product NO2More, " Fast-SCR " reacts easier progress, and also the higher present invention compares denitration efficiency with prior art, skill Art progress is significant.
In addition, In-situ Infrared Characterization the result shows that, the L-H mechanism and E-R mechanism of the catalyst coexist, in the L- of low-temperature zone In H mechanism, antimony element carries out chemisorption, while the nitrous acid that absorption is easy to react in catalyst surface doped with conducive to ammonia Class group, gradually stronger Nitrates of thermal stability less.
Catalyst of the present invention can be to the nitrogen oxides of exhaust gas of the discharges such as power generation gas turbine and coal-burning boiler at Reason can significantly improve low-temperature denitration activity, nitrogen selective and the anti-sulfur dioxide ability of water resistant.
Compared with prior art, the activity of catalyst provided by the invention Reduction of NO with higher in low temperature, I.e. when denitration temperature is 250 DEG C, the conversion ratio of NO reaches 91% or more.Catalyst preparation process is simple, environment friendly and pollution-free, adopts Catalyst is overcome because active component is single and easy by vapor and SO with bimetallic oxide component2The problem of influence, tool There is stronger industrial application value.The catalyst that the present invention is prepared at 150-450 DEG C, especially at 300 DEG C hereinafter, compared with Baseline catalyst is in activity and the anti-SO of water resistant2It is greatly improved in ability, is more conducive to that SCR denitration device is made to be arranged in thermal power plant's tail Portion's flue improves thermal power plant's performance driving economy to reduce waste heat loss.
Detailed description of the invention
Fig. 1 is the catalytic efficiency that catalyst of the present invention and typical catalyst carry out denitrating flue gas under the same conditions.
Specific embodiment
The present invention is further described with specific embodiment below, but is not intended to limit the present invention.
Catalytic reactor used in example of the invention use the outer diameter purchased from Zhejiang Fan Tai Instrument Ltd. for The 4100 type fixed bed micro anti-evaluation devices of 16mm, long 480mm, unstripped gas enter reactor by preheating, and reaction temperature exists 100-350 DEG C, flow velocity 1000ml/min, air speed ratio is 108000h-1
Simulated flue gas composition: NO 600ppm, NH3For 600ppm and O2It is 5%, remaining gas Ar is as Balance Air, gas Body flow is controlled by the CS200 type mass flowmenter purchased from Beijing Co., Ltd of Sevenstar Huachuang Electronic.
NO used in the present invention, NH3Molar concentration is 1%, is purchased from Shanghai Wei Chuan calibrating gas Co., Ltd, O2It is 5%, Remaining gas Ar is purchased from Jiangnan mixed gas Co., Ltd as Balance Air;Drug used is purchased from Aladdin.
Embodiment 1
What is made according to the present invention is used to be catalyzed the catalyst of the NO of reduction, wherein doping component, mole of antimony, copper and titanium Than for 0:1:10.Specific preparation step is as follows:
By 1.208g nitrate trihydrate copper dissolution in 40 milliliters of dehydrated alcohols, the dissolution of acceleration in 10 minutes is stirred at room temperature, so It is 17.108g butyl titanate ethanol solution that 30 milliliters of Solute mass, which are followed by added, and stirring makes solution full and uniform mixed for 5 minutes It closes;Continue to stir, the alcoholic solution of mass fraction 20% is gradually added dropwise in whipping process, is until mixed liquor gradually forms gel Only.Resulting colloidal solid is stood into 12h at room temperature, colloid cracks, and putting it into drying in baking oven, for 24 hours, removal is urged Dehydrated alcohol and moisture in agent, obtain crystalline presoma.Then resulting presoma is put into Muffle furnace at 550 DEG C 4h is calcined under environment, can be prepared by a kind of high-efficiency mercury removal catalyst (A).
Embodiment 2
What is made according to the present invention is used to be catalyzed the catalyst of the NO of reduction, wherein doping component, mole of antimony, copper and titanium Than for 0.1:1:10.Specific preparation step is as follows:
By 1.208g nitrate trihydrate copper dissolution in 40 milliliters of dehydrated alcohols, the dissolution of acceleration in 10 minutes is stirred at room temperature, so It is 17.108g butyl titanate ethanol solution that 30 milliliters of Solute mass, which are followed by added, and stirring makes solution full and uniform mixed for 5 minutes It closes;0.149g antimony acetate is dissolved in 20mL ethylene glycol, stirring 30min makes it completely dissolved, and is then added in mixed liquor. Continue to be stirred liquid, the alcoholic solution of mass fraction 20% be gradually added dropwise in whipping process, until mixed liquor gradually form it is solidifying Until glue.Resulting colloidal solid is stood into 12h at room temperature, colloid cracks, and puts it into drying in baking oven and for 24 hours, goes Except the dehydrated alcohol in catalyst, ethylene glycol and moisture obtain crystalline presoma.Resulting presoma is then put into Muffle furnace In calcine 4h in the environment of 550 DEG C, can be prepared by a kind of efficient cryogenic denitrating catalyst (B).
Embodiment 3
What is made according to the present invention is used to be catalyzed the catalyst of the NO of reduction, wherein doping component, mole of antimony, copper and titanium Than for 0.2:1:10.Specific preparation step is as follows:
By 1.208g nitrate trihydrate copper dissolution in 40 milliliters of dehydrated alcohols, the dissolution of acceleration in 10 minutes is stirred at room temperature, so It is 17.108g butyl titanate ethanol solution that 30 milliliters of Solute mass, which are followed by added, and stirring makes solution full and uniform mixed for 5 minutes It closes;0.2988g antimony acetate is dissolved in 20mL ethylene glycol, stirring 30min makes it completely dissolved, and is then added to mixed liquor In.Continue to be stirred liquid, the alcoholic solution of mass fraction 20% is gradually added dropwise in whipping process, until mixed liquor gradually forms Until gel.Resulting colloidal solid is stood into 12h at room temperature, colloid cracks, and it puts it into baking oven and dries for 24 hours, The dehydrated alcohol in catalyst, ethylene glycol and moisture are removed, crystalline presoma is obtained.Resulting presoma is then put into Muffle 4h is calcined in the environment of 550 DEG C in furnace, can be prepared by a kind of efficient cryogenic denitrating catalyst (C).
Embodiment 4
What is made according to the present invention is used to be catalyzed the catalyst of the NO of reduction, wherein doping component, mole of antimony, copper and titanium Than for 0.4:1:10.Specific preparation step is as follows:
By 1.208g nitrate trihydrate copper dissolution in 40 milliliters of dehydrated alcohols, the dissolution of acceleration in 10 minutes is stirred at room temperature, so It is 17.108g butyl titanate ethanol solution that 30 milliliters of Solute mass, which are followed by added, and stirring makes solution full and uniform mixed for 5 minutes It closes;0.598g antimony acetate is dissolved in 20mL ethylene glycol, stirring 30min makes it completely dissolved, and is then added in mixed liquor. Continue to be stirred liquid, the alcoholic solution of mass fraction 20% be gradually added dropwise in whipping process, until mixed liquor gradually form it is solidifying Until glue.Resulting colloidal solid is stood into 12h at room temperature, colloid cracks, and puts it into drying in baking oven and for 24 hours, goes Except the dehydrated alcohol in catalyst, ethylene glycol and moisture obtain crystalline presoma.Resulting presoma is then put into Muffle furnace In calcine 4h in the environment of 550 DEG C, can be prepared by a kind of efficient cryogenic denitrating catalyst (D).
Embodiment 5
What is made according to the present invention is used to be catalyzed the catalyst of the NO of reduction, wherein doping component, mole of antimony, copper and titanium Than for 0.4:1:10.Specific preparation step is as follows:
By 1.208g nitrate trihydrate copper dissolution in 40 milliliters of dehydrated alcohols, the dissolution of acceleration in 10 minutes is stirred at room temperature, so It is 17.108g butyl titanate ethanol solution that 30 milliliters of Solute mass, which are followed by added, and stirring makes solution full and uniform mixed for 5 minutes It closes;0.896g antimony acetate is dissolved in 20mL ethylene glycol, stirring 30min makes it completely dissolved, and is then added in mixed liquor. Continue to be stirred liquid, the alcoholic solution of mass fraction 20% be gradually added dropwise in whipping process, until mixed liquor gradually form it is solidifying Until glue.Resulting colloidal solid is stood into 12h at room temperature, colloid cracks, and puts it into drying in baking oven and for 24 hours, goes Except the dehydrated alcohol in catalyst, ethylene glycol and moisture obtain crystalline presoma.Resulting presoma is then put into Muffle furnace In calcine 4h in the environment of 550 DEG C, can be prepared by a kind of efficient cryogenic denitrating catalyst (E).
Experiment test is first passed through fixed bed micro anti-evaluation device with the gaseous state NO in simulated flue gas before starting, and allows catalyst pair The absorption of gaseous mercury reaches saturation, avoids the reduction for causing the NO detected when reaction because of suction-operated;Simulate gas (flue gas Flow velocity 1000ml/min, gas concentration: NO 600ppm, NH3For 600ppm and O2Be 5%, remaining gas Ar) after mixing It is sent into fixed bed micro anti-evaluation device and NO is reduced to by N by catalyst action at 100 DEG C~350 DEG C2, the NO of inlet and outlet Concentration is detected using ThermoNicoletiS50 flue gas analyzer, and denitration effect is as shown in table 1.
The Activity evaluation tables of data of 1 different catalysts of table
As can be drawn from Table 1, using the catalyst that is prepared of the present invention and typical catalyst under the same conditions into 350 row denitrating flue gas, it is higher than typical catalyst denitration efficiency, when low-temperature zone denitration temperature is 200-300 DEG C, low-temperature denitration The denitration efficiency of SbOx-CuOx-TiOx catalyst D is than benchmark CuOx-TiOx catalyst A high 35%~40%.
Catalyst obtained above is respectively placed in 100ppmSO2And 5%H2The anti-SO of water resistant is carried out under O2Poison experiment, it is real It is as shown in Figure 1 to test result.The result shows that under the same conditions using the catalyst of the invention being prepared and typical catalyst Carry out anti-H2O, anti-SO2Experiment, the antitoxinization performance of SbOx-CuOx-TiOx catalyst D is than benchmark CuOx-TiOx catalyst A It is good.
To sum up, the catalyst that the present invention is prepared is anti-with water resistant in activity compared with baseline catalyst at 200~300 DEG C SO2It is greatly improved in ability, is more conducive to that SCR denitration device is made to be arranged in thermal power plant's back-end ductwork, to reduce waste heat loss, mentions High thermal power plant's performance driving economy.
The embodiments described above only express several embodiments of the present invention, and the description thereof is more specific and detailed, but simultaneously Limitations on the scope of the patent of the present invention therefore cannot be interpreted as.It should be pointed out that for those of ordinary skill in the art For, without departing from the inventive concept of the premise, various modifications and improvements can be made, these belong to guarantor of the invention Protect range.Therefore, the scope of protection of the patent of the invention shall be subject to the appended claims.

Claims (9)

1. a kind of catalyst for low-temperature denitration of flue gas, which is characterized in that the catalyst is using titanium dioxide as carrier, with oxidation Copper is active component, and antimony oxide is auxiliary agent, wherein the molar ratio of antimony, copper and titanium is respectively 0.1~0.6:1:10.
2. a kind of catalyst for low-temperature denitration of flue gas according to claim 1, which is characterized in that the antimony, copper and The molar ratio of titanium is respectively 0.4~0.6:1:10.
3. a kind of preparation method of the catalyst for low-temperature denitration of flue gas as described in claim 1, which is characterized in that including Following steps:
(1) copper source and antimony source are mixed and is dissolved in solvent, and titanium source solution is added, stirred;
(2) ethanol water is added dropwise in whipping process, it is then quiet at room temperature until mixed liquor forms clear gummy solid It sets, until obvious crackle occurs in colloidal solid;
(3) after colloidal solid is dry and cracked, it is dried to obtain transparent crystalline presoma, then by presoma high-temperature calcination, after grinding, i.e., Obtain product.
4. a kind of preparation method of catalyst for low-temperature denitration of flue gas according to claim 3, which is characterized in that step Suddenly (1) copper source is nitrate trihydrate copper, and the antimony source is antimony acetate, and the solvent is that dehydrated alcohol is with ethylene glycol molar ratio The mixed liquor of 10:3.
5. a kind of preparation method of catalyst for low-temperature denitration of flue gas according to claim 3, which is characterized in that step Suddenly (1) described titanium source solution is the solution of tetrabutyl titanate for being dissolved in dehydrated alcohol.
6. a kind of preparation method of catalyst for low-temperature denitration of flue gas according to claim 3, which is characterized in that step Suddenly (2) described ethanol water is the ethanol water of mass fraction 20%.
7. a kind of preparation method of catalyst for low-temperature denitration of flue gas according to claim 3, which is characterized in that step Suddenly (3) dry temperature is 100 DEG C, and the processing time is 72~96h.
8. a kind of preparation method of catalyst for low-temperature denitration of flue gas according to claim 3, which is characterized in that step Suddenly the temperature of (3) high-temperature calcination is 550 DEG C, and calcination time is 4~6h.
9. a kind of application of the catalyst for low-temperature denitration of flue gas as described in claim 1, which is characterized in that the catalyst For denitrating flue gas.
CN201811057578.5A 2018-09-11 2018-09-11 A kind of catalyst and its preparation method and application for low-temperature denitration of flue gas Pending CN109158108A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811057578.5A CN109158108A (en) 2018-09-11 2018-09-11 A kind of catalyst and its preparation method and application for low-temperature denitration of flue gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811057578.5A CN109158108A (en) 2018-09-11 2018-09-11 A kind of catalyst and its preparation method and application for low-temperature denitration of flue gas

Publications (1)

Publication Number Publication Date
CN109158108A true CN109158108A (en) 2019-01-08

Family

ID=64894818

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811057578.5A Pending CN109158108A (en) 2018-09-11 2018-09-11 A kind of catalyst and its preparation method and application for low-temperature denitration of flue gas

Country Status (1)

Country Link
CN (1) CN109158108A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111701591A (en) * 2020-06-16 2020-09-25 北京石油化工学院 Hydrogenation catalyst and preparation method thereof and method for preparing fatty alcohol by hydrogenation of fatty acid ester
CN112452326A (en) * 2020-11-25 2021-03-09 常州大学 Preparation method of copper black titanium catalyst and application of copper black titanium catalyst in selective catalytic oxidation denitration

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20120201732A1 (en) * 2011-02-07 2012-08-09 Millennium Inorganic Chemicals, Inc. Ce containing, v-free mobile denox catalyst
CN103055889A (en) * 2012-12-31 2013-04-24 上海电气石川岛电站环保工程有限公司 A kind of low-temperature denitrification MnOx-CuO-TiO2 catalyst and its preparation method and application
CN104338534A (en) * 2013-08-09 2015-02-11 中国石油化工股份有限公司 Compound copper oxide catalyst, preparation method and application thereof
CN104607198A (en) * 2015-01-29 2015-05-13 李灏呈 Vanadium-free plate-like denitration catalyst and preparation method thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20120201732A1 (en) * 2011-02-07 2012-08-09 Millennium Inorganic Chemicals, Inc. Ce containing, v-free mobile denox catalyst
CN103055889A (en) * 2012-12-31 2013-04-24 上海电气石川岛电站环保工程有限公司 A kind of low-temperature denitrification MnOx-CuO-TiO2 catalyst and its preparation method and application
CN104338534A (en) * 2013-08-09 2015-02-11 中国石油化工股份有限公司 Compound copper oxide catalyst, preparation method and application thereof
CN104607198A (en) * 2015-01-29 2015-05-13 李灏呈 Vanadium-free plate-like denitration catalyst and preparation method thereof

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
DONOVAN A. PEÑA ET AL.: ""TiO2-supported metal oxide catalysts for low-temperature selective catalytic reduction of NO with NH3 I. Evaluation and characterization of first row transition metals"", 《JOURNAL OF CATALYSIS》 *
张蕾等编: "《烟气脱硫脱硝技术及催化剂的研究进展》", 31 July 2016, 中国矿业大学出版社 *
黄民生: "《节能环保产业》", 30 June 2014, 上海科学技术出本社 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111701591A (en) * 2020-06-16 2020-09-25 北京石油化工学院 Hydrogenation catalyst and preparation method thereof and method for preparing fatty alcohol by hydrogenation of fatty acid ester
CN112452326A (en) * 2020-11-25 2021-03-09 常州大学 Preparation method of copper black titanium catalyst and application of copper black titanium catalyst in selective catalytic oxidation denitration
CN112452326B (en) * 2020-11-25 2024-01-23 常州大学 Preparation method of copper black titanium catalyst and application of copper black titanium catalyst in selective catalytic oxidation denitration

Similar Documents

Publication Publication Date Title
US11161106B2 (en) Preparation method of denitration catalyst with wide operating temperature range for flue gas
CN101480611B (en) A vanadium-doped titanium-based flue gas denitrification catalytic material and preparation method thereof
CN101773824B (en) Catalyst for removing NOx in incineration gas and preparation method thereof
CN107899567B (en) Mesoporous Zr and Ce co-doped SCR catalyst
WO2015161627A1 (en) Honeycomb denitration catalyst for flue gas at 400°c-600°c and preparation method therefor
CN111992203A (en) NH (hydrogen sulfide)3-SCR low-temperature denitration catalyst and preparation method and application thereof
CN106732536B (en) A kind of CeO2@MnOx low-temperature SCR catalyst for denitrating flue gas and the preparation method and application thereof
CN104324729A (en) Flue gas low temperature denitration cobalt manganese oxide catalyst and preparation method thereof
CN103433033A (en) A low-temperature denitrification MnOx-CeO2-TiO2-Al2O3 catalyst and its preparation method and application
CN104001497B (en) A kind of wide temperature window denitrating catalyst and its preparation method and application
CN102259009A (en) Sulfate radical promoted TiO2 carrier based SCR (Selective Catalytic Reduction) flue gas denitration catalyst and preparation method thereof
CN104148052A (en) Cerium-vanadium-silicon-titanium composite oxide catalyst and preparation method thereof
CN103084182A (en) Vanadium-free denitration catalyst for flue gas denitration and preparation method thereof
CN111036229A (en) Low-temperature V2O5-WO3/TiO2NH3Selective reduction catalytic NO catalyst and preparation method thereof
CN101869833B (en) Catalyst for SCR denitration of furnace middle temperature fume and preparation method thereof
CN109158108A (en) A kind of catalyst and its preparation method and application for low-temperature denitration of flue gas
CN108554398A (en) A kind of preparation method and applications of wide temperature window denitrating catalyst
CN103055889A (en) A kind of low-temperature denitrification MnOx-CuO-TiO2 catalyst and its preparation method and application
CN104549380A (en) Method for phosphoric acidification modification of TiO2 carrier for preparing V2O5-WO3/TiO2 based SCR (selective catalytic reduction) denitration catalyst
CN109012680A (en) A kind of catalyst and its preparation method and application for denitrating flue gas
CN108855053A (en) A kind of preparation method and applications of rich oxygen type Mn based low-temperature denitration catalyst
CN108579756A (en) One main laminaria shape Mn-Fe bimetallic oxide load Cs eO2Catalyst and preparation method and application
CN108554419A (en) Low temperature removes the NH3-SCR catalyst and preparation method thereof of Diesel NOx
CN110523408B (en) Low-temperature denitration catalyst and preparation method thereof
CN109745995A (en) Wide temperature window SCR catalyst for denitrating flue gas and its 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: 20190108

RJ01 Rejection of invention patent application after publication