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CN105749943A - Low-temperature flue gas denitration catalyst powder and preparation method of low-temperature flue gas denitration catalyst powder - Google Patents

Low-temperature flue gas denitration catalyst powder and preparation method of low-temperature flue gas denitration catalyst powder Download PDF

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Publication number
CN105749943A
CN105749943A CN201610103780.1A CN201610103780A CN105749943A CN 105749943 A CN105749943 A CN 105749943A CN 201610103780 A CN201610103780 A CN 201610103780A CN 105749943 A CN105749943 A CN 105749943A
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Prior art keywords
oxide
flue gas
low
denitration catalyst
catalyst powder
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CN201610103780.1A
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延晓峰
杜德亮
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DONGGUAN XINTUO AUTOMOBILE MUFFLER CO LTD
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DONGGUAN XINTUO AUTOMOBILE MUFFLER CO LTD
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Priority to CN201610103780.1A priority Critical patent/CN105749943A/en
Publication of CN105749943A publication Critical patent/CN105749943A/en
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/14Phosphorus; Compounds thereof
    • B01J27/186Phosphorus; Compounds thereof with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J27/195Phosphorus; Compounds thereof with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium with vanadium, niobium or tantalum
    • B01J27/198Vanadium
    • B01J27/199Vanadium with chromium, molybdenum, tungsten or polonium

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

The invention discloses low-temperature flue gas denitration catalyst powder and a preparation method of the low-temperature flue gas denitration catalyst powder. The low-temperature flue gas denitration catalyst powder takes vanadium oxide, molybdenum oxide and tungstic oxide as main active components, takes phosphorus oxide, boron oxide and copper oxide as auxiliary active components and takes titanium dioxide as a carrier. The preparation method comprises the following steps: dissolving ammonium metavanadate, ammonium heptamolybdate and ammonium paratungstate into de-ionized water, and adding copper nitrate, boric acid and triammonium phosphate; heating and adjusting the pH value of the solution to be 2.0 to 3.0; slowly adding nano anatase titanium dioxide into an active component solution and dispersing the mixed active component solution by utilizing ultrasonic waves; drying and calcining to obtain the catalyst. According to the low-temperature flue gas denitration catalyst powder, the activity and the catalytic capability of the low-temperature denitration catalyst are remarkably improved; the low-temperature flue gas denitration catalyst powder has higher mechanical strength and anti-corrosion property, has stronger industrial application value and can be widely applied to NH3 selective catalytic reduction of nitrogen oxide in flue gas.

Description

A kind of low-temperature denitration of flue gas catalyst powder and preparation method thereof
One technical field
The present invention relates to catalyst technical field, particularly a kind of in the case of flue gas low-temperature (120 DEG C-300 DEG C), NH3Select Property catalysis reduction (SCR) removing NOXCatalyst and preparation method thereof.
Two technical backgrounds
Nitrogen oxides (NOX) produce essentially from combustion of fossil fuel, it is possible not only to produce acid rain, it is also possible to hydrocarbon Reaction forms photochemical fog, is one of the main source of current pm2.5 pollutant, develops efficient NO the most targetedlyX Emission control technique is significant to improving air quality.
NOXProcessing and mainly take in combustion process and the method for burning post processing, current industrial main application is low Nitrogen burning (LNB), SNCR (SNCR) and SCR (SCR) technology.LNB technology is to change fuel Combustion system, usual efficiency only has 30-40%.The reaction temperature of SNCR technology is 850 DEG C-1100 DEG C, and this kind of technical efficiency is High by about 50%, NH can be caused simultaneously3A large amount of escapes.And SCR technology NH3For reducing agent, efficiency generally up to more than 80%, it Feature be catalyst V2O5-TiO2 in 300 DEG C of-420 DEG C of temperature ranges, there is good catalysis activity.But for power plant Commercial Application condition outside boiler, owing to flue-gas temperature is low, generally below 300 DEG C, common denitrating catalyst cannot be just Often application.
Therefore, existing low-temperature denitration catalyst technology cannot be applied by heavy industrialization, and major defect is application temperature Degree narrow range, removal efficiency application life the highest, actual are short.
Three summary of the invention
It is an object of the invention to, for the deficiencies in the prior art, take with NH3For the SCR technology of reducing agent, with Based on vanadium/titanium catalyst research, it is provided that a kind of low-temperature denitration of flue gas catalyst with stronger industrial application value and system Preparation Method.
It is an object of the invention to be achieved through the following technical solutions:
A kind of low-temperature denitration of flue gas catalyst powder, with vanadium oxide, molybdenum oxide, tungsten oxide as main active component, with phosphorous oxide, Boron oxide, cupric oxide are Supplementary active compounds, with titanium dioxide as carrier;The mass parts of the most each component is: vanadium oxide 0.1- 3.0, molybdenum oxide 0.1-3.1, tungsten oxide 1.0-5.0, phosphorous oxide 0.01-0.1, boron oxide 0.01-0.05, cupric oxide 0.1-1.0, Titanium dioxide 75-90.
The preparation method of aforesaid low-temperature denitration of flue gas catalyst includes:
(1) configuration active component solution: by the presoma ammonium metavanadate of vanadium oxide, the presoma ammonium paramolybdate of molybdenum oxide, oxidation The presoma para-tungstic acid ammonia ammonium metavanadate 0.13-3.87 mass parts in proportion of tungsten, ammonium paramolybdate 0.12-3.81 mass parts, secondary tungsten Acid ammonium 1.13-5.65 mass parts is dissolved in deionized water, adds the copper nitrate of 0.3-0.8 mass parts, 0.02-0.1 mass parts Boric acid and the triammonium phosphate of 0.03-0.3 mass parts, solution is heated to 50 DEG C-60 DEG C, then with oxalic acid adjust solution ph extremely 2.0-3.0;
(2) use infusion process supported catalyst: Wastewater by Nanometer Anatase titanium dioxide is slowly added to active component solution, 50 DEG C- In 60 DEG C of solution, stirring dipping 2-3 hour, utilizes ultrasonic wave to disperse mixed active component solution, promotes homogenizing; Then 120 DEG C-220 DEG C dry 8-11 hour, then 400 DEG C-500 DEG C calcine 3-5 hour, obtain catalyst.
Described utilize ultrasonic wave to mixed active component solution be use ultrasonic wave rod to mixed active component Solution disperses.
The present invention utilizes infusion process load various active material and coagent, substantially increases active component in catalyst At the load area of carrier surface, it is effectively increased the contact area of active material and nitrogen oxides.Add various active simultaneously Material and co-catalyst, be effectively increased low temperature (more than the 120 DEG C) activity of catalyst.
Compared with prior art, its remarkable advantage is the present invention: (1) catalyst provided by the present invention keep vanadium/ On the basis of titanium catalyst commercial Application advantage, significantly improve low-temperature SCR activity (120 DEG C-300 DEG C) of catalyst, be adapted to Wider application.(2) by adding a certain proportion of various active material and co-catalysis material, it is effectively increased catalyst Activity.(3) being proved by experimental study, by adding various active material, catalyst has the spy of anti-sulfur dioxide, arsenic poisoning Property, and make denitration efficiency significantly promote, if NO concentration is at 800ppm, NH3/ NO=1.1, O25 v%, air speed 3000h-1Condition Under, when 120 DEG C, denitration efficiency improves 5 times, reaches 40%, and when 210 DEG C, efficiency improves 2.5 times, has reached 96.7%.Have Standby stronger industrial application value, the denitrating flue gas that can be widely applied to various industry is administered.
Four detailed description of the invention
A kind of low-temperature denitration of flue gas catalyst, with vanadium oxide, molybdenum oxide, tungsten oxide as main active component, with phosphorous oxide, oxidation Boron, cupric oxide are Supplementary active compounds, with titanium dioxide as carrier;The mass parts of the most each component is: vanadium oxide 0.1-3.0, Molybdenum oxide 0.1-3.1, tungsten oxide 1.0-5.0, phosphorous oxide 0.01-0.1, boron oxide 0.01-0.05, cupric oxide 0.1-1.0, dioxy Change titanium 75-90.
The preparation method of described low-temperature denitration of flue gas catalyst includes:
(1) configuration active component solution: by the presoma ammonium metavanadate of vanadium oxide, the presoma ammonium paramolybdate of molybdenum oxide, oxidation The presoma para-tungstic acid ammonia of tungsten is (ammonium metavanadate 0.13-3.87 mass parts, ammonium paramolybdate 0.12-3.81 mass parts, secondary in proportion Ammonium tungstate 1.13-5.65 mass parts, vanadium oxide is 0.775 with the ratio of ammonium metavanadate, and molybdenum oxide with the ratio of ammonium paramolybdate is 0.885, tungsten oxide is 0.81 with the proportionate relationship of ammonium paratungstate) it is dissolved in deionized water, add the nitre of 0.3-0.8 mass parts Acid copper, the boric acid of 0.02-0.1 mass parts and the triammonium phosphate of 0.03-0.3 mass parts, solution is heated to 50 DEG C-60 DEG C, then uses Oxalic acid adjusts solution ph to 2.0-3.0.
(2) infusion process supported catalyst is used: Wastewater by Nanometer Anatase titanium dioxide is slowly added to active component solution, 50 In DEG C-60 DEG C of solution, stirring dipping 2-3 hour, utilizes ultrasonic wave to disperse mixed active component solution, promotes all Change;Then 120 DEG C-220 DEG C dry 8-11 hour, then 400 DEG C-500 DEG C calcine 3-5 hour, obtain catalyst solid, through powder Catalyst powder is obtained after broken.
Ultrasonic wave is utilized mixed active component solution to preferably employ ultrasonic wave rod to mixing described in said method After active component solution disperse.
Embodiment 1.
(1) raw-material preparation (each constituent mass mark): ammonium metavanadate 3%, ammonium paramolybdate 3%, ammonium paratungstate 4%, nitre Acid copper 0.5 %, boric acid 0.1 %, triammonium phosphate 0.3%, Wastewater by Nanometer Anatase titanium dioxide 89.1%.
(2) configuration active component solution: first prepare and the quality deionized water such as titanium dioxide, is initially charged ammonium metavanadate, secondary Ammonium molybdate, ammonium paratungstate, add copper nitrate, boric acid, triammonium phosphate, and solution is heated to 60 DEG C and adds oxalic acid, adjusts pH value and arrives 2.0。
(3) infusion process supported catalyst is used: Wastewater by Nanometer Anatase titanium dioxide is slowly added to active component solution, 50 In DEG C-60 DEG C of solution, stirring dipping 2.5 hours, utilize ultrasonic wave to disperse mixed active component solution, promote all Change;Then 150 DEG C be dried 10 hours, more in atmosphere 430 DEG C calcine 3-5 hour, pulverize, be prepared as catalyst powder.
Embodiment 2.
(1) raw-material preparation (each constituent mass mark): ammonium metavanadate 3.5%, ammonium paramolybdate 2.5 %, ammonium paratungstate 3%, Copper nitrate 0.6%, boric acid 0.05%, triammonium phosphate 0.2%, Wastewater by Nanometer Anatase titanium dioxide 90.15%.
(2) configuration active component solution: first prepare and the quality deionized water such as titanium dioxide, is initially charged ammonium metavanadate, secondary Ammonium molybdate, ammonium paratungstate, add copper nitrate, boric acid, triammonium phosphate, and solution is heated to 60 DEG C and adds oxalic acid, adjusts pH value and arrives 2.0。
(3) infusion process supported catalyst is used: Wastewater by Nanometer Anatase titanium dioxide is slowly added to active component solution, 50 In DEG C-60 DEG C of solution, stirring dipping 2.5 hours, utilize ultrasonic wave to disperse mixed active component solution, promote all Change;Then 150 DEG C be dried 10 hours, more in atmosphere 430 DEG C calcine 3-5 hour, pulverize, be prepared as catalyst powder.
Ultrasonic wave is utilized mixed active component solution to preferably employ ultrasonic wave rod to mixing described in said method After active component solution disperse.

Claims (3)

1. a low-temperature denitration of flue gas catalyst powder, it is characterised in that with vanadium oxide, molybdenum oxide, tungsten oxide for chief active group Point, with phosphorous oxide, boron oxide, cupric oxide as Supplementary active compounds, with titanium dioxide as carrier;The mass parts of the most each component For: vanadium oxide 0.1-3.0, molybdenum oxide 0.1-3.1, tungsten oxide 1.0-5.0, phosphorous oxide 0.01-0.1, boron oxide 0.01-0.05, Cupric oxide 0.1-1.0, titanium dioxide 75-90.
2. according to the preparation method of the low-temperature denitration of flue gas catalyst described in claim 1, it is characterised in that including:
(1) configuration active component solution: by the presoma ammonium metavanadate of vanadium oxide, the presoma ammonium paramolybdate of molybdenum oxide, oxidation The presoma para-tungstic acid ammonia ammonium metavanadate 0.13-3.87 mass parts in proportion of tungsten, ammonium paramolybdate 0.12-3.81 mass parts, secondary tungsten Acid ammonium 1.13-5.65 mass parts is dissolved in deionized water, adds the copper nitrate of 0.3-0.8 mass parts, 0.02-0.1 mass parts Boric acid and the triammonium phosphate of 0.03-0.3 mass parts, solution is heated to 50 DEG C-60 DEG C, then with oxalic acid adjust solution ph extremely 2.0-3.0;
(2) use infusion process supported catalyst: Wastewater by Nanometer Anatase titanium dioxide is slowly added to active component solution, 50 DEG C- In 60 DEG C of solution, stirring dipping 2-3 hour, utilizes ultrasonic wave to disperse mixed active component solution, promotes homogenizing; Then 120 DEG C-220 DEG C dry 8-11 hour, then 400 DEG C-500 DEG C calcine 3-5 hour, obtain catalyst.
3. according to the preparation method of the low-temperature denitration of flue gas catalyst powder described in claim 2, it is characterised in that: described utilization Ultrasonic wave is to use ultrasonic wave rod to disperse mixed active component solution to mixed active component solution.
CN201610103780.1A 2016-02-26 2016-02-26 Low-temperature flue gas denitration catalyst powder and preparation method of low-temperature flue gas denitration catalyst powder Pending CN105749943A (en)

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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108212222A (en) * 2017-12-29 2018-06-29 浙江德创环保科技股份有限公司 A kind of porous honeycomb formula low-temperature denitration catalyst
CN109012712A (en) * 2018-09-30 2018-12-18 北京方信立华科技有限公司 A kind of low temperature vanadium titanium-based SCR catalyst and preparation method
CN109395756A (en) * 2018-09-30 2019-03-01 北京方信立华科技有限公司 A kind of honeycomb type low temperature high activity SCR catalyst preparation method
CN112403486A (en) * 2020-11-19 2021-02-26 高化学(江苏)化工新材料有限责任公司 V/Cu/B/W-TiO2-ZrO2Composite low-temperature denitration catalyst and preparation method thereof
CN114289011A (en) * 2021-12-29 2022-04-08 大唐南京环保科技有限责任公司 Denitration catalyst with wide activity temperature window and preparation method and application thereof
CN115739071A (en) * 2022-11-25 2023-03-07 大唐南京环保科技有限责任公司 Denitration catalyst and preparation method thereof

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CN101474565A (en) * 2009-01-06 2009-07-08 上海瀛正科技有限公司 Honeycomb type SCR denitration catalyst as well as preparation method thereof and equipment
CN101972647A (en) * 2010-11-26 2011-02-16 山东电力研究院 Titanium-base granular catalyst and preparation method and application thereof
CN103596678A (en) * 2011-02-07 2014-02-19 水晶美国股份公司 Ce containing, V-free mobile denox catalyst
JP2014144424A (en) * 2013-01-29 2014-08-14 Hitachi Zosen Corp Catalyst for decomposing ammonia

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101474565A (en) * 2009-01-06 2009-07-08 上海瀛正科技有限公司 Honeycomb type SCR denitration catalyst as well as preparation method thereof and equipment
CN101972647A (en) * 2010-11-26 2011-02-16 山东电力研究院 Titanium-base granular catalyst and preparation method and application thereof
CN103596678A (en) * 2011-02-07 2014-02-19 水晶美国股份公司 Ce containing, V-free mobile denox catalyst
JP2014144424A (en) * 2013-01-29 2014-08-14 Hitachi Zosen Corp Catalyst for decomposing ammonia

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108212222A (en) * 2017-12-29 2018-06-29 浙江德创环保科技股份有限公司 A kind of porous honeycomb formula low-temperature denitration catalyst
CN109012712A (en) * 2018-09-30 2018-12-18 北京方信立华科技有限公司 A kind of low temperature vanadium titanium-based SCR catalyst and preparation method
CN109395756A (en) * 2018-09-30 2019-03-01 北京方信立华科技有限公司 A kind of honeycomb type low temperature high activity SCR catalyst preparation method
CN112403486A (en) * 2020-11-19 2021-02-26 高化学(江苏)化工新材料有限责任公司 V/Cu/B/W-TiO2-ZrO2Composite low-temperature denitration catalyst and preparation method thereof
CN114289011A (en) * 2021-12-29 2022-04-08 大唐南京环保科技有限责任公司 Denitration catalyst with wide activity temperature window and preparation method and application thereof
CN114289011B (en) * 2021-12-29 2023-11-14 大唐南京环保科技有限责任公司 Denitration catalyst with wide active temperature window, and preparation method and application thereof
CN115739071A (en) * 2022-11-25 2023-03-07 大唐南京环保科技有限责任公司 Denitration catalyst and preparation method thereof

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