GB1349196A - Flue gas desulphurization process - Google Patents
Flue gas desulphurization processInfo
- Publication number
- GB1349196A GB1349196A GB1823771A GB1823771A GB1349196A GB 1349196 A GB1349196 A GB 1349196A GB 1823771 A GB1823771 A GB 1823771A GB 1823771 A GB1823771 A GB 1823771A GB 1349196 A GB1349196 A GB 1349196A
- Authority
- GB
- United Kingdom
- Prior art keywords
- absorbent
- returned
- flue gas
- absorber
- hso
- 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.)
- Expired
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
- B01D53/50—Sulfur oxides
- B01D53/501—Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Environmental & Geological Engineering (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Treating Waste Gases (AREA)
Abstract
1349196 Desulphurization of flue gas ESSO RESEARCH & ENG CO 1 June 1971 [1 June 1970] 18237/71 Heading C1A In a process for desulphurizing an SO 2 and O 2 containing flue gas in which a small amount of S<SP>VI</SP> is formed in the course of absorbing SO 2 in an aqueous absorbent containing NH 3 and/ or NH 4 <SP>+</SP> and in which at least a part of the absorber effluent (containing S<SP>IV</SP> and S<SP>VI</SP>) is acidified with NH 4 HSO 4 to form SO 2 and an aqueous mixture of (NH 4 )SO 4 and (NH 4 )HSO 4 , the major portion of the (NH 4 ) 2 SO 4 content of said mixture is decomposed to form (NH 4 )HSO 4 and NH 3 and a major portion of the (NH 4 )HSO 4 thus produced is returned to the acidifier where it is used for acidification of the absorber effluent, a minor portion being returned to the furnace, in which the flue gas is produced, where it is decomposed into a gaseous mixture of N 2 , SO 2 and water thereby reducing the S<SP>VI</SP> content of the system. It is preferred that the amount of bisulphate returned to the furnace is equivalent to the sum of the amount of S<SP>VI</SP> formed and the amount of SO 3 present in the flue gas, that the absorbent contains ammonium sulphite as solute. Liberated SO 2 may be converted into useful products such as S or H 2 SO 4 and ammonia liberated in the decomposition stage may be reacted with a second portion of the absorber effluent which is not acidified, to produce fresh absorbent. In the drawing the flue gas leaving furnace 10 is cooled by exchange with combustion air in heat exchanger 12 before passing up absorber tower 20 against a stream of aqueous ammoniacal absorbent solution. Desulphurized gas containing <10% of the original SO 2 content is vented at 23. The absorbent passes to holding tank 25 and from there a portion is passed to acidifier 30 where it is treated with ammonium bisulphate via 31. The slurry produced on acidification and after liberation of SO 2 via 32 is passed into a stream of hot gas 34 and decomposer 35 where water is evaporated and the ammonium sulphate content of the slurry is decomposed to yield gaseous ammonia and ammonium bisulphate. The ammonium bisulphate is returned in major proportion to acidifier 30 via line 31, the minor proportion being returned via line 50 to furnace 14, either in molten state or as a particulate solid, where it is decomposed to produce SO 2 , N 2 and H 2 O. Ammonia leaving decomposer 35 is returned to ammoniator 40 where it is contacted with absorber effluent taken from line 28 and diluted with water in liner 41-42 to produce fresh absorbent which is recycled via lines 43 and 46 to absorber 20 via holding tank 21. Line 40 and cooler 45 are employed for circulation and cooling of the regenerated absorbent from 40 in order to maintain a desired temperature in said ammoniator.
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US4194270A | 1970-06-01 | 1970-06-01 |
Publications (1)
Publication Number | Publication Date |
---|---|
GB1349196A true GB1349196A (en) | 1974-03-27 |
Family
ID=21919173
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
GB1823771A Expired GB1349196A (en) | 1970-06-01 | 1971-06-01 | Flue gas desulphurization process |
Country Status (4)
Country | Link |
---|---|
CA (1) | CA948377A (en) |
DE (1) | DE2126818A1 (en) |
FR (1) | FR2095750A5 (en) |
GB (1) | GB1349196A (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4151263A (en) * | 1977-07-29 | 1979-04-24 | Air Products And Chemicals, Inc. | Removal of sulfur oxides from gases by scrubbing with ammoniacal solutions |
-
1971
- 1971-05-29 DE DE19712126818 patent/DE2126818A1/en active Pending
- 1971-05-31 CA CA114,405A patent/CA948377A/en not_active Expired
- 1971-06-01 GB GB1823771A patent/GB1349196A/en not_active Expired
- 1971-06-01 FR FR7119803A patent/FR2095750A5/fr not_active Expired
Also Published As
Publication number | Publication date |
---|---|
DE2126818A1 (en) | 1971-12-16 |
FR2095750A5 (en) | 1972-02-11 |
CA948377A (en) | 1974-06-04 |
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Legal Events
Date | Code | Title | Description |
---|---|---|---|
PS | Patent sealed | ||
PCNP | Patent ceased through non-payment of renewal fee |