CN108421309A - A kind of filter felt and preparation method for flue-gas dust removal and purification - Google Patents

A kind of filter felt and preparation method for flue-gas dust removal and purification Download PDF

Info

Publication number
CN108421309A
CN108421309A CN201810210096.2A CN201810210096A CN108421309A CN 108421309 A CN108421309 A CN 108421309A CN 201810210096 A CN201810210096 A CN 201810210096A CN 108421309 A CN108421309 A CN 108421309A
Authority
CN
China
Prior art keywords
weight
parts
felt
flue
dust removal
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.)
Withdrawn
Application number
CN201810210096.2A
Other languages
Chinese (zh)
Inventor
陈庆
曾军堂
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.)
Chengdu New Keli Chemical Science Co Ltd
Original Assignee
Chengdu New Keli Chemical Science 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 Chengdu New Keli Chemical Science Co Ltd filed Critical Chengdu New Keli Chemical Science Co Ltd
Priority to CN201810210096.2A priority Critical patent/CN108421309A/en
Publication of CN108421309A publication Critical patent/CN108421309A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D39/00Filtering material for liquid or gaseous fluids
    • B01D39/14Other self-supporting filtering material ; Other filtering material
    • B01D39/20Other self-supporting filtering material ; Other filtering material of inorganic material, e.g. asbestos paper, metallic filtering material of non-woven wires
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D46/00Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
    • B01D46/0001Making filtering elements
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D46/00Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
    • B01D46/0027Filters or filtering processes specially modified for separating dispersed particles from gases or vapours with additional separating or treating functions
    • 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

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • General Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Biomedical Technology (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)

Abstract

The invention discloses a kind of filter felts and preparation method for flue-gas dust removal and purification.The filter felt is made by following steps:A, by carbon nanotube and ammonium metavanadate, titanium dioxide, oxalic acid liquid Hybrid Heating, catalytic activity liquid is made;B, by aerosil felt and catalytic activity liquid mixing pre-burning, pre-burning felt is made;C, hydrotalcite, silica, aluminium oxide, indium oxide, zeolite, natural clay, bonding agent, foaming agent and water are mixed and made into slurry;D, slurry is coated on pre-burning felt surface, up to the filter felt for flue-gas dust removal and purification after calcining.The method has the advantages that:Porcelain is fired by coating slurry on pre-burning felt surface, and microporous membrane is formed after porcelain under foaming agent effect, the micronic dust in flue gas can effectively be filtered, so that filtered flue gas is not interfered by micronic dust, the reduction purification of nitrogen oxides is efficient, effect is good, can effectively realize dedusting denitrification integral Effec-tive Function, and extend the working life of catalyst.

Description

A kind of filter felt and preparation method for flue-gas dust removal and purification
Technical field
The present invention relates to filed of flue gas purification, and in particular to the preparation of filter felt is removed more particularly, to one kind for flue gas The filter felt and preparation method of dirt purification.
Background technology
Currently, the close phase of the smoke emissioning pollutions such as the formation of haze and coal fired power plant, coal-burned industrial boiler, coal-fired furnace kiln It closes.Therefore, coal-fired flue-gas contamination control is the important channel for controlling air environmental pollution, and the pollution of the nitrogen oxides generated is The main cause that acid rain, haze are formed, and an important factor for endanger environmental and human health impacts, therefore to nitrogen oxidation in coal-fired flue-gas The purified treatment of object is extremely urgent.
Have a large amount of technology applications to the contamination control of nitrogen oxides at present, is broadly divided into two classes:Control in stove(Burning Control technology)With control technology outside stove(Burn post-control technology).Control includes mainly low nitrogen oxide burning technology in stove(It is low Excess air burner, Gases Recirculation, fuel reburning, fractional combustion)It is fired with being catalyzed in SNCR gas denitrifying technologies and stove Burn etc.;Burning post-control technology include:Wet denitration, SCR, electron beam denitration etc..Since denitration in the stove can at most provide 50% ~60% denitration efficiency, therefore increasingly stringent discharge standard cannot be met, therefore, denitration at present is controlled after mostly using burning System, mainstream technology mostly use selective catalytic reduction to reduce the pollution of nitrogen oxides.And it is catalyzed the material and knot of reduction Structure research becomes key.
Number of patent application 201510789500.2 discloses a kind of solid catalyst for coal-fired flue gas denitration, described to urge Agent is made of vanadic anhydride, ferroso-ferric oxide and titanium dioxide.It, should compared with the catalyst of existing selective reduction denitrogenation The catalyst Deitrogenatin of invention is efficient, and resourceful, and adaptability is good, and nitrogen extrusion rate can reach 95% or more.
Number of patent application 201510969485.X discloses a kind of coal-fired flue gas denitration demercuration catalyst and preparation method thereof And application, catalyst is mainly using attapulgite as carrier, by loading molybdenum trioxide and mesopore metal oxide TOX institutes shape At composite catalyst.Compared with the existing technology, invention proposition will be carried on attapulgite using modified SCR catalyst and will Be used for coal-fired flue gas denitration demercuration;Cheap convex stick soil is used to replace expensive activated carbon, titanium dioxide etc. as catalyst Carrier;The catalyst is efficient in low-temperature region denitration demercuration;SCR denitration equipment, drop can be utilized when the catalyst denitration demercuration Low equipment cost.
Number of patent application 201510789500.2 discloses a kind of coal-fired flue-gas dust-removing and desulfurization denitration combination process system, it It is high temperature fume dust removal desulphurization denitration and the complete set of equipments of UTILIZATION OF VESIDUAL HEAT IN, rough dedusting is mainly carried out by ceramic multicyclone dust collector and is taken off Sulphur, ceramic filter membrane filter carry out deep-purification dedusting and denitration, and cold wind is become hot wind by heat exchanger using fume afterheat, into It is combustion-supporting to enter boiler combustion mouth.The manufacture material of filter mantle is metal and nonmetal oxide, inherently catalyst Ontology and carrier, in conjunction with refractory ceramics method, sintering prepares catalyst at a certain temperature.It is a kind of high-temperature dust removal desulphurization denitration Integrated technique especially substitutes electric precipitator and purifies coal gas, and no explosion danger, securely and reliably, investment reduction improves thermal energy profit With, increase energy-saving effect, design is simple, reasonable for structure, be current energy-saving and emission-reduction, transition and upgrade cross-centennial China make brand Product.
Number of patent application 201610473625.9 discloses a kind of coal-fired flue gas denitration sulfur method, is filled by following desulfurization Processing is set, desulfurizer includes desulfuration pipeline, and desulfuration pipeline includes that the preliminary screen pipe being sequentially connected, adsorption filtration pipe and light are urged Change purification pipe, be equipped with successively from gas inlet to exhanst gas outlet on the inner wall of preliminary screen pipe liquor natrii hypochloritis's atomizer, Oxygen nozzle and ammonium persulfate solution atomizer, liquor natrii hypochloritis's atomizer are parallel to the inner wall of the preliminary screen pipe Installation, oxygen nozzle are installed diagonally downward, and the inner wall with preliminary screen pipe is in 35 ~ 55 ° of angle, ammonium persulfate solution atomization spray Head is installed perpendicular to the inner wall of the preliminary screen pipe, and the plate body of the honeycomb hole of perforation is equipped in adsorption filtration pipe.The invention exists Denitration process can be completed while desulfurization, and the extrusion rate of sulfur dioxide can reach 99% or more, the extrusion rate of oxynitrides It can reach 90% or more.
It can be seen that being applied to the reducing agent of purification of nitrogen oxides in the prior art, its catalysis efficiency is studied mostly, and is neglected Depending on micro dust, in practice, micro dust itself pollutant that still haze is not formed, and it carries a large amount of nitrogen oxidation Object, and be tightly combined, catalyst is catalyzed reduction effect to it and is not obvious, and this kind of micro dust once enters air, harmfulness Than simple nitrogen oxides and dust bigger, the problems such as prior art cannot achieve dedusting denitrification integral.
Invention content
Effectively to solve above-mentioned technical problem, the present invention proposes a kind of filter felt for flue-gas dust removal and purification and preparation Method can effectively filter the micronic dust in flue gas, and filtered flue gas is not interfered by micronic dust, fast in the internal layer of supported active agent Fast nitrogen oxides reduction realizes dedusting denitrification integral Effec-tive Function, and extends the working life of catalyst.
The specific technical solution of the present invention is as follows:
A kind of preparation method of filter felt for flue-gas dust removal and purification, the filter felt are by the slurry containing bonding agent and foaming agent Material is coated on the surface of the aerosil pre-burning felt of load ammonium metavanadate, is made through calcining, specific preparation process For:
A, carbon nanotube is mixed with ammonium metavanadate, titanium dioxide, oxalic acid liquid, is heated, catalytic activity liquid is made;
B, aerosil felt is immersed in the catalytic activity liquid of step a, simultaneously pre-burning is taken out after 20 ~ 30min, thickness is made For the pre-burning felt of 2 ~ 3mm;
C, by hydrotalcite, silica, aluminium oxide, indium oxide, zeolite, natural clay and water mixed grinding, and be added bonding agent, Slurry is made in foaming agent;
D, the slurry of step c is coated on to the pre-burning felt surface of step b, further calcined, slurry porcelainization is made to form micropore ceramics The filter felt for flue-gas dust removal and purification is made in film.
Preferably, in the step a, heating temperature is 40 ~ 50 DEG C, and soaking time is 10 ~ 20min.
Preferably, in the step a, 22 ~ 28 parts by weight of carbon nanotube, 4 ~ 6 parts by weight of ammonium metavanadate, titanium dioxide 10 ~ 15 Parts by weight, 51 ~ 64 parts by weight of oxalic acid liquid.
Preferably, in the step b, 20 ~ 30 parts by weight of aerosil felt, 70 ~ 80 parts by weight of catalytic activity liquid.
Preferably, in the step b, calcined temperature is 200 ~ 300 DEG C, and temperature is 1 ~ 2h.
Preferably, in the step c, bonding agent is at least one in epoxy resin adhesive or phenolic resin binder Kind.
Preferably, in the step c, foaming agent is at least one of saleratus, sodium bicarbonate or calcium bicarbonate.
Preferably, in the step c, 10 ~ 12 parts by weight of hydrotalcite, 3 ~ 16 parts by weight of silica 1,4 ~ 6 weight of aluminium oxide Measure part, 2 ~ 4 parts by weight of indium oxide, 2 ~ 4 parts by weight of zeolite, 20 ~ 25 parts by weight of natural clay, 29 ~ 47 parts by weight of water, bonding agent 1 ~ 2 parts by weight, 1 ~ 2 parts by weight of foaming agent.
Preferably, in the step d, calcination temperature is 800 ~ 1000 DEG C, and the time is 3 ~ 5h.
The above of the present invention also proposes a kind of filter felt for flue-gas dust removal and purification, by the way that ammonium metavanadate to be carried on Carbon nanotube, titanium dioxide, aerosil felt, make the surface area for the vanadic anhydride to be formed fully demonstrate, and stablize Fixed vanadic anhydride.Further, on pre-burning felt surface, coating slurry fires porcelain, hydrotalcite, silica, aluminium oxide, oxygen Change indium, zeolite, natural clay and form microporous membrane after porcelain under foaming agent effect, can effectively filter micro- in flue gas Dirt, filtered flue gas are not interfered by micronic dust, in the quick nitrogen oxides reduction of the internal layer of supported active agent, realize dedusting denitration Integrated high-efficiency is run, and further extends the working life of catalyst.
Beneficial effects of the present invention are:
1. proposing a kind of method forming the filter felt that microporous membrane is made for flue-gas dust removal and purification using porcelainization.
2. the present invention is micro- by being formed in pre-burning felt surface coating slurry firing porcelain, and under foaming agent effect after porcelain Hole ceramic membrane can effectively filter the micronic dust in flue gas so that filtered flue gas is not interfered by micronic dust, in supported active agent Internal layer more fast and effeciently nitrogen oxides reduction.
3. the surface area for the vanadic anhydride that the present invention is formed in preparing fully demonstrates and stablizes and fixes, in flue gas Nitrogen oxides reduction purification effect is good.
4. filter felt produced by the present invention can effectively realize dedusting denitrification integral Effec-tive Function, and extend catalysis The working life of agent.
Specific implementation mode
In the following, the present invention will be further described in detail by way of specific embodiments, but this should not be interpreted as to the present invention Range be only limitted to example below.Without departing from the idea of the above method of the present invention, according to ordinary skill The various replacements or change that knowledge and customary means are made, should be included in the scope of the present invention.
Embodiment 1
A, carbon nanotube is mixed with ammonium metavanadate, titanium dioxide, oxalic acid liquid, is heated, catalytic activity liquid is made;
B, aerosil felt is immersed in the catalytic activity liquid of step a, simultaneously pre-burning is taken out after 25min, pre-burning felt is made;
C, by hydrotalcite, silica, aluminium oxide, indium oxide, zeolite, natural clay and water mixed grinding, and be added bonding agent, Slurry is made in foaming agent;
D, the slurry of step c is coated on to the pre-burning felt surface of step b, further calcine, be made for flue-gas dust removal and purification Filter felt.
In step b, the average thickness of aerosil felt is 2mm;In step c, bonding agent is adhering with epoxy resin Agent;In step c, foaming agent is saleratus;
In step a, heating temperature is 45 DEG C, soaking time 15min;In step b, calcined temperature is 250 DEG C, and temperature is 1.5h;In step d, calcination temperature is 900 DEG C, time 4h;
In step a, 25 parts by weight of carbon nanotube, 5 parts by weight of ammonium metavanadate, 13 parts by weight of titanium dioxide, 57 parts by weight of oxalic acid liquid;Step In rapid b, 25 parts by weight of aerosil felt, 75 parts by weight of catalytic activity liquid;In step c, 11 parts by weight of hydrotalcite, dioxy 15 parts by weight of SiClx, 5 parts by weight of aluminium oxide, 3 parts by weight of indium oxide, 3 parts by weight of zeolite, 23 parts by weight of natural clay, 37 weight of water Measure part, 1 parts by weight of bonding agent, 2 parts by weight of foaming agent.
Embodiment 2
A, carbon nanotube is mixed with ammonium metavanadate, titanium dioxide, oxalic acid liquid, is heated, catalytic activity liquid is made;
B, aerosil felt is immersed in the catalytic activity liquid of step a, simultaneously pre-burning is taken out after 20min, pre-burning felt is made;
C, by hydrotalcite, silica, aluminium oxide, indium oxide, zeolite, natural clay and water mixed grinding, and be added bonding agent, Slurry is made in foaming agent;
D, the slurry of step c is coated on to the pre-burning felt surface of step b, further calcine, be made for flue-gas dust removal and purification Filter felt.
In step b, the average thickness of aerosil felt is 3mm;In step c, bonding agent is bonded for phenolic resin Agent;In step c, foaming agent is sodium bicarbonate;
In step a, heating temperature is 50 DEG C, soaking time 10min;In step b, calcined temperature is 300 DEG C, temperature 1h; In step d, calcination temperature is 1000 DEG C, time 3h;
In step a, 28 parts by weight of carbon nanotube, 6 parts by weight of ammonium metavanadate, 15 parts by weight of titanium dioxide, 51 parts by weight of oxalic acid liquid;Step In rapid b, 30 parts by weight of aerosil felt, 70 parts by weight of catalytic activity liquid;In step c, 12 parts by weight of hydrotalcite, dioxy 16 parts by weight of SiClx, 6 parts by weight of aluminium oxide, 4 parts by weight of indium oxide, 4 parts by weight of zeolite, 25 parts by weight of natural clay, 29 weight of water Measure part, 2 parts by weight of bonding agent, 2 parts by weight of foaming agent.
Embodiment 3
A, carbon nanotube is mixed with ammonium metavanadate, titanium dioxide, oxalic acid liquid, is heated, catalytic activity liquid is made;
B, aerosil felt is immersed in the catalytic activity liquid of step a, simultaneously pre-burning is taken out after 30min, pre-burning felt is made;
C, by hydrotalcite, silica, aluminium oxide, indium oxide, zeolite, natural clay and water mixed grinding, and be added bonding agent, Slurry is made in foaming agent;
D, the slurry of step c is coated on to the pre-burning felt surface of step b, further calcine, be made for flue-gas dust removal and purification Filter felt.
In step b, the average thickness of aerosil felt is 2mm;In step c, bonding agent is adhering with epoxy resin Agent;In step c, foaming agent is calcium bicarbonate;
In step a, heating temperature is 40 DEG C, soaking time 20min;In step b, calcined temperature is 200 DEG C, temperature 2h; In step d, calcination temperature is 800 DEG C, time 5h;
In step a, 22 parts by weight of carbon nanotube, 4 parts by weight of ammonium metavanadate, 10 parts by weight of titanium dioxide, 64 parts by weight of oxalic acid liquid;Step In rapid b, 20 parts by weight of aerosil felt, 80 parts by weight of catalytic activity liquid;In step c, 10 parts by weight of hydrotalcite, dioxy 13 parts by weight of SiClx, 4 parts by weight of aluminium oxide, 2 parts by weight of indium oxide, 2 parts by weight of zeolite, 20 parts by weight of natural clay, 47 weight of water Measure part, 1 parts by weight of bonding agent, 1 parts by weight of foaming agent.
Embodiment 4
A, carbon nanotube is mixed with ammonium metavanadate, titanium dioxide, oxalic acid liquid, is heated, catalytic activity liquid is made;
B, aerosil felt is immersed in the catalytic activity liquid of step a, simultaneously pre-burning is taken out after 22min, pre-burning felt is made;
C, by hydrotalcite, silica, aluminium oxide, indium oxide, zeolite, natural clay and water mixed grinding, and be added bonding agent, Slurry is made in foaming agent;
D, the slurry of step c is coated on to the pre-burning felt surface of step b, further calcine, be made for flue-gas dust removal and purification Filter felt.
In step b, the average thickness of aerosil felt is 3mm;In step c, bonding agent is bonded for phenolic resin Agent;In step c, foaming agent is saleratus;
In step a, heating temperature is 42 DEG C, soaking time 18min;In step b, calcined temperature is 220 DEG C, temperature 2h; In step d, calcination temperature is 850 DEG C, time 4.5h;
In step a, 26 parts by weight of carbon nanotube, 6 parts by weight of ammonium metavanadate, 14 parts by weight of titanium dioxide, 54 parts by weight of oxalic acid liquid;Step In rapid b, 22 parts by weight of aerosil felt, 78 parts by weight of catalytic activity liquid;In step c, 10 parts by weight of hydrotalcite, dioxy 14 parts by weight of SiClx, 4 parts by weight of aluminium oxide, 2 parts by weight of indium oxide, 2 parts by weight of zeolite, 22 parts by weight of natural clay, 44 weight of water Measure part, 1 parts by weight of bonding agent, 1 parts by weight of foaming agent.
Embodiment 5
A, carbon nanotube is mixed with ammonium metavanadate, titanium dioxide, oxalic acid liquid, is heated, catalytic activity liquid is made;
B, aerosil felt is immersed in the catalytic activity liquid of step a, simultaneously pre-burning is taken out after 28min, pre-burning felt is made;
C, by hydrotalcite, silica, aluminium oxide, indium oxide, zeolite, natural clay and water mixed grinding, and be added bonding agent, Slurry is made in foaming agent;
D, the slurry of step c is coated on to the pre-burning felt surface of step b, further calcine, be made for flue-gas dust removal and purification Filter felt.
In step b, the average thickness of aerosil felt is 3mm;In step c, bonding agent is adhering with epoxy resin Agent;In step c, foaming agent is sodium bicarbonate;
In step a, heating temperature is 48 DEG C, soaking time 12min;In step b, calcined temperature is 290 DEG C, temperature 1h; In step d, calcination temperature is 950 DEG C, time 4.5h;
In step a, 27 parts by weight of carbon nanotube, 5 parts by weight of ammonium metavanadate, 14 parts by weight of titanium dioxide, 54 parts by weight of oxalic acid liquid;Step In rapid b, 27 parts by weight of aerosil felt, 73 parts by weight of catalytic activity liquid;In step c, 12 parts by weight of hydrotalcite, dioxy 15 parts by weight of SiClx, 6 parts by weight of aluminium oxide, 3 parts by weight of indium oxide, 3 parts by weight of zeolite, 24 parts by weight of natural clay, 34 weight of water Measure part, 2 parts by weight of bonding agent, 1 parts by weight of foaming agent.
Comparative example 1
A, carbon nanotube is mixed with ammonium metavanadate, titanium dioxide, oxalic acid liquid, is heated, catalytic activity liquid is made;
B, skeleton steel wire is immersed in the catalytic activity liquid of step a, simultaneously pre-burning is taken out after 28min, pre-burning felt is made;
C, by hydrotalcite, silica, aluminium oxide, indium oxide, zeolite, natural clay and water mixed grinding, and be added bonding agent, Slurry is made;
D, the slurry of step c is coated on to the pre-burning felt surface of step b, further calcine, be made for flue-gas dust removal and purification Filter felt.
In step b, skeleton steel wire average thickness is 3mm;In step c, bonding agent is epoxy resin adhesive;Step c In, foaming agent is sodium bicarbonate;
In step a, heating temperature is 48 DEG C, soaking time 12min;In step b, calcined temperature is 290 DEG C, temperature 1h; In step d, calcination temperature is 950 DEG C, time 4.5h;
In step a, 27 parts by weight of carbon nanotube, 5 parts by weight of ammonium metavanadate, 14 parts by weight of titanium dioxide, 54 parts by weight of oxalic acid liquid;Step In rapid b, 27 parts by weight of pre-burning felt, 73 parts by weight of catalytic activity liquid;In step c, 12 parts by weight of hydrotalcite, 5 weight of silica 1 Part, 6 parts by weight of aluminium oxide, 3 parts by weight of indium oxide, 3 parts by weight of zeolite, 24 parts by weight of natural clay, 34 parts by weight of water, bonding agent 2 parts by weight, 1 parts by weight of foaming agent;
Filter felt made from above-described embodiment 1 ~ 5 and comparative example 1 tests micro mist dust concentration and denitration efficiency, tests the side of characterization Method or condition are as follows:
Micro mist dust concentration:At 25 DEG C, fume sample is passed through to the dust removal and filtration system for having installed the filter felt, carries out micro dust Filtration test, flue gas flow rate 0.5m/s measure the concentration of micro dust in the front and back flue gas of filtering, table using dust detector respectively Levy the filter effect to micro dust.
Denitration efficiency:At 25 DEG C, fume sample is passed through to the denitrating system for having installed the filter felt, flue gas flow rate is 0.5m/s measures the nitrous oxides concentration C before denitration using nitrogen oxides detector1With the nitrous oxides concentration C after denitration2, press According to formula η=(C1-C2)/ C1 × 100% calculates denitration efficiency, characterizes the removal effect to nitrogen oxides.
The results are shown in Table 1.
Table 1:

Claims (10)

1. a kind of preparation method of filter felt for flue-gas dust removal and purification, which is characterized in that the filter felt is by containing bonding The slurry of agent and foaming agent is coated on the surface of the aerosil pre-burning felt of load ammonium metavanadate, is made through calcining, Specifically preparation process is:
A, carbon nanotube is mixed with ammonium metavanadate, titanium dioxide, oxalic acid liquid, is heated, catalytic activity liquid is made;
B, aerosil felt is immersed in the catalytic activity liquid of step a, simultaneously pre-burning is taken out after 20 ~ 30min, thickness is made For the pre-burning felt of 2 ~ 3mm;
C, by hydrotalcite, silica, aluminium oxide, indium oxide, zeolite, natural clay and water mixed grinding, and be added bonding agent, Slurry is made in foaming agent;
D, the slurry of step c is coated on to the pre-burning felt surface of step b, further calcined, slurry porcelainization is made to form micropore ceramics The filter felt for flue-gas dust removal and purification is made in film.
2. the preparation method of a kind of filter felt for flue-gas dust removal and purification according to claim 1, it is characterised in that:It is described In step a, heating temperature is 40 ~ 50 DEG C, and soaking time is 10 ~ 20min.
3. the preparation method of a kind of filter felt for flue-gas dust removal and purification according to claim 1, it is characterised in that:It is described In step a, 22 ~ 28 parts by weight of carbon nanotube, 4 ~ 6 parts by weight of ammonium metavanadate, 10 ~ 15 parts by weight of titanium dioxide, 51 ~ 64 weight of oxalic acid liquid Measure part.
4. the preparation method of a kind of filter felt for flue-gas dust removal and purification according to claim 1, it is characterised in that:It is described In step b, 20 ~ 30 parts by weight of aerosil felt, 70 ~ 80 parts by weight of catalytic activity liquid.
5. the preparation method of a kind of filter felt for flue-gas dust removal and purification according to claim 1, it is characterised in that:It is described In step b, calcined temperature is 200 ~ 300 DEG C, and temperature is 1 ~ 2h.
6. the preparation method of a kind of filter felt for flue-gas dust removal and purification according to claim 1, it is characterised in that:It is described In step c, bonding agent is at least one of epoxy resin adhesive or phenolic resin binder.
7. the preparation method of a kind of filter felt for flue-gas dust removal and purification according to claim 1, it is characterised in that:It is described In step c, foaming agent is at least one of saleratus, sodium bicarbonate or calcium bicarbonate.
8. the preparation method of a kind of filter felt for flue-gas dust removal and purification according to claim 1, it is characterised in that:It is described In step c, 10 ~ 12 parts by weight of hydrotalcite, 3 ~ 16 parts by weight of silica 1,4 ~ 6 parts by weight of aluminium oxide, 2 ~ 4 weight of indium oxide Part, 2 ~ 4 parts by weight of zeolite, 20 ~ 25 parts by weight of natural clay, 29 ~ 47 parts by weight of water, 1 ~ 2 parts by weight of bonding agent, foaming agent 1 ~ 2 Parts by weight.
9. a kind of filter felt and preparation method for flue-gas dust removal and purification according to claim 1, it is characterised in that:It is described In step d, calcination temperature is 800 ~ 1000 DEG C, and the time is 3 ~ 5h.
10. a kind of filter felt for flue-gas dust removal and purification that any one of claim 1 ~ 9 preparation method is prepared.
CN201810210096.2A 2018-03-14 2018-03-14 A kind of filter felt and preparation method for flue-gas dust removal and purification Withdrawn CN108421309A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810210096.2A CN108421309A (en) 2018-03-14 2018-03-14 A kind of filter felt and preparation method for flue-gas dust removal and purification

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810210096.2A CN108421309A (en) 2018-03-14 2018-03-14 A kind of filter felt and preparation method for flue-gas dust removal and purification

Publications (1)

Publication Number Publication Date
CN108421309A true CN108421309A (en) 2018-08-21

Family

ID=63158388

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810210096.2A Withdrawn CN108421309A (en) 2018-03-14 2018-03-14 A kind of filter felt and preparation method for flue-gas dust removal and purification

Country Status (1)

Country Link
CN (1) CN108421309A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109091956A (en) * 2018-10-15 2018-12-28 安徽元琛环保科技股份有限公司 A kind of preparation method of the dedusting denitrification integral filtrate based on ceramic fibre
CN111229035A (en) * 2020-01-21 2020-06-05 鞍钢股份有限公司 Denitration method suitable for sintering flue gas

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109091956A (en) * 2018-10-15 2018-12-28 安徽元琛环保科技股份有限公司 A kind of preparation method of the dedusting denitrification integral filtrate based on ceramic fibre
CN111229035A (en) * 2020-01-21 2020-06-05 鞍钢股份有限公司 Denitration method suitable for sintering flue gas

Similar Documents

Publication Publication Date Title
JP4831801B2 (en) Method and apparatus for removing mercury from exhaust gas
KR101298305B1 (en) Apparatus for removing of trace of toxic substance from exhaust gas and method of operating the same
JP5051977B2 (en) Device for removing trace harmful substances in exhaust gas and operation method thereof
CN108176224A (en) A kind of regeneration fume from catalytic cracking ammonia process of desulfurization denitration dust collecting method and device
CN107376639B (en) Hazardous waste incineration flue gas purification method
CN101791561B (en) Desulphurization and denitration catalyst and preparation method thereof
CN104841420A (en) Denitration catalyst activity mother liquor preparation method and application of denitration catalyst activity mother liquor
CN111773915B (en) Flue gas dry desulfurization process
CN110124708A (en) A kind of cement kiln flue gas SCR denitration catalyst and denitrating system
CN205032070U (en) Desulfurization dust removal denitration integrated device
CN106669670A (en) Preparation method of flue gas desulfurization agent
WO2020191915A1 (en) Cement kiln flue gas denitration, demercuration, and desulphurisation system and method
CN108421309A (en) A kind of filter felt and preparation method for flue-gas dust removal and purification
CN113842761A (en) Garbage tail gas treatment system and method
CN107420927A (en) A kind of fire coal boiler fume high-efficient purification and UTILIZATION OF VESIDUAL HEAT IN technique
CN105833692A (en) Industrial fume dry type low-temperature synergic dedusting desulfurization and denitrification mercury removal integrated device and process
EP1726565A1 (en) Carbon material and flue gas treatment apparatus
CN107990335A (en) A kind of environment-friendly and energy-efficient industrial waste gas burning processing device
US20060178263A1 (en) Carbon material and flue gas treatment apparatus
CN106512687A (en) Powdered coal industrial boiler flue gas denitrifying system and denitrifying method
CN109847578A (en) A kind of various pollutants of fume cooperation-removal method
CN115970485A (en) Ultralow-emission treatment device and process for regenerated metal flue gas
CN110614028A (en) Low-temperature flue gas SO in cement kiln2、NOxAnd Hg0Cooperative control system and method
CN216062684U (en) Garbage tail gas treatment system
JP2004066009A (en) Carbon material and equipment for treating flue gas

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
WW01 Invention patent application withdrawn after publication
WW01 Invention patent application withdrawn after publication

Application publication date: 20180821