DE3235020A1 - Chemisorption process for absorbing preferably sulphur dioxide downstream of power stations, refuse incineration plants and the like - Google Patents
Chemisorption process for absorbing preferably sulphur dioxide downstream of power stations, refuse incineration plants and the likeInfo
- Publication number
- DE3235020A1 DE3235020A1 DE19823235020 DE3235020A DE3235020A1 DE 3235020 A1 DE3235020 A1 DE 3235020A1 DE 19823235020 DE19823235020 DE 19823235020 DE 3235020 A DE3235020 A DE 3235020A DE 3235020 A1 DE3235020 A1 DE 3235020A1
- Authority
- DE
- Germany
- Prior art keywords
- fed
- lime
- chemisorption
- power stations
- incineration plants
- 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.)
- Granted
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
- B01D53/508—Sulfur oxides by treating the gases with solids
-
- 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
-
- 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
- B01D53/54—Nitrogen compounds
- B01D53/56—Nitrogen oxides
-
- 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
- B01D53/68—Halogens or halogen compounds
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
Description
Beschreibung und Erläuterung zur PatentanmeldungDescription and explanation of the patent application
"Chemisorptionsverfahren zur Absorption von vorzugsweise Schwefeldioxid hinter Kraftwerken und Müllverbrennungsanlagen und dergleichen"."Chemisorption process for the absorption of preferably sulfur dioxide behind power plants and waste incineration plants and the like ".
Es ist bekannt, Trockenadditive in Wirbelbettreaktoren, Kontaktstrecken und ähnlichen Kontakteinrichtungen aufzugeben und hinter diesen Kontakteinrichtungen - wo der Frischkalk mit dem Schwefeldioxid in Kontakt gebracht wird - die Gewebefilter nachzuschalten, die dann den reagierten und/oder nicht reagierten Kalk abscheiden.It is known to use dry additives in fluidized bed reactors, contact sections and similar contact devices and behind these contact devices - where the fresh lime is brought into contact with the sulfur dioxide - the fabric filters downstream, which then deposit the reacted and / or unreacted lime.
Um die Reaktion in den Kontakteinbauten zu verbessern, wird vielfach Dampf zugegeben oder ein Sprühturm verwendet, bei dem eine Suspension aufgegeben wird, die einen Feststoffgehalt von ungefähr 35 % besitzt.In order to improve the reaction in the built-in contacts, many times Steam added or a spray tower used, in which a suspension is applied which has a solids content of approximately 35%.
Es läßt sich nicht vermeiden, daß nicht genügend SO, -trotz eingesprühter Suspension - im Sprühturm abgeschieden wird- und infolgedessen saure Bestandteile mit evtl. tröpfchenartigen, sauren Feuchtigkeitsanteilen in den Bereich des nachgeschalteten Gewebefilters eindringen.It cannot be avoided that not enough SO, -in spite of the sprayed in Suspension - is deposited in the spray tower - and, as a result, acidic components with possibly droplet-like, acidic moisture in the area of the downstream Penetrate the fabric filter.
Hier sind aufgrund dieser Tatsache Korrosionen die unabdingbare Folge.Because of this, corrosion is the inevitable consequence.
Um diesen Nachteil zu vermeiden, wird erfindungsgemäß folgende Verfahrenstechnologie vorgeschlagen.In order to avoid this disadvantage, the following process technology is used according to the invention suggested.
In der beiliegenden Zeichnung ist dargestellt: mit (1) das Rohgas; mit (2) ein Sprühturm - in dem die nasse Suspension aufgegeben wird; mit (3) eine Kontaktstrecke oder ein Trockenreaktor, in dem Frischkalk (6) aufgegeben wird; mit (4) Gewebefilter; mit (5) der Ventilator; mit (6) der Frischkalk; mit (7) der zum Teil bei (3) aufgegebene, mit den Schadstoffen reagierte Frischkalk2 der als Altkalk zum Mischer (8) geführt wird und mit Wasser zu einer Emulsion gemischt auf den Sprühturm (2) aufgegeben wird, mit (8) der Mischer; mit (9) der Austrag des mit S02, HC1, HF und weiteren Schadstoffen reagierten Kaltes; mit (do) Reingas zum Kamin.The accompanying drawing shows: with (1) the raw gas; with (2) a spray tower - in which the wet suspension is applied; with (3) a Contact section or a dry reactor in which fresh lime (6) is applied; with (4) bag filter; with (5) the fan; with (6) the fresh lime; with (7) the for Part of (3) abandoned, fresh lime2 reacted with the pollutants as old lime to the mixer (8) and mixed with water to form an emulsion on the spray tower (2) is abandoned, with (8) the mixer; with (9) the discharge of the cold reacted with SO2, HC1, HF and other pollutants; with (do) clean gas to Chimney.
Durch die erfindungsgemäße Zugabe des Friscbkalkes, nicht wie bisher üblich über einen Emulsionshersteller mit nachfolgender Aufgabe auf einen Sprühturm, sondern vorab bei (3) erfindungsgemäß in einer Kontaktstrecke oder einem trockenen Reaktor (z.B. Wirbelbettreaktor, rezirkulierender Reaktor oder dergleichen) wird der Frischkalk im weiteren Verlauf dann in einen Gewebefilter eingeführt und abgeschieden. Auf den Filterflächen absorbiert der abgeschiedene Kalk den Restanteil der im Rauchgas nach dem Sprühturm verbliebenen Schadstoffe, wirkt somit neutralisierend und alkalisierend, so daß das Gewebefilter in der bisher bekannten Korrosion dem Zubacken nicht mehr ausgesetzt ist.By adding the fresh lime according to the invention, not as before Usually via an emulsion manufacturer with the following task on a spray tower, but in advance at (3) according to the invention in a contact path or a dry one Reactor (e.g. fluidized bed reactor, recirculating reactor or the like) the fresh lime is then introduced into a fabric filter and deposited. The lime deposited on the filter surfaces absorbs the remaining portion of the flue gas pollutants remaining after the spray tower, thus has a neutralizing and alkalizing effect, so that the fabric filter no longer bakes in the previously known corrosion is exposed.
Die Reaktion im Trockenbereich - Kontaktstrecke (3) -als auch auf dem Gewebefilter (4) ist infolge der hohen Feuchte, die teilweise aus dem Sprühturm (2) in den Bereich (3) und (4) herübergerissen wird -sehr gut.The reaction in the dry area - contact section (3) - as well the fabric filter (4) is due to the high humidity, which is partly from the spray tower (2) is torn over into area (3) and (4) - very well.
Durch die Übergabe in den Sprühturm, durch Aufmischen über den Mischer (8), wird im Prinzip eine doppelte Abscheideleistung von Schadstoffen mit a) großer Verfügbarkeit und b) hoher Abscheideleistung erzielt.By transferring it to the spray tower, by mixing it up via the mixer (8), there is in principle a double separation efficiency of pollutants with a) large Availability and b) high separation efficiency achieved.
Versuche haben gezeigt, daß Abscheideraten bis zu 99 % erzielt werden können.Tests have shown that separation rates of up to 99% can be achieved can.
Patentanspruch: LeerseiteClaim: Blank page
Claims (1)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE19823235020 DE3235020A1 (en) | 1982-09-22 | 1982-09-22 | Chemisorption process for absorbing preferably sulphur dioxide downstream of power stations, refuse incineration plants and the like |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE19823235020 DE3235020A1 (en) | 1982-09-22 | 1982-09-22 | Chemisorption process for absorbing preferably sulphur dioxide downstream of power stations, refuse incineration plants and the like |
Publications (2)
Publication Number | Publication Date |
---|---|
DE3235020A1 true DE3235020A1 (en) | 1984-03-22 |
DE3235020C2 DE3235020C2 (en) | 1991-10-02 |
Family
ID=6173820
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
DE19823235020 Granted DE3235020A1 (en) | 1982-09-22 | 1982-09-22 | Chemisorption process for absorbing preferably sulphur dioxide downstream of power stations, refuse incineration plants and the like |
Country Status (1)
Country | Link |
---|---|
DE (1) | DE3235020A1 (en) |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0217733A1 (en) * | 1985-09-30 | 1987-04-08 | Mitsubishi Jukogyo Kabushiki Kaisha | Process for the systematic treatment of exhaust gases |
EP0226863A1 (en) * | 1985-11-29 | 1987-07-01 | General Electric Company | Method for scrubbing sulfur oxides and nitrogen oxides in a flue gas duct |
EP0253563A1 (en) * | 1986-07-16 | 1988-01-20 | Niro A/S | A process for removal of mercury vapor and/or vapor of noxious organic compounds and/or nitrogen oxides from flue gas from an incinerator plant |
EP0268353A1 (en) * | 1986-11-19 | 1988-05-25 | The Babcock & Wilcox Company | Controlling emission of pollutants from coal-fired boiler systems |
EP0273508A1 (en) * | 1986-12-23 | 1988-07-06 | Metallgesellschaft Ag | Waste gas purification process |
CN111603923A (en) * | 2020-05-22 | 2020-09-01 | 朱文艳 | Tertiary tail gas cleanup tower of high concentration nitrogen oxide |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE3610408A1 (en) * | 1986-03-27 | 1987-10-01 | Hoelter Heinz | Two-stage semi-dry desulphurisation process |
DE4419669A1 (en) * | 1994-06-07 | 1995-12-14 | Krc Umwelttechnik Gmbh | Process for the separation of very fine particles from exhaust gases from wet combustion plants desulphurized with limestone |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
AT212290B (en) * | 1956-09-12 | 1960-12-12 | Wheelabrator Corp | Method and device for removing gaseous halides, in particular fluorides, from gaseous systems |
GB1429427A (en) * | 1974-07-25 | 1976-03-24 | Asahi Fibreglass Co | Method of cleaning waste gases containing a fluorine component |
DE2625280A1 (en) * | 1975-06-06 | 1976-12-16 | Us Energy | METHOD FOR LIMITING SULFUR DIOXIDE EMISSIONS |
DE2615828A1 (en) * | 1976-04-10 | 1977-10-13 | Heinz Hoelter | Gas purificn. by addn. of absorbent - in series of stages with sepn. and recycling of absorbent after each stage |
-
1982
- 1982-09-22 DE DE19823235020 patent/DE3235020A1/en active Granted
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
AT212290B (en) * | 1956-09-12 | 1960-12-12 | Wheelabrator Corp | Method and device for removing gaseous halides, in particular fluorides, from gaseous systems |
GB1429427A (en) * | 1974-07-25 | 1976-03-24 | Asahi Fibreglass Co | Method of cleaning waste gases containing a fluorine component |
DE2625280A1 (en) * | 1975-06-06 | 1976-12-16 | Us Energy | METHOD FOR LIMITING SULFUR DIOXIDE EMISSIONS |
DE2615828A1 (en) * | 1976-04-10 | 1977-10-13 | Heinz Hoelter | Gas purificn. by addn. of absorbent - in series of stages with sepn. and recycling of absorbent after each stage |
Non-Patent Citations (3)
Title |
---|
Forschungsbericht des Landes Nordrhein-Westfalen, Nr. 2907/Fachgruppe Umwelt/Verkehr, Dipl.-Ing. Paul Gerhard Schuch "Trockensorption von Chlorwasserstoff, Fluorwasserstoff und Schwefeldioxid aus Rauchgasen in einer halb- technischen Versuchsanlage", Westdeutscher Verlag,1980, S. 11-13, insbes. Abb. 5 auf S. 12 * |
Gas Wärme International, 28, 4, 1979, S. 173-183 * |
Staub Reinhaltung Luft 40, 7, 1980 * |
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0217733A1 (en) * | 1985-09-30 | 1987-04-08 | Mitsubishi Jukogyo Kabushiki Kaisha | Process for the systematic treatment of exhaust gases |
EP0226863A1 (en) * | 1985-11-29 | 1987-07-01 | General Electric Company | Method for scrubbing sulfur oxides and nitrogen oxides in a flue gas duct |
EP0253563A1 (en) * | 1986-07-16 | 1988-01-20 | Niro A/S | A process for removal of mercury vapor and/or vapor of noxious organic compounds and/or nitrogen oxides from flue gas from an incinerator plant |
US4889698A (en) * | 1986-07-16 | 1989-12-26 | A/S Niro Atomizer | Process for removal or mercury vapor and/or vapor of noxious organic compounds and/or nitrogen oxides from flue gas from an incinerator plant |
EP0268353A1 (en) * | 1986-11-19 | 1988-05-25 | The Babcock & Wilcox Company | Controlling emission of pollutants from coal-fired boiler systems |
EP0468540A1 (en) * | 1986-11-19 | 1992-01-29 | The Babcock & Wilcox Company | Controlling emission of pollutants from coal-fired boiler systems |
EP0273508A1 (en) * | 1986-12-23 | 1988-07-06 | Metallgesellschaft Ag | Waste gas purification process |
US4908195A (en) * | 1986-12-23 | 1990-03-13 | Metallgesellschaft Aktiengesellschaft | Process of purifying exhaust gas |
CN111603923A (en) * | 2020-05-22 | 2020-09-01 | 朱文艳 | Tertiary tail gas cleanup tower of high concentration nitrogen oxide |
Also Published As
Publication number | Publication date |
---|---|
DE3235020C2 (en) | 1991-10-02 |
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Legal Events
Date | Code | Title | Description |
---|---|---|---|
OM8 | Search report available as to paragraph 43 lit. 1 sentence 1 patent law | ||
OP8 | Request for examination as to paragraph 44 patent law | ||
D2 | Grant after examination | ||
8363 | Opposition against the patent | ||
8366 | Restricted maintained after opposition proceedings | ||
8305 | Restricted maintenance of patent after opposition | ||
D4 | Patent maintained restricted | ||
8339 | Ceased/non-payment of the annual fee |