CN104826410B - Smoke filtration element and preparation method - Google Patents

Smoke filtration element and preparation method Download PDF

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Publication number
CN104826410B
CN104826410B CN201510178565.3A CN201510178565A CN104826410B CN 104826410 B CN104826410 B CN 104826410B CN 201510178565 A CN201510178565 A CN 201510178565A CN 104826410 B CN104826410 B CN 104826410B
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filter core
preparation
filtration element
smoke filtration
flue gas
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CN104826410A (en
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高麟
汪涛
莫代林
覃金
刘勇
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Intermet Technology Chengdu Co Ltd
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Intermet Technology Chengdu Co Ltd
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Abstract

The present invention relates to smoke filtration element and preparation method, include, for filtering granule foreign and the filter core for porous metals filter course in flue gas, the clean air cavity in filter core being filled with and described harmful substances in flue gas can being reacted the catalytic specie for harmless components at filter element.Smoke filtration element of the present invention and preparation method, the equipment of the filtration of ash-laden gas and catalysis reduction can be integrated, simplify existing equipment and process largely, the efficiency that improve fume treatment of highly significant, and it is that whole operation reduces substantial amounts of production cost by the device structure of integration, creates obviously economic benefit for manufacturing enterprise.

Description

Smoke filtration element and preparation method
Technical field
The present invention relates to smoke filtration element and preparation method, be particularly suitable for but not only limit the use of in in high-temperature gas denitration.
Background technology
The useless smoke processing system of current most coal-burning power plant and coal chemical industry enterprises all has gas solid separation system, SCR catalysis Reaction system and other subsystem, such as, have pulverized-coal fired boiler, smokejack, flue gas gaseous mixture, Benitration reactor etc..And Often containing the furnace gas of a large amount of dust and nitrogen oxides, such as coal-fired plant boiler in industrial furnace gas, its contained nitrogen oxides is to promote Become the main cause that acid rain is formed, and possibly together with the dust of tens of grams in the furnace gas of general every liter of coal-fired plant boiler.For such as The usual method that the purification of the contour dust of furnace gas of coal-fired plant boiler and the industrial furnace gas of amount of nitrogen oxides is taked is: first will Furnace gas introduces SCR reactor and (also needs to inject reducing agent during furnace gas introduces SCR reactor in furnace gas, should go back Former dose is usually ammoniacal liquor) thus nitrogen oxides is reduced to harmless nitrogen gas, it is achieved furnace gas denitration purifies, then by the stove after denitration Gas introducing electric cleaner is to remove the dust in furnace gas, then the gas after dedusting introduces discharge after desulfurizing tower desulfurizing and purifying.Described Term " SCR " refer to Selective Catalytic Reduction, i.e. SCR.
Catalyst in above-mentioned SCR reactor is the key factor affecting SCR system entirety denitration effect.The SCR being originally developed Catalyst is graininess, the cellular or tabular catalyst of main employing.On honeycombed catalyst and tabular catalyst All being placed with and numerous be available for the checkerwork cell that flue gas passes through, the big I of these checkerwork cells is selected according to concentration and the size of dust in flue gas Selecting, during use, flue gas flows to the opposite side of catalyst, flue gas therebetween from the side of catalyst by the passage being made up of these checkerwork cells Contact with the catalytic active substance on checkerwork cell inwall, thus the nitrogen oxides in flue gas is reduced to harmless nitrogen gas.Above-mentioned honeycomb Shape catalyst and tabular catalyst are typically made up of carrier and catalytic active layer, and wherein carrier is first made into cellular or tabular (general employing is extruded), adheres to the catalytic active layer being made up of catalytic active substance the most again on carrier.
But owing to SCR catalyst is direct and high dustiness smoke contacts, hold very much if directly ash-laden gas is catalyzed It is easily caused catalytic active substance poisoning, shortens service life.If first ash-laden gas being catalyzed by after filter element filtering again Reduction reaction, different with the equipment of catalysis owing to filtering, the most solely dispersion of each equipment, it is highly detrimental to procedure operation and dimension Protect.
Summary of the invention
The invention provides a kind of smoke filtration element and preparation method, enable the filtration to ash-laden gas and catalysis reduction one Individual system completes, simplifies existing equipment and process, reduce energy loss and cost-effective, improve production efficiency.
The smoke filtration element of the present invention, including for filtering granule foreign in flue gas and the filter core for porous metals filter course, Clean air cavity in filter core is filled with and described harmful substances in flue gas can be reacted the catalytic specie for harmless components.Wherein described The filtering layer inner surface of porous metals can also be covered with catalytic specie.Porous metals are existing a kind of metal materials, are inside one There is many average pore sizes metal at the tiny micropore of 1~200 μm.Porous metals can be single metal, it is also possible to for metal Between compound, intermetallic compound also makes solid relate to metal mutually, is the compound being made up of two or more metal.Gold The advantage that the filter core that between genus, compound is constituted has highly significant in high temperature air filtration.Catalytic specie is packed into the clean gas of filter core In chamber, after flue gas falls granule foreign therein by filter element filtering, carry out catalysis reduction at once with the catalytic specie in clean air cavity Reaction, is then discharged out.If when the filtering layer inner surface of filter element is also covered with catalytic specie, the catalytic specie on filtering layer just with Flue gas after filtering layer filters reacts first, is had remnants in flue gas by the catalytic specie being seated in clean air cavity the most again Pest matter is reacted further.This structure seems simple, but can be integrated by the distinct device of the most different operations, Being obtained for huge raising in industrial management efficiency and fume treatment efficiency, this is not have in the fume treatment of traditional approach Standby, simultaneously because the raising of various efficiency and be that manufacturing enterprise creates significant economic benefit.The filter element of the present invention is also Can be suitable for and at high temperature filter flue gas, such as, when flue gas being carried out SCR denitration, catalytic specie can be with TiO2 For base material, with V2O5For main active ingredient, with WO3、MoO3Constitute for anti-oxidant and antitoxinization auxiliary ingredients.Other cigarette During gas disposal, select existing corresponding catalytic specie.
Further, it is provided with erection joint in the end of filter core, so can facilitate other in the filters such as filter core and card Equipment connects.
One of which attachment structure is, described erection joint is threadeded with filter core.This mode simple in construction, easy accessibility, It is likely that there will be the poorly sealed close problem in threaded connection place.
Another kind of attachment structure is, described erection joint is connected by flange and filter core are fixing.The connected mode of flange arrangement is same Sample ensure that the sealing of junction, and dismounts the most simple and convenient.In addition, erection joint can also pass through bonding grade side Formula is connected with filter core.
Optionally, described catalytic specie fills in the catalysis cage of clean air cavity combination assembling, and the sidewall of described catalysis cage is provided with Through hole.So at filling and taking-up catalytic specie, particularly can be very convenient during taking-up catalytic specie, directly will be equipped with urging The catalysis cage of compound matter takes out, and can also avoid catalytic specie that filter core inwall is caused secondary pollution simultaneously.
Present invention also offers a kind of preparation method for above-mentioned filter element, include addition granulation agent in metal dust, Metal dust is prepared as metallic particles;Then described metallic particles is compressed under pressure environment filter core pressed compact, then by described Filter core pressed compact is sintered to the filter core of porous metal structure;Finally the Catalyst packing reacted with harmful substances in flue gas will be needed to enter institute State in the clean air cavity of filter core.
Further, at least including iron powder and aluminium powder in described metal dust, wherein the weight ratio of iron powder is 40~80%, aluminium The weight ratio of powder is 15~30%, according to the use environment of filter element, it is also possible to add weight ratio other metal less than 20% Powder, such as chromium (Cr), nickel (Ni), silicon (Si) and other rare earth element (such as cerium, lanthanum, yttrium etc.).Other metal powder End effect primarily to improve some characteristics of filter element filtering layer material, including decay resistance, toughness, mechanical property, Distribution of pores and size etc. thereof, as added Cr, can be obviously improved the power such as the tensile strength of material, three-point bending resistance, crushing strength Learn performance, additionally it is possible to be obviously improved material decay resistance under the adverse circumstances such as strong acid and strong base.Change between the metal so made The filter core of laminate structures more can be suitable for the filtration to high-temperature gas.Whether adding other metal dust can be according to actual condition bar Part specifically determines, if actual service conditions is gentleer, then can be without, if use environment relatively more severe (as sulfur-bearing, Fluorine-containing or other acid-base environment), then must add respective metal powder, to ensure that filter element is applicable to this environment.
Preferably, described metallic particles is compressed to filter core pressed compact in the isostatic cool pressing environment that pressure is 100~300MPa.Cold Isostatic pressed is a kind of conventional compact technique, be loaded into sealing, material in elastic mould, be placed in and contain liquid or gas In container, with liquid or gas, it is applied with certain pressure, material is pressed into entity, obtains the base substrate of original-shape. After pressure release, mould is taken out in container, after the demoulding, as required base substrate is being made further Shape correction.
Preferably, described filter core pressed compact passes through vacuum-sintering for having porous metal structure at a temperature of 950 DEG C~1300 DEG C Filter core, wherein sintering temperature can also is that 1000 DEG C~1200 DEG C.
Further, the particle diameter of described metal dust is 100~400 mesh, and the filter element filtering effect so produced is more preferable.Have one The particle diameter of the most special metal dust can also be micron order.
After tested, smoke filtration element of the present invention and preparation method, it is possible to by whole to the filtration of ash-laden gas and the equipment of catalysis reduction It is integrated, simplifies existing equipment and process largely, the efficiency that improve fume treatment of highly significant.To cigarette In gas denitrating technique, denitration temperature uses 300 DEG C~400 DEG C, obtained denitration rate >=80%, SO2Conversion ratio≤2%, reaches Arrive the most outstanding denitration effect, and the device structure by integration be that whole operation reduces substantial amounts of production cost, Obviously economic benefit is created for manufacturing enterprise.
Below in conjunction with the detailed description of the invention of embodiment, the foregoing of the present invention is described in further detail again.But should not This is interpreted as, and the scope of the above-mentioned theme of the present invention is only limitted to Examples below.Without departing from the idea case in the present invention described above, The various replacements made according to ordinary skill knowledge and customary means or change, all should be included within the scope of the invention.
Accompanying drawing explanation
Fig. 1 is a kind of structural representation of embodiment 1.
Fig. 2 is the another kind of structural representation of embodiment 1.
Fig. 3 is a kind of structural representation of embodiment 2.
Detailed description of the invention
Embodiment 1:
The smoke filtration element of the present invention as shown in Figure 1, including for filtering in flue gas granule foreign and having porous metals and filter The filter core 1 of layer, is filled with the catalytic specie 3 of SCR (SCR) in the clean air cavity 2 in filter core 1.In order to reach Higher efficiency and the catalytic reaction of effect, the filtering layer inner surface at described porous metals can also be covered with catalytic specie 3.Catalytic materials Matter 3 can be with TiO2For base material, with V2O5For main active ingredient, with WO3、MoO3For anti-oxidant and antitoxinization auxiliary Composition is constituted.Being provided with erection joint 4 in the end of filter core 1, for being connected with the card (orifice plate) in filter, installation connects 4 are fastenedly connected with filter core 1 helicitic texture 41.
When making above-mentioned filter element, first particle diameter be 100 mesh proportions be 20% aluminium powder, particle diameter be 200 mesh proportions be 75% Iron powder, and in the metal dust of other powder that proportion is 5% add granulation agent, metal dust is prepared as metallic particles; Then described metallic particles is compressed under the isostatic cool pressing environment of 100~300MPa filter core pressed compact, then by described filter core pressed compact The filter core 1 of porous metal structure it is sintered at a temperature of 950 DEG C~1300 DEG C.The filter core 1 so sintered out after testing, its flux For 368m3/m2.h.kpa, the average pore size of filter opening is 65um, and normal temperature tension reaches 90MPa, and the tension at 600 DEG C is 75MPa, Porosity is 42%.Finally described SCR catalytic specie is packed in the clean air cavity 2 of described filter core 1.With to denitrating flue gas As a example by technique, denitration temperature is 350 DEG C, obtained denitration rate >=80%, SO2Conversion ratio≤2%, has reached the most outstanding Denitration effect.
Embodiment 2:
As in figure 2 it is shown, on the basis of embodiment 1, described erection joint 4 is by flange arrangement 42 with filter core 1 combination even Connect, to ensure the sealing between erection joint 4 and filter core 1.
Embodiment 3:
As it is shown on figure 3, on the basis of embodiment 1 or 2, described catalytic specie 3 fills in and the combination assembling of clean air cavity 2 In catalysis cage 5, the sidewall of described catalysis cage 5 is provided with through hole 51, is used for allowing flue gas contact with catalytic specie 3 and to react.This Sample is in filling and takes out catalytic specie 3, particularly can be very convenient during taking-up catalytic specie 3, directly will be equipped with catalytic materials The catalysis cage 5 of matter 3 takes out, and can also avoid catalytic specie 3 that filter core inwall is caused secondary pollution simultaneously.

Claims (9)

1. smoke filtration element, including for filtering granule foreign in flue gas and there is the filter core (1) of porous metals filter course, its It is characterized as: being filled with in the clean air cavity (2) in filter core (1) can be harmless components by the reaction of described harmful substances in flue gas Catalytic specie (3);Described filter element includes and the catalysis cage (5) of clean air cavity (2) combination assembling, this catalysis cage (5) Sidewall is provided with through hole (51), and described catalytic specie (3) fills in catalysis cage (5), is wherein catalyzed cage (5) and filter core (1) releasable connection is used.
2. smoke filtration element as claimed in claim 1, is characterized by: be provided with erection joint (4) in the end of filter core (1).
3. smoke filtration element as claimed in claim 2, is characterized by: described erection joint (4) and filter core (1) spiral shell Line connects.
4. smoke filtration element as claimed in claim 2, is characterized by: flange arrangement is passed through in described erection joint (4) Fix with filter core (1) and be connected.
5., for the preparation method of the smoke filtration element described in one of Claims 1-4, its feature includes: at metal dust Middle addition granulation agent, is prepared as metallic particles by metal dust;Then described metallic particles is compressed to filter core under pressure environment Pressed compact, is sintered to the filter core of porous metal structure by described filter core pressed compact;The catalytic specie that will be able to react with harmful substances in flue gas Fill in the catalysis cage assembled with the combination of clean air cavity.
6. preparation method as claimed in claim 5, is characterized by: at least include iron powder and aluminium powder in described metal dust, Wherein the weight ratio of iron powder is 40~80%, and the weight ratio of aluminium powder is 15~30%.
7. preparation method as claimed in claim 5, is characterized by: described metallic particles is 100~300MPa at pressure Isostatic cool pressing environment in be compressed to filter core pressed compact.
8. preparation method as claimed in claim 5, is characterized by: described filter core pressed compact is 950 DEG C~the temperature of 1300 DEG C Under be the filter core with porous metal structure by vacuum-sintering.
9. the preparation method as described in one of claim 5 to 8, is characterized by: the particle diameter of described metal dust is 100~400 Mesh.
CN201510178565.3A 2015-04-15 2015-04-15 Smoke filtration element and preparation method Active CN104826410B (en)

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CN107261692A (en) * 2017-08-11 2017-10-20 上海闰铭精密技术有限公司 Ultrapure nanoelectronic level gas-filtering device
CN109454231B (en) * 2018-12-18 2021-02-05 湖北汽车工业学院 Preparation method of iron-aluminum-copper alloy microporous filter material
CN109645572B (en) * 2019-01-14 2024-05-14 广东精彩国际生物科技有限公司 Filtering component and electronic smoking set using same
CN113584402B (en) * 2021-08-03 2022-11-08 西部宝德科技股份有限公司 Preparation method of iron-aluminum-chromium filtering material

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CN2303476Y (en) * 1997-07-17 1999-01-13 青岛高科技工业园统力商贸有限公司 Toxicant-filtering tip of cigarette
US7189375B2 (en) * 2002-09-16 2007-03-13 Delphi Technologies, Inc. Exhaust treatment device
CN2689720Y (en) * 2003-09-03 2005-04-06 牡丹江卷烟材料厂有限责任公司 Acetate fibre plus nano noble metal catalyst binary composite filter stick
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Denomination of invention: Smoke filter elements and production methods

Effective date of registration: 20231218

Granted publication date: 20160824

Pledgee: Chengdu Rural Commercial Bank Co.,Ltd. Wenjiang Liulin Branch

Pledgor: INTERMET TECHNOLOGIES CHENGDU Co.,Ltd.

Registration number: Y2023980072440