CN105617861B - A kind of dry powder adsorbent flue injection removing SO3Equipment - Google Patents

A kind of dry powder adsorbent flue injection removing SO3Equipment Download PDF

Info

Publication number
CN105617861B
CN105617861B CN201610202418.XA CN201610202418A CN105617861B CN 105617861 B CN105617861 B CN 105617861B CN 201610202418 A CN201610202418 A CN 201610202418A CN 105617861 B CN105617861 B CN 105617861B
Authority
CN
China
Prior art keywords
storage tank
tank
pneumatic
gravimetric
dry powder
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.)
Active
Application number
CN201610202418.XA
Other languages
Chinese (zh)
Other versions
CN105617861A (en
Inventor
张志刚
王海刚
胡冬
郭婷婷
贾嘉
王艺霏
张冠军
邱桂芝
陈坤洋
高智溥
吴智泉
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.)
China Datang Corp Science and Technology Research Institute Co Ltd
Original Assignee
China Datang Corp Science and Technology Research Institute 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 China Datang Corp Science and Technology Research Institute Co Ltd filed Critical China Datang Corp Science and Technology Research Institute Co Ltd
Priority to CN201610202418.XA priority Critical patent/CN105617861B/en
Publication of CN105617861A publication Critical patent/CN105617861A/en
Application granted granted Critical
Publication of CN105617861B publication Critical patent/CN105617861B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

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
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/508Sulfur oxides by treating the gases with solids
    • 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
    • B01D53/06Separation 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 moving adsorbents, e.g. rotating beds
    • 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
    • B01D53/90Injecting reactants
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/30Alkali metal compounds
    • B01D2251/304Alkali metal compounds of sodium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/40Alkaline earth metal or magnesium compounds
    • B01D2251/404Alkaline earth metal or magnesium compounds of calcium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • B01D2257/302Sulfur oxides
    • 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
    • B01D2259/12Methods and means for introducing reactants
    • B01D2259/128Solid reactants

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)

Abstract

The present invention relates to coal-fired flue-gas Pollutant Control Technology fields, and in particular to a kind of dry powder adsorbent flue injection removing SO3Equipment.It includes the storage tank for storing dry powder alkaline adsorbent, the top of storage tank is equipped with reservoir inlet and storage tank exhaust outlet, storage tank exhaust outlet is connected by storage tank appendix with the air inlet of storage tank filter, the middle part of storage tank appendix is connected by being equipped with the pipeline of the first pneumatic pipe valve with first pressure gas source, the top of storage tank is equipped with the micro positive pressure device for making to keep micro-positive pressure in storage tank, the lower part of storage tank is cone angle cone bucket shape directed downwardly, the bottom of storage tank is equipped with reservoir outlet, pneumatic feeding machine is equipped at reservoir outlet, the lower section of pneumatic feeding machine is equipped with gravimetric tank, the discharge port of pneumatic feeding machine is connected by pneumatic feeding machine conveying pipeline with the feed inlet at the top of gravimetric tank, pneumatic feeding machine conveying pipeline is connected by being equipped with the pipeline of pipe valve with second pressure gas source, the top of gravimetric tank is equipped with gravimetric tank exhaust outlet.

Description

A kind of dry powder adsorbent flue injection removing SO3Equipment
Technical field
The present invention relates to atmosphere pollution control technology fields, and in particular to a kind of dry powder adsorbent flue injection removing SO3Equipment.
Background technique
Coal-fired thermal power generation is the principal mode of the current electrical energy production in China.Data show that China's thermoelectricity generated energy is up to 80% or more of total power generation, wherein the electric installed capacity based on fire coal accounts for total capacity 75%, the energy nature in China is objective Determine that the power supply pattern based on coal-fired thermal power generation will not change in a short time.The flue gas of coal-burning power plant's discharge contains greatly Sulfide, NOx and heavy metal etc. are measured, wherein SO2It has been more than 50% with ratio of the NOx in flue gas.In addition to this one generated Secondary to be important industrial pollution source with secondary PM2.5, the atmosphere pollution of control coal-burning power plant discharge, which becomes, administers haze weather Main behave.SO in coal-fired flue-gas2There are about 1.5%-3% to be changed into SO3, as SO in flue gas3When concentration is more than 10ppm, with water Steam, which combines, forms small aerosol particle, improves flue gas acid dew point, causes low-temperature corrosion.In addition to environment and corrosion failure, SO3It is the main reason for causing SCR denitration system catalyst and air preheater cold-end air heat exchange element " stifled ash ", to cause air-introduced machine Stall influences to keep the safety in production.
Currently, the Conventional pollutions such as the electrostatic precipitator of coal fired power plant and WFGD control equipment to SO in flue gas3Removing effect Rate is lower.Main flue gas SO3Control technology includes mixing to burn low-sulfur coal, the low SO of exploitation2/SO3The SCR denitration of conversion ratio, Lime stone is added into fire coal and physics removing, the SO of the above apparatus and method are carried out using wet electrical dust precipitator3Removal effect Also it is difficult to meet the requirements.The Chinese patent of Patent No. 201120223113.X discloses a kind of sulfur trioxide tail gas absorption dress It sets, including absorption tower, sulfur trioxide reaction tower etc., the apparatus function is similar with WESP, can not solve SO3Caused by air preheat Device blockage problem.Patent No. 201310044506.8X discloses a kind of SO using trona slurries3Removing means, the dress It sets by injecting trona slurries into flue and removes SO3.The physicochemical characteristic of slurries is different with dry powder physicochemical property, device system Difference of uniting is big, meanwhile, slurry injection device way of realization is more complex, and reliability is poor.
Summary of the invention
The object of the present invention is to provide a kind of removing SO3It is high-efficient, remove SO3Thoroughly, stable and reliable for performance, to delay SO3 Caused by air preheater block, reduce SO3Caused upstream device corrosion, is effectively reduced the SO in flue gas3Content, reduction pair The destruction of ecological environment, and can effectively save the dry powder adsorbent flue injection removing SO of alkaline adsorbent3Equipment.
Dry powder adsorbent flue injection removing SO of the invention3Equipment, including the storage for storing dry powder alkaline adsorbent Tank, the top of storage tank are equipped with reservoir inlet and storage tank exhaust outlet, and storage tank exhaust outlet passes through storage tank appendix and storage tank filter Air inlet be connected, storage tank appendix be equipped with the first pneumatic pipe valve, the first pneumatic pipe valve pass through pneumatic line and first pressure Gas source is connected, and the top of storage tank is equipped with the micro positive pressure device for making to keep micro-positive pressure in the storage tank, and the lower part of storage tank is Cone angle cone bucket shape directed downwardly, the bottom of storage tank are equipped with reservoir outlet, are equipped with pneumatic feeding machine, pneumatic feeding at reservoir outlet The bottom of machine is equipped with discharge port, and the lower section of pneumatic feeding machine is equipped with gravimetric tank, and the discharge port of pneumatic feeding machine passes through pneumatic feeding Machine conveying pipeline is connected with the feed inlet at the top of gravimetric tank, and pneumatic feeding machine conveying pipeline is equipped with the second pneumatic pipe valve, and second is pneumatic Pipe valve is connected by pneumatic line with second pressure gas source, and the top of gravimetric tank is equipped with gravimetric tank exhaust outlet, gravimetric tank exhaust outlet It is connected by gravimetric tank appendix with the air inlet of gravimetric tank filter, gravimetric tank appendix is equipped with pneumatic pipe valve of weighing, and claims The pneumatic pipe valve of weight is connected by pneumatic line with second pressure gas source, and the bottom of gravimetric tank is equipped with gravimetric tank discharge port, gravimetric tank Lower section be equipped with rotary valve, gravimetric tank discharge port is connected by gravimetric tank conveying pipeline with the feed inlet at the top of rotary valve, gravimetric tank Conveying pipeline is equipped with the pneumatic pipe valve of third, and the pneumatic pipe valve of third is connected by pneumatic line with third pressure gas source, the rotation The bottom of valve is equipped with rotary valve discharge port;
The rotary valve discharge port is connected with the feed inlet being located on air delivery tube tube wall, the air inlet of air delivery tube It is connected with the air outlet of blower, the discharge port of air delivery tube is connected with the feed inlet of distributor, and the discharge port of distributor passes through Pipeline is connected with the multiple nozzles being located in flue.
Preferably, the micro-positive pressure of 0.4kPa -0.8kPa is kept in the powder storage tank.
Preferably, the blower is roots blower.
Preferably, the dry powder alkaline adsorbent is calcium hydroxide or sodium carbonate or sodium bicarbonate.
Preferably, the spray feed amount M (kg/h) and flue gas SO of the dry powder alkaline adsorbent2Concentration C (mg/Nm3) and flue gas Measure V (Nm3/ h) relationship are as follows:
M=4kCV
Wherein k takes 1.5 × 10-5-4×10-5
Technical solution of the present invention has the advantages that
Dry powder adsorbent flue injection removing SO of the invention3Equipment, can be according to SO in flue gas2Concentration makes alkaline adsorbent SO in the straying quatity and flue gas of feed powder3Amount match.To ensure that SO3Removal effect saves alkaline adsorbent feed powder.This The dry powder adsorbent flue injection removing SO of invention3Equipment, the tank top is equipped with micro positive pressure device, for keeping in storage tank The micro-positive pressure of 0.4kPa-0.8kPa realizes that powder is moisture-proof and blanking smoothly function.The pneumatic feeding machine is not only fed speed Degree is fast, and stable and reliable working performance.In addition, filter is provided at the top of the powder storage tank and gravimetric tank, for filtering What is be discharged from the tank injures containing dusty gas, reduction pollution environment and to the dust of operator.SO of the invention3Removing Equipment can change feed powder injection volume by adjusting rotary valve, make SO in alkaline adsorbent injection volume and flue gas3Amount match. To ensure that removal efficiency, thereby save alkaline adsorbent.Therefore, dry powder adsorbent flue of the invention injects removing SO3Equipment has removing SO3It is high-efficient, remove SO3Thoroughly, stable and reliable for performance, to delay SO3Caused by Blocking in Air Preheater Plug reduces SO3Caused upstream device corrosion, is effectively reduced the SO in flue gas3Content reduces the destruction to ecological environment, and can The characteristics of effectively saving alkaline adsorbent.
Dry powder adsorbent flue injection removing SO of the invention is further illustrated below in conjunction with accompanying drawings and embodiments3If It is standby.
Detailed description of the invention
Fig. 1 is dry powder adsorbent flue injection removing SO of the invention3The structural schematic diagram of equipment.
Specific embodiment
As shown in Figure 1, dry powder adsorbent flue injection removing SO of the invention3Equipment, including for storing dry powder alkalinity The storage tank 3 of adsorbent, the top of storage tank 3, which is equipped with reservoir inlet and storage tank exhaust outlet, can pass through the top of storage tank 3 when in use Dry powder alkaline adsorbent is added in storage tank 3 by the reservoir inlet in portion, and storage tank exhaust outlet passes through storage tank appendix and storage tank mistake The air inlet of filter 1 is connected, and storage tank filter 1 is used to filter the dust in the gas for getting rid of the discharge of storage tank 3, storage tank appendix Middle part be equipped with the first pneumatic pipe valve, the first pneumatic pipe valve is connected by pneumatic line with first pressure gas source 2, first pressure gas Source 2 can control the first pneumatic pipe valve to open or close, the top of storage tank 3 be equipped with for make to keep in the storage tank 3 it is micro- just The micro positive pressure device 12 of pressure realizes moisture-proof and blanking smoothly function.The lower part of storage tank 3 is cone angle cone bucket shape directed downwardly, storage tank 3 Bottom be equipped with reservoir outlet, the pneumatic feeding machine 4 for feed, the bottom of pneumatic feeding machine 4 are equipped at reservoir outlet Equipped with discharge port, the lower section of pneumatic feeding machine 4 is equipped with the gravimetric tank 6 for weighing, and the discharge port of pneumatic feeding machine 4 passes through pneumatic Batcher conveying pipeline is connected with the feed inlet at 6 top of gravimetric tank, when in use, can be realized by pneumatic feeding device 4 to storage tank 3 Input the control of the powder in weighing pot 6.Pneumatic feeding machine conveying pipeline is equipped with the second pneumatic pipe valve, and the second pneumatic pipe valve passes through gas Dynamic pipeline is connected with second pressure gas source 13, and second pressure gas source 13 can control opening or closing for the second pneumatic pipe valve, weighs The top of tank 6 is equipped with gravimetric tank exhaust outlet, and gravimetric tank exhaust outlet passes through the air inlet of gravimetric tank appendix and gravimetric tank filter 5 Mouthful it is connected, gravimetric tank filter 5 is used to filter the dust got rid of in the gas that gravimetric tank 6 is discharged, in gravimetric tank appendix Portion is equipped with pneumatic pipe valve of weighing, and pneumatic pipe valve of weighing is connected by pneumatic line with second pressure gas source 13, second pressure gas source 13 controllable pneumatic pipe valves of weighing open or close, and the bottom of gravimetric tank 6 is equipped with gravimetric tank discharge port, the lower section of gravimetric tank 6 Equipped with for making feed powder enter the rotary valve 7 of air delivery tube, gravimetric tank discharge port is pushed up by gravimetric tank conveying pipeline and rotary valve 7 The feed inlet in portion is connected, and gravimetric tank conveying pipeline is equipped with the pneumatic pipe valve of third, the pipeline and third pressure gas source of the pneumatic pipe valve of third 14 are connected, and third pressure gas source 14 can control opening or closing for the pneumatic pipe valve of third, and the bottom of rotary valve 7 goes out equipped with rotary valve Material mouth;
The rotary valve discharge port is connected with the feed inlet being located on air delivery tube tube wall, the air inlet of air delivery tube It is connected with the air outlet of blower 9, the discharge port of air delivery tube is connected with the feed inlet of distributor 10, and distributor 10 can be by air-flow The feed powder of delivery pipe conveying branches in multiple pipelines, and the discharge port of distributor 10 passes through pipeline and multiple sprays in flue Mouth 11 is connected.
Further, the micro-positive pressure of 0.4kPa -0.8kPa is kept in the powder storage tank 3.
Further, the blower 9 is roots blower.
Further, the dry powder alkaline adsorbent is calcium hydroxide or sodium carbonate or sodium bicarbonate.
Further, the spray feed amount M (kg/h) and flue gas SO of the dry powder alkaline adsorbent2Concentration C (mg/Nm3) and cigarette Tolerance V (Nm3/ h) relationship are as follows:
M=4kCV
Wherein k takes 1.5 × 10-5-4×10-5
Embodiment 1
Below by taking certain 600MW coal unit as an example, in conjunction with attached drawing, the invention will be further described.
The present embodiment provides a kind of dry powder adsorbent flues to inject removing SO3Equipment, as shown in Figure 1, comprising:
Storage tank 3, for storing dry powder alkaline adsorbent;
Gravimetric tank 6 is connected to the storage tank 3;
It is connected to, is realized by pneumatic feeding device 4 to powder storage tank by pneumatic feeding device 4 between storage tank 3 and weighing pot 6 3 are passed through the control of the powder in weighing pot 6.
Rotary valve 7 is arranged below gravimetric tank 6, for making feed powder enter air delivery tube;
Distributor 10, the feed powder for conveying air delivery tube shunt;
Nozzle 11 protrudes into the allocated device 10 in flue and is connected to by feeding pipeline with the rotary valve 7;
Roots blower 9 divides feed powder by the allocated device 10 of air delivery tube for feeding gas into air delivery tube It is sprayed after stream by nozzle 11;
Micro positive pressure device, for keeping the micro-positive pressure in storage tank;
It is respectively arranged with storage tank filter 1 and gravimetric tank filter 5 at the top of the powder storage tank 3 and gravimetric tank 6, was used for The dust in gas is discharged in filter tank.
Further, it is additionally provided with micro positive pressure device at the top of the powder storage tank 3, is protected in the powder storage tank 1 for making The micro-positive pressure of 0.4kPa-0.8kPa is held, realizes that powder is moisture-proof and blanking is smooth.
The present invention exports the flue between air preheater in SCR denitration reaction device and injects dry powder adsorbent, selected suction Attached dose is calcium hydroxide, and design adsorbent injection volume is 1.3ton/h.Utilize the strong basicity and SO of calcium hydroxide3Reaction, through SO3 Analyzer detection, this system can be by the SO of air preheater entrance3Mean concentration is down to 3.85ppm.Therefore, dry powder of the invention absorption Agent flue injection removing SO3Equipment has removing SO3It is high-efficient, remove SO3Thoroughly, stable and reliable for performance, to delay SO3It causes Air preheater blocking, reduce SO3Caused upstream device corrosion, is effectively reduced the SO in flue gas3Content reduces to ecology The destruction of environment, and the characteristics of can effectively save alkaline adsorbent.

Claims (3)

1. dry powder adsorbent flue injection removing SO3Equipment, it is characterised in that including the storage tank for storing dry powder alkaline adsorbent (3), the top of storage tank (3) is equipped with reservoir inlet and storage tank exhaust outlet, and storage tank exhaust outlet passes through storage tank appendix and storage tank mistake The air inlet of filter (1) is connected, and storage tank appendix is equipped with the first pneumatic pipe valve, and the first pneumatic pipe valve passes through pneumatic line and the One pressure gas source (2) is connected, and the top of storage tank (3) is equipped with the micro-positive pressure dress for making to keep micro-positive pressure in the storage tank (3) It sets (12), the lower part of storage tank (3) is cone angle cone bucket shape directed downwardly, and the bottom of storage tank (3) is equipped with reservoir outlet, reservoir outlet Place is equipped with pneumatic feeding machine (4), and the bottom of pneumatic feeding machine (4) is equipped with discharge port, and the lower section of pneumatic feeding machine (4) is equipped with weighing The discharge port of tank (6), pneumatic feeding machine (4) is connected by pneumatic feeding machine conveying pipeline with the feed inlet at the top of gravimetric tank (6), gas Dynamic batcher conveying pipeline is equipped with the second pneumatic pipe valve, and the second pneumatic pipe valve passes through pneumatic line and second pressure gas source (13) phase Even, the top of gravimetric tank (6) is equipped with gravimetric tank exhaust outlet, and gravimetric tank exhaust outlet passes through gravimetric tank appendix and gravimetric tank filter (5) air inlet is connected, and gravimetric tank appendix is equipped with pneumatic pipe valve of weighing, and pneumatic pipe valve of weighing passes through pneumatic line and second Pressure gas source (13) is connected, and the bottom of gravimetric tank (6) is equipped with gravimetric tank discharge port, and the lower section of gravimetric tank (6) is equipped with rotary valve (7), gravimetric tank discharge port is connected by gravimetric tank conveying pipeline with the feed inlet at the top of rotary valve (7), is set on gravimetric tank conveying pipeline There is the pneumatic pipe valve of third, the pneumatic pipe valve of third is connected by pneumatic line with third pressure gas source (14), the rotary valve (7) Bottom is equipped with rotary valve discharge port;
The rotary valve discharge port is connected with the feed inlet being located on air delivery tube tube wall, the air inlet and wind of air delivery tube The air outlet of machine (9) is connected, and the discharge port of air delivery tube is connected with the feed inlet of distributor (10), the discharging of distributor (10) Mouth is connected by pipeline with the multiple nozzles (11) being located in flue;
The spray feed amount M (kg/h) and flue gas SO of the dry powder alkaline adsorbent2Concentration C (mg/Nm3) and exhaust gas volumn V (Nm3/ h) Relationship are as follows:
M=4kCV
Wherein k takes 1.5 × 10-5-4×10-5
The micro-positive pressure of 0.4kPa or 0.8kPa is kept in the powder storage tank (3).
2. dry powder adsorbent flue injection removing SO according to claim 13Equipment, it is characterised in that the blower (9) is Roots blower.
3. dry powder adsorbent flue injection removing SO according to claim 23Equipment, it is characterised in that the dry powder alkalinity Adsorbent is calcium hydroxide or sodium carbonate or sodium bicarbonate.
CN201610202418.XA 2016-04-01 2016-04-01 A kind of dry powder adsorbent flue injection removing SO3Equipment Active CN105617861B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610202418.XA CN105617861B (en) 2016-04-01 2016-04-01 A kind of dry powder adsorbent flue injection removing SO3Equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610202418.XA CN105617861B (en) 2016-04-01 2016-04-01 A kind of dry powder adsorbent flue injection removing SO3Equipment

Publications (2)

Publication Number Publication Date
CN105617861A CN105617861A (en) 2016-06-01
CN105617861B true CN105617861B (en) 2019-04-23

Family

ID=56033438

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610202418.XA Active CN105617861B (en) 2016-04-01 2016-04-01 A kind of dry powder adsorbent flue injection removing SO3Equipment

Country Status (1)

Country Link
CN (1) CN105617861B (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106179739A (en) * 2016-08-02 2016-12-07 中国华电科工集团有限公司 Dust arrester and flue gas ash removal method
CN106861375A (en) * 2017-04-25 2017-06-20 广州冉升环保工程有限公司 The device and method that a kind of sulfur trioxide in flue gas is administered
CN108636096A (en) * 2018-06-08 2018-10-12 中国大唐集团科学技术研究院有限公司火力发电技术研究院 The method that alkaline adsorbent flue injects cooperation-removal heavy metal in flue gas and sour gas
CN109051815A (en) * 2018-06-29 2018-12-21 亚德(上海)环保***有限公司 A kind of dry-process deacidification material-transporting system
CN113844917A (en) * 2021-10-08 2021-12-28 佛山市金银河智能装备股份有限公司 Powder self-bleeding filtering mechanism
CN114159960A (en) * 2021-10-11 2022-03-11 中国大唐集团科学技术研究院有限公司火力发电技术研究院 Alkaline slurry injection SO that can accurate measurement is adjusted3Removal equipment

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201545512U (en) * 2009-06-10 2010-08-11 陈毅 Limestone continuous conveying system
CN102921291A (en) * 2012-11-21 2013-02-13 江苏中建材环保研究院有限公司 Novel integrated device for tempering and desulphurizing smoke of glass smelting kiln by utilizing dry method
CN102974211A (en) * 2012-11-06 2013-03-20 镇江市电站辅机厂有限公司 Circulating fluidized bed boiler in-furnace desulfurization device
CN203790809U (en) * 2014-02-22 2014-08-27 江苏中建材环保研究院有限公司 Alkaline material adding device based on wet desulphurization
CN205461810U (en) * 2016-04-01 2016-08-17 中国大唐集团科学技术研究院有限公司 Dry powder adsorbent flue injection desorption SO3's equipment

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201545512U (en) * 2009-06-10 2010-08-11 陈毅 Limestone continuous conveying system
CN102974211A (en) * 2012-11-06 2013-03-20 镇江市电站辅机厂有限公司 Circulating fluidized bed boiler in-furnace desulfurization device
CN102921291A (en) * 2012-11-21 2013-02-13 江苏中建材环保研究院有限公司 Novel integrated device for tempering and desulphurizing smoke of glass smelting kiln by utilizing dry method
CN203790809U (en) * 2014-02-22 2014-08-27 江苏中建材环保研究院有限公司 Alkaline material adding device based on wet desulphurization
CN205461810U (en) * 2016-04-01 2016-08-17 中国大唐集团科学技术研究院有限公司 Dry powder adsorbent flue injection desorption SO3's equipment

Also Published As

Publication number Publication date
CN105617861A (en) 2016-06-01

Similar Documents

Publication Publication Date Title
CN105617861B (en) A kind of dry powder adsorbent flue injection removing SO3Equipment
CN105195008A (en) Process and equipment for flue gas roasting, adsorption desulfurization, dust removal and purification by adopting combination process
CN104874269B (en) System and method for synchronous implementation of online monitoring of mercury content in flue gas and mercury removal
CN102794090A (en) Flue gas purifier utilizing combination of spray-drying method and hydrated lime powder injection
CN106139846A (en) A kind of sintering device flue gas dry desulfurization urea liquid direct-injection denitrification apparatus
CN102688684A (en) Fixed spray flue gas purifying device
CN204563902U (en) Flue gas circulating fluidized bed associating demercuration dearsenification device
CN204502789U (en) A kind of incinerator smoke denitration desulfurizer
CN204469514U (en) A kind of boiler smoke denitration in the stove device
CN201899980U (en) Complete device for treating sludge incineration tail gas in semidry method
CN104759204B (en) The associating demercuration dearsenization device of a kind of boiler smoke and removal methods thereof
CN104353350A (en) Smoke purification technology implemented based on adsorbent pretreatment
CN107252624A (en) The semi-dry desulphurization system and technique of a kind of utilization flyash
CN211799937U (en) Flue gas ultralow emission treatment device for biomass power plant
CN202823129U (en) Flue gas cleaning device of spray drying method combined with hydrated lime powder spraying
CN210278551U (en) Hg and SO3Bag type dust collector with synergistic removal
CN105889960A (en) Flue gas desulfurization device for coal-fired boiler
CN209155537U (en) Coke oven flue gas semi-dry desulphurization, dedusting and low-temperature denitration device
CN204582926U (en) A kind of boiler smoke denitration in the stove dry desulfurization device
CN108636096A (en) The method that alkaline adsorbent flue injects cooperation-removal heavy metal in flue gas and sour gas
CN205461810U (en) Dry powder adsorbent flue injection desorption SO3's equipment
CN202606003U (en) Fixed-spraying flue-gas purifying device
CN202224058U (en) Desulfurization and dust removal device for sprayed supersaturation water quicklime powder
CN106139879A (en) A kind of fire coal boiler fume denitration in the stove wet desulphurization device
CN204513432U (en) A kind of incinerator smoke denitration in the stove wet desulphurization device

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
EE01 Entry into force of recordation of patent licensing contract

Application publication date: 20160601

Assignee: YANGCHENG INTERNATIONAL POWER GENERATION Co.,Ltd.

Assignor: CHINA DATANG CORPORATION SCIENCE AND TECHNOLOGY RESEARCH INSTITUTE Co.,Ltd.

Contract record no.: X2020990000563

Denomination of invention: A device for removing so3by flue injection with dry powder adsorbent

Granted publication date: 20190423

License type: Common License

Record date: 20201028

Application publication date: 20160601

Assignee: INNER MONGOLIA DATANG INTERNATIONAL TUOKETUO POWER GENERATION Co.,Ltd.

Assignor: CHINA DATANG CORPORATION SCIENCE AND TECHNOLOGY RESEARCH INSTITUTE Co.,Ltd.

Contract record no.: X2020990000564

Denomination of invention: A device for removing so3by flue injection with dry powder adsorbent

Granted publication date: 20190423

License type: Common License

Record date: 20201028

Application publication date: 20160601

Assignee: YANGCHENG DATANG POWER GENERATION Co.,Ltd.

Assignor: CHINA DATANG CORPORATION SCIENCE AND TECHNOLOGY RESEARCH INSTITUTE Co.,Ltd.

Contract record no.: X2020990000565

Denomination of invention: A device for removing so3by flue injection with dry powder adsorbent

Granted publication date: 20190423

License type: Common License

Record date: 20201028

EE01 Entry into force of recordation of patent licensing contract