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CN1194176A - New technology for absorbing and eliminating sulfur dioxide in smoke chemically - Google Patents

New technology for absorbing and eliminating sulfur dioxide in smoke chemically Download PDF

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Publication number
CN1194176A
CN1194176A CN97103626A CN97103626A CN1194176A CN 1194176 A CN1194176 A CN 1194176A CN 97103626 A CN97103626 A CN 97103626A CN 97103626 A CN97103626 A CN 97103626A CN 1194176 A CN1194176 A CN 1194176A
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China
Prior art keywords
desulfurization
ammonium
regeneration
ammonium sulfite
desulfurizer
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CN97103626A
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Chinese (zh)
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CN1086148C (en
Inventor
邵春岩
金重阳
祁国恕
蒋桂华
彭万寿
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Shenyang Academy Environmental Sciences
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Shenyang Academy Environmental Sciences
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Priority to CN 97103626 priority Critical patent/CN1086148C/en
Publication of CN1194176A publication Critical patent/CN1194176A/en
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Publication of CN1086148C publication Critical patent/CN1086148C/en
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Abstract

The new technological process of eliminating SO2 in smoke with ammonia water consists of two parts, the desulfurization and the regeneration of desulfurizing agent. It uses the liquid mixture of hydrated ammonia and ammonium sulfite as absorbing liquid to absorb SO2 in smoke and to produce liquid mixture of ammonium sulfite and ammonium bisulfite, and the used liquid mixture is then regenerated by calcium hydroxide for reuse. The whole process consumes only calcium hydroxide, and no precipitate produces in desulfurization, so that it has high desulfurization effect and low cost.

Description

Novel process for absorbing and removing sulfur dioxide in flue gas by using chemical method
The invention relates to a flue gas treatment process, in particular to a novel process for absorbing and removing sulfur dioxide in flue gas by adopting a chemical method.
With the development of industrial production scale, industrial waste gas is discharged in large quantity, acid rain and acid mist are generated in many places, the human health and the biological balance of an ecosystem are directly harmed, and meanwhile certain damage is caused to buildings and ancient cultural relics. The generation of acid rain and acid mist is mainly caused by the sulfur-containing components in the fuel, and a large amount of sulfur dioxide is generated in the combustion process of the fuel. At present, the domestic flue gas desulfurization method mainly adopts lime milk to absorb sulfur dioxide in flue gas, the absorption rate of the sulfur dioxide is low, and the solubility of calcium hydroxide is low, and in addition, calcium sulfite produced in the desulfurization process is precipitated, so that the equipment is complex, the operation is difficult, and the pipeline blockage phenomenon is easily produced, so that the fatal defects of short service life, large investment and the like exist.
The invention aims to provide a novel efficient flue gas desulfurization process with simple process, simple equipment, low investment and low cost.
The desulfurization process provided by the invention comprises two parts of desulfurization and desulfurizer regeneration:
first, desulfurization part
The desulfurization part comprises a plurality of desulfurizers, and desulfurization is carried out by utilizing a forward absorption method;
firstly, absorbing sulfur dioxide in flue gas by absorption liquid consisting of mixed liquid of ammonia water and ammonium sulfite or pure ammonium sulfite solution through a desulfurizer to generate ammonium sulfite and ammonium bisulfite; the two ammonium salt solutions enter a regeneration part; the desulfurized flue gas passes through an ammonia absorption tower to form ammonium sulfite and ammonium bisulfite, and the ammonium sulfite and the ammonium bisulfite are returned to the regeneration part;
secondly, a desulfurizer regeneration part
The desulfurizing agent regeneration part is composed of a plurality of regeneration tanks, absorption liquid from a desulfurizer enters the regeneration tanks, calcium hydroxide is added, the temperature is controlled at 20-70 ℃, the reaction is carried out for 2-6 minutes, and the absorption liquid returns to the desulfurization part immediately after ammonium sulfite is generated; or reacting for 0.1-2 hours under the condition to generate ammonia monohydrate, and filtering to obtain a mixed solution of the ammonia monohydrate and the ammonium sulfite after the reaction is finished, wherein the mixed solution is used as a desulfurizing agent for repeated use.
The desulfurization process disclosed by the invention has high desulfurization efficiency, and does not generate precipitate in the desulfurization process, so that the problem of pipeline blockage does not exist; in addition, the whole equipment is simple, the investment is low, and the desulfurizer can be regenerated and used, so that the flue gas desulfurization cost is low, and the method is suitable for wide popularization and application.
The present invention will be described in detail with reference to specific examples.
FIG. 1 is a process flow diagram of the present invention.
As shown inthe figure, the desulfurization process provided by the invention consists of two parts, namely desulfurization and desulfurizer regeneration; the desulfurization part adopts a desulfurizer, sulfur dioxide in the flue gas is absorbed by a forward absorption method, the absorption liquid can adopt a mixed solution of ammonium monohydrate and ammonium sulfite or a pure ammonium sulfite solution, the absorption liquid of the embodiment adopts a mixed solution of ammonium hydrate and ammonium sulfite, the mixed solution reacts with the sulfur dioxide in the flue gas in the desulfurizer to generate a mixed solution of ammonium bisulfite and ammonium sulfite, and the mixed solution enters the regeneration part; and the flue gas discharged by the desulfurizer enters an ammonia absorption tower, the ammonia absorption tower is used for absorbing ammonia in the flue gas to generate ammonium sulfite and ammonium bisulfite, the ammonium sulfite and the ammonium bisulfite are returned to a regeneration part, and finally the flue gas without sulfur dioxide is emptied. The chemical equation for the above reaction is as follows:
and (3) introducing the absorption liquid from the desulfurizer into a regeneration tank, adding calcium hydroxide into the regeneration tank, controlling the temperature at 50 ℃, and reacting for 1 hour. The reaction formula is as follows:
this step of the reaction can completely and completely produce ammonium sulfite.
The conversion rate of the monohydrate ammonia generated by the reaction in the step can reach 90 percent.
After the reaction is finished, filtering to obtain mixed liquid of ammonium monohydrate and ammonium sulfite, and reusing the mixed liquid as a desulfurizing agent.

Claims (1)

1. A high-efficiency flue gas desulfurization process is characterized in that: it is composed of two parts of desulfurization and desulfurizer regeneration:
first, desulfurization part
The desulfurization part comprises a plurality of desulfurizers, and desulfurization is carried out by utilizing a forward absorption method;
firstly, absorbing sulfur dioxide in flue gas by absorption liquid consisting of mixed liquid of ammonia water and ammonium sulfite or pure ammonium sulfite solution through a desulfurizer to generate ammonium sulfite and ammonium bisulfite; the two ammonium salt solutions enter a regeneration part; the desulfurized flue gas passes through an ammonia absorption tower to form ammonium sulfite and ammonium bisulfite, and the ammonium sulfite and the ammonium bisulfite are returned to the regeneration part;
secondly, a desulfurizer regeneration part
The desulfurizing agent regeneration part is composed of a plurality of regeneration tanks, absorption liquid from a desulfurizer enters the regeneration tanks, calcium hydroxide is added, the temperature is controlled at 20-70 ℃, the reaction is carried out for 2-6 minutes, and the absorption liquid returns to the desulfurization part immediately after ammonium sulfite is generated; or reacting for 0.1-2 hours under the condition to generate ammonia monohydrate, and filtering to obtain a mixed solution of the ammonia monohydrate and the ammonium sulfite after the reaction is finished, wherein the mixed solution is used as a desulfurizing agent for repeated use.
CN 97103626 1997-03-21 1997-03-21 New technology for absorbing and eliminating sulfur dioxide in smoke chemically Expired - Fee Related CN1086148C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN 97103626 CN1086148C (en) 1997-03-21 1997-03-21 New technology for absorbing and eliminating sulfur dioxide in smoke chemically

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN 97103626 CN1086148C (en) 1997-03-21 1997-03-21 New technology for absorbing and eliminating sulfur dioxide in smoke chemically

Publications (2)

Publication Number Publication Date
CN1194176A true CN1194176A (en) 1998-09-30
CN1086148C CN1086148C (en) 2002-06-12

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CN 97103626 Expired - Fee Related CN1086148C (en) 1997-03-21 1997-03-21 New technology for absorbing and eliminating sulfur dioxide in smoke chemically

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CN (1) CN1086148C (en)

Cited By (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1086959C (en) * 1999-10-14 2002-07-03 王晋宁 Flue gas desulfurizing agent and method
CN1092994C (en) * 1999-02-05 2002-10-23 魏雄辉 Gas decarbonization, desulfuration and decyanation technology by Fe-alkalisolution catalyst method
CN1132663C (en) * 2000-07-04 2003-12-31 罗广福 Method for removing sulphur oxides from smelting equipment flue gas
WO2004022205A1 (en) * 2002-09-09 2004-03-18 East China University Of Science & Technology Method and apparatus for eliminating and recovering s02 from fume
CN1321723C (en) * 2003-09-17 2007-06-20 镇江市江南环保设备研究所 Method of separating and recovering sulfur dioxide in smoke using ammonia method
CN100430113C (en) * 2006-09-29 2008-11-05 云南亚太环境工程设计研究有限公司 Process and apparatus for eliminating fume SO2 from waste coking ammonia water of iron and steel and coal chemical enterprise
CN100460045C (en) * 2006-05-31 2009-02-11 中国石油化工股份有限公司 Process for disposing SOx in discharge gas
CN101429070B (en) * 2008-12-05 2011-05-04 聊城鲁西化工第四化肥厂 Method for producing azophoska complex fertilizer with boiler flue gas and sulphuric acid tail gas
CN101549246B (en) * 2009-04-30 2011-08-17 杭州三和环保技术工程有限公司 Sintering flue gas desulfurization combined coking coal gas deamination cycling system
CN101596399B (en) * 2009-06-29 2011-11-16 安徽工业大学 Self-suction oxidation desulfuration process and device thereof
CN102485324A (en) * 2011-04-15 2012-06-06 安徽理工大学 Ammonium sulphate-limestone method for desulphurization of flue gas
CN102485325A (en) * 2011-04-19 2012-06-06 安徽理工大学 Flue gas desulphurization technology with ammonium sulfate-calcium hydroxide slurry method
EP2500082A1 (en) * 2011-03-15 2012-09-19 Linde Aktiengesellschaft Method and assembly for de-nitrification of exhaust gas
CN101612515B (en) * 2008-06-28 2013-01-02 金隆铜业有限公司 Wet flue gas desulfurization method
CN106422730A (en) * 2016-08-31 2017-02-22 张明鑫 Double wet method flue gas desulphurization and dust removal treatment process
CN107497270A (en) * 2017-04-28 2017-12-22 武志军 The method of ammonia calcium combined desulfurization

Cited By (19)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1092994C (en) * 1999-02-05 2002-10-23 魏雄辉 Gas decarbonization, desulfuration and decyanation technology by Fe-alkalisolution catalyst method
CN1086959C (en) * 1999-10-14 2002-07-03 王晋宁 Flue gas desulfurizing agent and method
CN1132663C (en) * 2000-07-04 2003-12-31 罗广福 Method for removing sulphur oxides from smelting equipment flue gas
WO2004022205A1 (en) * 2002-09-09 2004-03-18 East China University Of Science & Technology Method and apparatus for eliminating and recovering s02 from fume
CN1321723C (en) * 2003-09-17 2007-06-20 镇江市江南环保设备研究所 Method of separating and recovering sulfur dioxide in smoke using ammonia method
CN100460045C (en) * 2006-05-31 2009-02-11 中国石油化工股份有限公司 Process for disposing SOx in discharge gas
CN100430113C (en) * 2006-09-29 2008-11-05 云南亚太环境工程设计研究有限公司 Process and apparatus for eliminating fume SO2 from waste coking ammonia water of iron and steel and coal chemical enterprise
CN101612515B (en) * 2008-06-28 2013-01-02 金隆铜业有限公司 Wet flue gas desulfurization method
CN101429070B (en) * 2008-12-05 2011-05-04 聊城鲁西化工第四化肥厂 Method for producing azophoska complex fertilizer with boiler flue gas and sulphuric acid tail gas
CN101549246B (en) * 2009-04-30 2011-08-17 杭州三和环保技术工程有限公司 Sintering flue gas desulfurization combined coking coal gas deamination cycling system
CN101596399B (en) * 2009-06-29 2011-11-16 安徽工业大学 Self-suction oxidation desulfuration process and device thereof
EP2500082A1 (en) * 2011-03-15 2012-09-19 Linde Aktiengesellschaft Method and assembly for de-nitrification of exhaust gas
CN102485324A (en) * 2011-04-15 2012-06-06 安徽理工大学 Ammonium sulphate-limestone method for desulphurization of flue gas
CN102485324B (en) * 2011-04-15 2015-12-16 安徽理工大学 The method of sulphur ammonium-limestone-based process flue gas desulfurization
CN102485325A (en) * 2011-04-19 2012-06-06 安徽理工大学 Flue gas desulphurization technology with ammonium sulfate-calcium hydroxide slurry method
CN102485325B (en) * 2011-04-19 2015-06-24 安徽理工大学 Flue gas desulphurization technology with ammonium sulfate-calcium hydroxide slurry method
CN106422730A (en) * 2016-08-31 2017-02-22 张明鑫 Double wet method flue gas desulphurization and dust removal treatment process
CN106422730B (en) * 2016-08-31 2018-12-07 张明鑫 Double wet process of FGD dust removal process techniques
CN107497270A (en) * 2017-04-28 2017-12-22 武志军 The method of ammonia calcium combined desulfurization

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