[go: up one dir, main page]

CN107321135A - A kind of low temperature charcoal base combined desulfurization and denitration flue gas system and its application method - Google Patents

A kind of low temperature charcoal base combined desulfurization and denitration flue gas system and its application method Download PDF

Info

Publication number
CN107321135A
CN107321135A CN201710717818.9A CN201710717818A CN107321135A CN 107321135 A CN107321135 A CN 107321135A CN 201710717818 A CN201710717818 A CN 201710717818A CN 107321135 A CN107321135 A CN 107321135A
Authority
CN
China
Prior art keywords
reactor
switching valve
flue gas
ngd
plenum chamber
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
CN201710717818.9A
Other languages
Chinese (zh)
Inventor
王乃继
张鑫
李婷
曹好
闫黎黎
程晓磊
王永英
梁兴
肖翠微
杨石
陈隆
张广琦
刘振宇
崔豫鸿
刘增斌
苗鹏
徐大宝
李小炯
谭静
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.)
Energy Saving Technology Co Ltd
China Coal Research Institute CCRI
Original Assignee
Energy Saving Technology Co Ltd
China Coal Research Institute CCRI
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 Energy Saving Technology Co Ltd, China Coal Research Institute CCRI filed Critical Energy Saving Technology Co Ltd
Priority to CN201710717818.9A priority Critical patent/CN107321135A/en
Publication of CN107321135A publication Critical patent/CN107321135A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • B01D53/75Multi-step processes
    • 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
    • B01D53/02Separation 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 by adsorption, e.g. preparative gas chromatography
    • B01D53/04Separation 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 by adsorption, e.g. preparative gas chromatography with stationary adsorbents
    • 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
    • B01D53/8603Removing sulfur compounds
    • B01D53/8609Sulfur oxides
    • 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
    • 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
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/10Oxidants
    • B01D2251/102Oxygen
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/20Reductants
    • B01D2251/206Ammonium compounds
    • B01D2251/2062Ammonia
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/10Inorganic adsorbents
    • B01D2253/102Carbon
    • 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
    • B01DSEPARATION
    • B01D2259/00Type of treatment
    • B01D2259/40Further details for adsorption processes and devices
    • B01D2259/40083Regeneration of adsorbents in processes other than pressure or temperature swing adsorption
    • B01D2259/40088Regeneration of adsorbents in processes other than pressure or temperature swing adsorption by heating
    • B01D2259/4009Regeneration of adsorbents in processes other than pressure or temperature swing adsorption by heating using hot gas

Landscapes

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

Abstract

The present invention relates to a kind of low temperature charcoal base combined desulfurization and denitration flue gas system and its application method, wherein, the system includes completely identical in structure first reactor, second reactor and the 3rd reactor, first reactor, second reactor and the 3rd reactor include filling active carbon material in centrally located charcoal bedding layer, left and right sides cloth style grid and the left and right sides plenum chamber in outside, charcoal bedding layer.The present invention is by using identical three reactors, while having fine de-sulfur, denitration and regeneration function, fine de-sulfur, denitrification process series connection are in parallel with regenerative process, and can carry out simultaneously, really realize in-situ regeneration.The reactor of the present invention is made up of charcoal bedding layer, left and right sides cloth style grid and the left and right sides plenum chamber in center, and bed front face area is big, it is ensured that gas is evenly distributed in its work and regenerative process, and reduces occupation area of equipment.The present invention makes the desulphurization denitration performance of active carbon material be further enhanced.

Description

A kind of low temperature charcoal base combined desulfurization and denitration flue gas system and its application method
Technical field
Join the present invention relates to a kind of combined desulfurization and denitration flue gas system and its application method, more particularly to a kind of low temperature charcoal base Close desulphurization denitration flue gas system and its application method.
Background technology
At present, in the flue gas desulfurization and denitrification technology of boiler of power plant, Industrial Boiler and industrial furnace, active carbon material (such as activated coke) desulfurization combined purifying technique with its water saving, integrated purifying, non-secondary pollution, the low advantage of operation temperature at home It has been applied outside.Due to the limited sorption capacity of active carbon material, lost activity after desulphurization denitration, must be by regeneration Can activity recovery simultaneously recycle, therefore the regeneration of active carbon material is essential process in the technique use.
A kind of existing flue gas pollutant joint removal methods based on activity solid absorbent, the main body of this method is main It is made up of the grey calcium circulation desulfurization (NGD) of high magnification, active carbon material fine de-sulfur and active carbon material denitrification apparatus, using direct heat The mode of flue gas, solves the regeneration issues of active carbon material, realizes the reasonable employment of the energy, with higher desulfurization Efficiency and denitration efficiency, achieve good effect.The regeneration of this method carbon material uses in-situ regeneration, but carbon material is used In still can partly move, produce abrasion, and operate it is relative complex.
The content of the invention
In view of the above-mentioned problems, it is an object of the invention to provide a kind of low temperature charcoal base combined desulfurization and denitration flue gas system and its making With method, problem present in existing process is further solved, desulphurization and denitration agent regenerative process can be realized simultaneously, it is real to realize In-situ regeneration, and it is simple to operation, the desulphurization denitration performance of active carbon material is further enhanced.
To achieve the above object, the present invention takes following technical scheme:A kind of low temperature charcoal base combined desulfurization and denitration flue gas system System, it is characterised in that it includes completely identical in structure first reactor, second reactor and the 3rd reactor, described first Reactor, second reactor and the 3rd reactor include centrally located charcoal bedding layer, left and right sides cloth style grid and outside Left and right sides plenum chamber, filling active carbon material in charcoal bedding layer;
Wherein, the left side plenum chamber of the first reactor is by connecting pipe and the outlet of NGD equipment, heating furnace and draws Blower fan is connected, and sets first to switch on the connecting pipe of the outlet with the NGD equipment, heating furnace and air-introduced machine respectively Valve, the 4th switching valve and the 3rd switching valve;The right side plenum chamber of the first reactor is set by connecting pipe with ammonia area and NGD Standby entrance is connected, and respectively with set on the connecting pipe of the ammonia area and the entrance of NGD equipment the second switching valve and 5th switching valve;
The left side plenum chamber of the second reactor is by connecting pipe and the outlet of the NGD equipment, heating furnace and draws Blower fan is connected, and sets the 6th to switch on the connecting pipe of the outlet with the NGD equipment, heating furnace and air-introduced machine respectively Valve, the 9th switching valve and the 8th switching valve;The right side plenum chamber of the second reactor by connecting pipe and the ammonia area and The entrance of NGD equipment is connected, and respectively with setting the 7th to switch on the connecting pipe of the ammonia area and the entrance of NGD equipment Valve and the 8th switching valve;
The left side plenum chamber of 3rd reactor is by connecting pipe and the outlet of the NGD equipment, heating furnace and draws Blower fan is connected, and respectively on the connecting pipe of the outlet with the NGD equipment, heating furnace and air-introduced machine set the tenth all Change valve, the 14th switching valve and the 13rd switching valve;The right side plenum chamber of 3rd reactor by connecting pipe with it is described Ammonia area is connected with the entrance of NGD equipment, and respectively with setting on the connecting pipe of the ammonia area and the entrance of NGD equipment 12 switching valves and the 15th switching valve.
A kind of application method of low temperature charcoal base combined desulfurization and denitration flue gas system, comprises the following steps:
1) by the first switching valve, the second switching valve, the 7th switching valve, the 8th switching valve, the 14th switching valve and the 15th Switching valve is opened, and remaining switching valve is closed, and first reactor is used as denitration reaction as fine de-sulfur reactor, second reactor Device, the 3rd reactor, as regeneration reactor, is now the first stage;
2) after the catalyst inactivation in first reactor of the first stage as fine de-sulfur reactor, the tenth is simultaneously closed off Four switching valves and the 15th switching valve, open the 12nd switching valve and the 13rd switching valve, close the 8th switching valve;Is opened again Six switching valves, close the first switching valve and the second switching valve, open the 4th switching valve and the 5th switching valve;So as to which first be reacted Device switches to regeneration reactor;Second reactor is switched into fine de-sulfur reactor simultaneously, the 3rd reactor is switched into denitration Reactor, is now second stage;
3) after the catalyst inactivation in second reactor of the second stage as fine de-sulfur reactor, the 4th is simultaneously closed off Switching valve and the 5th switching valve, open the second switching valve and the 3rd switching valve, close the 13rd switching valve;Open again the tenth all Valve is changed, the 6th switching valve and the 7th switching valve is closed, the 9th switching valve and the tenth switching valve is opened;So as to which second reactor be cut Regeneration reactor is changed to, while the 3rd reactor is switched into fine de-sulfur reactor, first reactor is switched into denitration reaction Device, is now the phase III;
4) after the catalyst inactivation in the 3rd reactor of the phase III as fine de-sulfur reactor, the 9th is simultaneously closed off Switching valve and the tenth switching valve, open the 7th switching valve and the 8th switching valve, close the 3rd switching valve;The first switching is opened again Valve, closes the 11st switching valve and the 12nd switching valve, opens the 14th switching valve and the 15th switching valve;So as to anti-by the 3rd Answer device to switch to regeneration reactor, first reactor is switched into fine de-sulfur reactor, switches to denitration anti-second reactor Device is answered, now system switches back into the first stage;So move in circles.
The flow direction for having completed the flue gas after thick desulfurization from NGD is advanced fine de-sulfur reactor, then enters Benitration reactor, Fine de-sulfur, denitrification process series connection;Meanwhile, the heat smoke from heating furnace enters regeneration reactor, regenerative process and fine de-sulfur and Denitrification process is in parallel;The flue gas completed after thick desulfurization from NGD enters the left side plenum chamber of fine de-sulfur reactor, then through a left side The SO that side cloth style grid enter in the charcoal bedding layer of fine de-sulfur reactor, flue gas2Removed by active carbon material, with the water in flue gas Generation H is combined with oxygen2SO4Absorption is in active carbon material hole;Remove SO2Flue gas afterwards enters right side through right side cloth style grid Plenum chamber, the flue gas for going out fine de-sulfur reactor from right side plenum chamber is mixed with dilution ammonia, subsequently into the right side of Benitration reactor Side plenum chamber, then the NO entered through right side cloth style grid in the charcoal bedding layer of Benitration reactor, flue gas is in the presence of catalyst, Or by NH3Reduction generation N2And H2O takes away with flue gas, or by O in flue gas2Oxidation generation NO2, and adsorb in active carbon material hole It is interior;Remove left side cloth style grid of the flue gas through Benitration reactor after NO and enter left side plenum chamber, plenum chamber goes out denitration from left side The clean flue gas of reactor is discharged into air by air-introduced machine;Meanwhile, the heat smoke from heating furnace enters the left side of regeneration reactor Plenum chamber, then through left side cloth style grid into the charcoal bedding layer of regeneration reactor, the regeneration gas that active carbon material is produced is by heating agent Carry, through right side cloth style grid enter right side plenum chamber, the flue gas for going out regeneration reactor from right side plenum chamber return to before NGD with The fresh smoke mixing that boiler is produced, subsequently into NGD, so as to realize in-situ regeneration.
The present invention is due to taking above technical scheme, and it has advantages below:1st, a kind of low temperature charcoal base of the invention joint Desulphurization denitration flue gas system and its application method, by using identical three reactors, while having fine de-sulfur, denitration And regeneration function, fine de-sulfur, denitrification process series connection are in parallel with regenerative process, and can carry out simultaneously, really realize in-situ regeneration. 2nd, a kind of low temperature charcoal base combined desulfurization and denitration flue gas system of the invention and its application method, take off due to having carried out depth before denitration Sulphur, therefore reduce the influence to denitration reaction, it is ensured that denitration efficiency.3rd, a kind of low temperature charcoal base combined desulfurization of the invention takes off Nitre flue gas system and its application method, Benitration reactor can be adjusted flexibly according to smoke behavior, when flue-gas temperature is higher than 100 DEG C When, it is passed through the reducing agents such as ammonia and nitrogen oxides is reduced to nitrogen, when flue-gas temperature is less than 100 DEG C, passes through reactor carbon materials Material bed catalyst oxidation generation nitrogen dioxide is simultaneously adsorbed, and sending into NGD desulfurizers by regenerative process absorbs.4th, of the invention one Low temperature charcoal base combined desulfurization and denitration flue gas system and its application method are planted, as a result of identical fixed bed reactors, is passed through Valve transfer realizes power and energy, has both improved the utilization rate and interchangeability of equipment, and quick, convenient switching can be realized again.5、 A kind of low temperature charcoal base combined desulfurization and denitration flue gas system and its application method of the present invention, reactor by center charcoal bedding layer, Left and right sides cloth style grid and left and right sides plenum chamber composition, bed front face area are big, it is ensured that gas in its work and regenerative process It is evenly distributed, and reduces occupation area of equipment.
Brief description of the drawings
Fig. 1 is the structural representation of the present invention;
Fig. 2 is the structural representation of present invention work in the first stage;
Fig. 3 is the structural representation that the present invention is operated in second stage;
Fig. 4 is the structural representation that the present invention is operated in the phase III.
Embodiment
The present invention is described in detail with reference to the accompanying drawings and examples.
Charcoal base combined desulfurization and denitration flue gas system, is that the grey calcium circulating flue gas desulfurization (NGD) of high magnification is urged with charcoal based selective Change the part of reduction and oxidation (C-SCR and C-SCO) denitrating flue gas coupling technique system, the flue gas after the thick desulfurization of NGD enters Activated coke combined desulfurization and denitration device, completes fine de-sulfur and C-SCR and C-SCO denitrations.Whole bed after absorbent charcoal based catalyst inactivation Regeneration, the heating agent that regeneration needs is a small amount of clean flue gas after circulating fan pressurizes and reheated through boiler furnace.Carbon material The regeneration gas of generation carries out combined desulfurization and denitration device by heating agent, and it is mixed to return to the fresh smoke produced before NGD with boiler Close, subsequently into NGD riser reactors, SO therein2、NO2Finally by the active Ca (OH) in circulating ash2Absorb and solidify, Desulfurization degree more than 98%, denitration rate more than 90% finally can be achieved.
Based on above-mentioned principle, as shown in figure 1, a kind of low temperature charcoal base combined desulfurization and denitration flue gas system that the present invention is provided, It includes first reactor A, second reactor B and the 3rd reactor C, first reactor A, second reactor B and the 3rd reaction Device C is identical, and can not only be used for fine de-sulfur reactor, can also be used as Benitration reactor or regeneration reactor;First is anti- Device A, second reactor B and the 3rd reactor C is answered to include charcoal bedding layer, left and right sides cloth style grid and the left and right sides gas collection in center Filling active carbon material in case, charcoal bedding layer.
Wherein, first reactor A left side plenum chamber passes through connecting pipe and outlet, heating furnace and the air inducing of NGD equipment Machine is connected, and sets the first switching valve A on the connecting pipe of the outlet with NGD equipment, heating furnace and air-introduced machine respectively1、 4th switching valve A4With the 3rd switching valve A3;First reactor A right side plenum chamber passes through connecting pipe and ammonia area and NGD equipment Entrance be connected, and respectively with setting the second switching valve A on the connecting pipe of ammonia area and the entrance of NGD equipment2With the 5th Switching valve A5.Second reactor B left side plenum chamber passes through connecting pipe and the outlet of NGD equipment, heating furnace and air-introduced machine phase Connection, and the 6th switching valve B is set on the connecting pipe of the outlet with NGD equipment, heating furnace and air-introduced machine respectively1, the 9th Switching valve B4With the 8th switching valve B3;Second reactor B right side plenum chamber is entered by connecting pipe and ammonia area and NGD equipment Mouth is connected, and respectively with setting the 7th switching valve B on the connecting pipe of ammonia area and the entrance of NGD equipment2With the tenth switching Valve B5.3rd reactor C left side plenum chamber is connected by connecting pipe with the outlet of NGD equipment, heating furnace and air-introduced machine, And the 11st switching valve C is set on the connecting pipe of the outlet with NGD equipment, heating furnace and air-introduced machine respectively1, the 14th cut Change valve C4With the 13rd switching valve C3;3rd reactor C right side plenum chamber is entered by connecting pipe and ammonia area and NGD equipment Mouth is connected, and respectively with setting the 12nd switching valve C on the connecting pipe of ammonia area and the entrance of NGD equipment2With the 15th Switching valve C5.By controlling the first to the 15th switching valve A1-A5、B1-B5And C1-C5Opening and closing, control the thick desulfurization from NGD Flue gas, the heat smoke from heating furnace and the NH3 from ammonia area pass through first reactor A, second reactor B, the 3rd reactor C Sequencing so that realize fine de-sulfur, denitration and regenerate three processes switching;And fine de-sulfur, denitrification process are connected, Ran Houyu Regenerative process is in parallel, and fine de-sulfur and denitrification process are carried out simultaneously with regenerative process, really realize in-situ regeneration.
A kind of low temperature charcoal base combined desulfurization and denitration flue gas system of the present invention when in use, comprises the following steps:
1) as shown in Fig. 2 by the first switching valve A1, the second switching valve A2, the 7th switching valve B2, the 8th switching valve B3, the tenth Four switching valve C4With the 15th switching valve C5Open, other switching valves are closed.The flue gas completed after thick desulfurization warp from NGD First switching valve A1Plenum chamber on the left of into first reactor A, then enter first reactor A charcoal beddings through left side cloth style grid SO in layer, flue gas2Removed by active carbon material, generation H is combined with the water and oxygen in flue gas2SO4Absorption is in active carbon material hole In gap.Remove SO2Flue gas afterwards enters right side plenum chamber through right side cloth style grid, goes out first reactor A's from right side plenum chamber Flue gas is in the second switching valve A2Afterwards at flue gas house steward, mixed with the dilution ammonia from ammonia-spraying grid.Increase the flue gas after ammonia through the Seven switching valve B2Plenum chamber on the right side of into second reactor B, then enter second reactor B charcoals bedding layer through right side cloth style grid, NO in flue gas is in the presence of catalyst, or by NH3Reduction generation N2And H2O takes away with flue gas, or by O in flue gas2Oxidation life Into NO2, and adsorb in active carbon material hole.Remove the flue gas after NO and enter left through cloth style grid on the left of second reactor B Side plenum chamber.Go out second reactor B clean flue gas through the 8th switching valve B from left side plenum chamber3Air is discharged into by air-introduced machine.Together When, the heat smoke from heating furnace is through the 14th switching valve C4Plenum chamber on the left of into the 3rd reactor C, then through left side cloth style Grid enter the 3rd reactor C charcoals bedding layer, and the regeneration gas that active carbon material is produced is carried by heating agent, entered through right side cloth style grid Right side plenum chamber, the flue gas for going out the 3rd reactor C from right side plenum chamber returns to the fresh smoke produced before NGD with boiler and mixed Close, subsequently into NGD riser reactors, so as to realize in-situ regeneration.The flow direction of flue gas is advanced fine de-sulfur reactor, then is entered Benitration reactor, therefore first reactor A is fine de-sulfur reactor, second reactor B is Benitration reactor, the 3rd reactor C It it is now the first stage for regeneration reactor.
2) as shown in figure 3, after catalyst inactivation in first reactor A of the first stage as fine de-sulfur reactor, Simultaneously close off the 14th switching valve C4With the 15th switching valve C5, open the 12nd switching valve C2With the 13rd switching valve C3, close 8th switching valve B3;The 6th switching valve B is opened again1, close the first switching valve A1With the second switching valve A2, open the 4th switching valve A4 With the 5th switching valve A5;So as to which first reactor A is switched into regeneration reactor;Switch to essence de- second reactor B simultaneously Reaction of Salmon-Saxl device, Benitration reactor is switched to by the 3rd reactor C, is now second stage.
3) as shown in figure 4, after catalyst inactivation in second reactor B of the second stage as fine de-sulfur reactor, Simultaneously close off the 4th switching valve A4With the 5th switching valve A5, open the second switching valve A2With the 3rd switching valve A3, close the 13rd and cut Change valve C3;The 11st switching valve C is opened again1, close the 6th switching valve B1With the 7th switching valve B2, open the 9th switching valve B4With Ten switching valve B5;So as to which second reactor B is switched into regeneration reactor, while switching to fine de-sulfur anti-3rd reactor C Device is answered, first reactor A is switched into Benitration reactor, is now the phase III.
4) after the catalyst inactivation in the 3rd reactor C of the phase III as fine de-sulfur reactor, is simultaneously closed off Nine switching valve B4With the tenth switching valve B5, open the 7th switching valve B2With the 8th switching valve B3, close the 3rd switching valve A3;Open again First switching valve A1, close the 11st switching valve C1With the 12nd switching valve C2, open the 14th switching valve C4With the 15th switching Valve C5;So as to which the 3rd reactor C is switched into regeneration reactor, first reactor A is switched into fine de-sulfur reactor, by second Reactor B switches to Benitration reactor, and now system switches back into the first stage.So move in circles, realize in-situ regeneration.
The various embodiments described above are merely to illustrate the present invention, wherein the structure of each part, set location and its connected mode etc. It can all be varied from, every equivalents carried out on the basis of technical solution of the present invention and improvement should not be arranged In addition in protection scope of the present invention.

Claims (3)

1. a kind of low temperature charcoal base combined desulfurization and denitration flue gas system, it is characterised in that it is anti-that it includes completely identical in structure first Device, second reactor and the 3rd reactor are answered, the first reactor, second reactor and the 3rd reactor are included in being located at The active carbon materials of filling in charcoal bedding layer, left and right sides cloth style grid and the left and right sides plenum chamber in outside of centre, the charcoal bedding layer Material;
Wherein, the left side plenum chamber of the first reactor passes through connecting pipe and outlet, heating furnace and the air-introduced machine of NGD equipment Be connected, and set respectively on the connecting pipe of the outlet with the NGD equipment, heating furnace and air-introduced machine the first switching valve, 4th switching valve and the 3rd switching valve;The right side plenum chamber of the first reactor passes through connecting pipe and ammonia area and NGD equipment Entrance be connected, and respectively with setting the second switching valve and on the connecting pipe of the ammonia area and the entrance of NGD equipment Five switching valves;
The left side plenum chamber of the second reactor passes through connecting pipe and outlet, heating furnace and the air-introduced machine of the NGD equipment Be connected, and respectively on the connecting pipe of the outlet with the NGD equipment, heating furnace and air-introduced machine set the 6th switching valve, 9th switching valve and the 8th switching valve;The right side plenum chamber of the second reactor passes through connecting pipe and the ammonia area and NGD The entrance of equipment is connected, and respectively with setting the 7th switching valve on the connecting pipe of the ammonia area and the entrance of NGD equipment With the 8th switching valve;
The left side plenum chamber of 3rd reactor passes through connecting pipe and outlet, heating furnace and the air-introduced machine of the NGD equipment It is connected, and sets the 11st to switch on the connecting pipe of the outlet with the NGD equipment, heating furnace and air-introduced machine respectively Valve, the 14th switching valve and the 13rd switching valve;The right side plenum chamber of 3rd reactor passes through connecting pipe and the ammonia Area is connected with the entrance of NGD equipment, and respectively with setting the tenth on the connecting pipe of the ammonia area and the entrance of NGD equipment Two switching valves and the 15th switching valve.
2. a kind of application method of low temperature charcoal base combined desulfurization and denitration flue gas system, comprises the following steps:
1) by the first switching valve, the second switching valve, the 7th switching valve, the 8th switching valve, the 14th switching valve and the 15th switching Valve is opened, and remaining switching valve is closed, and first reactor is as fine de-sulfur reactor, and second reactor is as Benitration reactor, and the Three reactors, as regeneration reactor, are now the first stage;
2) after the catalyst inactivation in first reactor of the first stage as fine de-sulfur reactor, simultaneously close off the 14th and cut Valve and the 15th switching valve are changed, the 12nd switching valve and the 13rd switching valve is opened, the 8th switching valve is closed;The 6th is opened again to cut Valve is changed, the first switching valve and the second switching valve is closed, the 4th switching valve and the 5th switching valve is opened;So as to which first reactor be cut It is changed to regeneration reactor;Second reactor is switched into fine de-sulfur reactor simultaneously, the 3rd reactor is switched into denitration reaction Device, is now second stage;
3) after the catalyst inactivation in second reactor of the second stage as fine de-sulfur reactor, the 4th switching is simultaneously closed off Valve and the 5th switching valve, open the second switching valve and the 3rd switching valve, close the 13rd switching valve;The 11st switching is opened again Valve, closes the 6th switching valve and the 7th switching valve, opens the 9th switching valve and the tenth switching valve;So as to which second reactor be switched For regeneration reactor, while the 3rd reactor is switched into fine de-sulfur reactor, first reactor is switched into Benitration reactor, It is now the phase III;
4) after the catalyst inactivation in the 3rd reactor of the phase III as fine de-sulfur reactor, the 9th switching is simultaneously closed off Valve and the tenth switching valve, open the 7th switching valve and the 8th switching valve, close the 3rd switching valve;The first switching valve is opened again, is closed The 11st switching valve and the 12nd switching valve are closed, the 14th switching valve and the 15th switching valve is opened;So as to by the 3rd reactor Regeneration reactor is switched to, first reactor is switched into fine de-sulfur reactor, second reactor is switched into Benitration reactor, Now system switches back into the first stage;So move in circles.
3. a kind of application method of low temperature charcoal base combined desulfurization and denitration flue gas system as claimed in claim 2, it is characterised in that The flow direction for having completed the flue gas after thick desulfurization from NGD is advanced fine de-sulfur reactor, then enters Benitration reactor, fine de-sulfur, Denitrification process is connected;Meanwhile, the heat smoke from heating furnace enters regeneration reactor, regenerative process and fine de-sulfur and denitrification process It is in parallel;
The flue gas completed after thick desulfurization from NGD enters the left side plenum chamber of fine de-sulfur reactor, then through left side cloth style The SO that grid enter in the charcoal bedding layer of fine de-sulfur reactor, flue gas2Removed, combined with the water and oxygen in flue gas by active carbon material Generate H2SO4Absorption is in active carbon material hole;Remove SO2Flue gas afterwards enters right side plenum chamber through right side cloth style grid, from The flue gas that right side plenum chamber goes out fine de-sulfur reactor is mixed with dilution ammonia, subsequently into the right side plenum chamber of Benitration reactor, The NO entered again through right side cloth style grid in the charcoal bedding layer of Benitration reactor, flue gas is in the presence of catalyst, or by NH3Also It is primary into N2And H2O takes away with flue gas, or by O in flue gas2Oxidation generation NO2, and adsorb in active carbon material hole;Removing Left side cloth style grid of the flue gas through Benitration reactor after NO enter left side plenum chamber, and from left side, plenum chamber goes out Benitration reactor Clean flue gas is discharged into air by air-introduced machine;
Meanwhile, the heat smoke from heating furnace enters the left side plenum chamber of regeneration reactor, then enters again through left side cloth style grid The charcoal bedding layer of raw reactor, the regeneration gas that active carbon material is produced is carried by heating agent, enters right side collection through right side cloth style grid Gas tank, the flue gas for going out regeneration reactor from right side plenum chamber returns to the fresh smoke produced before NGD with boiler and mixed, Ran Houjin Enter NGD, so as to realize in-situ regeneration.
CN201710717818.9A 2017-08-21 2017-08-21 A kind of low temperature charcoal base combined desulfurization and denitration flue gas system and its application method Pending CN107321135A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710717818.9A CN107321135A (en) 2017-08-21 2017-08-21 A kind of low temperature charcoal base combined desulfurization and denitration flue gas system and its application method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710717818.9A CN107321135A (en) 2017-08-21 2017-08-21 A kind of low temperature charcoal base combined desulfurization and denitration flue gas system and its application method

Publications (1)

Publication Number Publication Date
CN107321135A true CN107321135A (en) 2017-11-07

Family

ID=60224468

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710717818.9A Pending CN107321135A (en) 2017-08-21 2017-08-21 A kind of low temperature charcoal base combined desulfurization and denitration flue gas system and its application method

Country Status (1)

Country Link
CN (1) CN107321135A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108126492A (en) * 2018-02-01 2018-06-08 北京国能中电节能环保技术股份有限公司 Flue gas desulfurization and denitrification device
CN110966613A (en) * 2019-12-20 2020-04-07 煤科院节能技术有限公司 Method and system for treating low-temperature denitration inactivation activated carbon material thermal regeneration waste gas
CN111495138A (en) * 2020-04-26 2020-08-07 安徽顺达环保科技股份有限公司 Desulfurization and denitrification equipment and process capable of circularly accelerating flue gas cracking catalysis

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0568850A (en) * 1991-09-12 1993-03-23 Mitsubishi Heavy Ind Ltd Method for simultaneously denitrating and desulfurizing exhaust gas of combustor
CN101574622A (en) * 2008-05-05 2009-11-11 韩松 Dry-method desulphurization and deodorization technology with high efficiency low pressure drop
CN105597531A (en) * 2016-02-17 2016-05-25 中国科学院过程工程研究所 Desulfurization and denitration device and technology used for purifying coke oven smoke
CN106563351A (en) * 2016-09-23 2017-04-19 中冶华天南京工程技术有限公司 Vertical modular flue gas desulfurization and denitrification adsorption regeneration integration system
CN107051104A (en) * 2017-05-12 2017-08-18 江苏净领环保科技有限公司 A kind of modular unit and technique for handling organic exhaust gas
CN207221629U (en) * 2017-08-21 2018-04-13 煤科院节能技术有限公司 A kind of low temperature charcoal base combined desulfurization and denitration flue gas system

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0568850A (en) * 1991-09-12 1993-03-23 Mitsubishi Heavy Ind Ltd Method for simultaneously denitrating and desulfurizing exhaust gas of combustor
CN101574622A (en) * 2008-05-05 2009-11-11 韩松 Dry-method desulphurization and deodorization technology with high efficiency low pressure drop
CN105597531A (en) * 2016-02-17 2016-05-25 中国科学院过程工程研究所 Desulfurization and denitration device and technology used for purifying coke oven smoke
CN106563351A (en) * 2016-09-23 2017-04-19 中冶华天南京工程技术有限公司 Vertical modular flue gas desulfurization and denitrification adsorption regeneration integration system
CN107051104A (en) * 2017-05-12 2017-08-18 江苏净领环保科技有限公司 A kind of modular unit and technique for handling organic exhaust gas
CN207221629U (en) * 2017-08-21 2018-04-13 煤科院节能技术有限公司 A kind of low temperature charcoal base combined desulfurization and denitration flue gas system

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108126492A (en) * 2018-02-01 2018-06-08 北京国能中电节能环保技术股份有限公司 Flue gas desulfurization and denitrification device
CN110966613A (en) * 2019-12-20 2020-04-07 煤科院节能技术有限公司 Method and system for treating low-temperature denitration inactivation activated carbon material thermal regeneration waste gas
CN111495138A (en) * 2020-04-26 2020-08-07 安徽顺达环保科技股份有限公司 Desulfurization and denitrification equipment and process capable of circularly accelerating flue gas cracking catalysis
CN111495138B (en) * 2020-04-26 2022-05-06 安徽顺达环保科技股份有限公司 Desulfurization and denitrification equipment and process capable of circularly accelerating flue gas cracking catalysis

Similar Documents

Publication Publication Date Title
CN103239985B (en) Efficient fuel coal flue gas desulfurizing and hydrargyrum-removing method and device thereof
CN103007679B (en) Flue gas cleaning system capable of switching pollutant desorption technology and adsorbent regeneration technology and method thereof
CN101279186B (en) Flue gas dry-type method for simultaneously desulfurizing and denitrating
CN111495112A (en) Low temperature removes integration of bed and adsorbs SOx/NOx control system
CN105413326B (en) A kind of activated coke flue gas purification system
CN102188891B (en) Acidic oxidation-alkaline reduction purification process of exhaust gas containing nitrogen oxides
CN102974181A (en) Flue gas dedusting and desulfurization and denitrification craft and special device thereof
CN207221629U (en) A kind of low temperature charcoal base combined desulfurization and denitration flue gas system
CN107321135A (en) A kind of low temperature charcoal base combined desulfurization and denitration flue gas system and its application method
CN201020334Y (en) Desulfurization denitration integrative smoke purifying device
CN109499313A (en) The low-temp desulfurization method of denitration of sintering flue gas
CN201586464U (en) Large-scale active coke convection adsorption flue gas purification system
CN110180355A (en) A kind of wet-dry change combined desulfurization and denitration running gear and method
CN100434144C (en) Boiler low-temperature flue gas SCR combined adsorption-desorption catalytic bed to prevent ammonia escape
CN105536515A (en) Two-stage flue gas desulphurization and denitration system and treating method
CN212790372U (en) Low temperature fixed bed integration adsorbs SOx/NOx control system
CN203108371U (en) Special device for flue gas dust removal desulfurization and denitrification process
CN108211698A (en) Coal-fired flue-gas all contaminants level Four cleaning system and method
CN206424781U (en) Horizontal modularization flue gas desulfurization and denitrification absorption regeneration integral system
CN108654363A (en) Couple waste heat of coke-oven flue gas and amounts of sulphur contaminants acid-making process
CN209865775U (en) Denitration device for activated carbon fixed bed
CN210522265U (en) Ozone desulfurization and denitrification system
CN213853889U (en) Waste incineration flue gas treatment system
CN214287417U (en) An integrated removal device for flue gas pollutants
CN214261076U (en) Sintering flue gas circulation combined full-pollutant integrated treatment device

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: 20171107

RJ01 Rejection of invention patent application after publication