DK165736B - PROCEDURE FOR THE REMOVAL OF HARMFUL MATERIALS FROM COGAS - Google Patents
PROCEDURE FOR THE REMOVAL OF HARMFUL MATERIALS FROM COGAS Download PDFInfo
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- DK165736B DK165736B DK606386A DK606386A DK165736B DK 165736 B DK165736 B DK 165736B DK 606386 A DK606386 A DK 606386A DK 606386 A DK606386 A DK 606386A DK 165736 B DK165736 B DK 165736B
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- process according
- solid
- flue gases
- cement
- adsorbent
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- 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
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- General Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Biomedical Technology (AREA)
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- Health & Medical Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Treating Waste Gases (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Gas Separation By Absorption (AREA)
- Processing Of Solid Wastes (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
- Curing Cements, Concrete, And Artificial Stone (AREA)
Abstract
Description
iin
DK 165736BDK 165736B
oisland
Den foreliggende opfindelse angår en fremgangsmåde til tør fjernelse af skadelige stoffer fra røggasserne fra brændingsprocesser i silikatindustrien, navnlig ved cementfremstilling. For at tilfredsstille gælden-5 de miljøbestemmelser bliver i stigende grad også anlæg i silikatindustrien udstyret med indretninger til fraskil-lelse af skadelige gasser.The present invention relates to a process for the dry removal of noxious substances from the flue gases from combustion processes in the silicate industry, especially in cement production. In order to satisfy the debt environmental regulations, plants in the silicate industry are increasingly equipped with devices for separating harmful gases.
Ved den kendte vådrensningsfremgangsmåde bliver røggasserne sædvanligvis efter en støvfjernelse behandlet 10 med en i kredsløb ledet vaskevæske og derved afkølet så meget, at en genopvarmning til ca. 20°C over dugpunktet bliver nødvendig for at undgå korrosionsskader. Den fremkomne mængde af reaktionsprodukter er i regelen også for stor til, at den i sin helhed kan tilbageføres til frem-15 stillingsprocessen. Vådrensningsfremgangsmåder er derfor for det meste forbundet med store anlægs- og driftsomkostninger, der ofte modvirker en konsekvent realisering af røggasrensningen.In the known wet cleaning process, after a dust removal, the flue gases are usually treated with a circulating wash liquid and cooled so much that a reheat to approx. 20 ° C above the dew point becomes necessary to avoid corrosion damage. The resulting amount of reaction products is also generally too large for it to be returned in its entirety to the manufacturing process. Wet cleaning procedures are therefore usually associated with large construction and operating costs, often counteracting a consistent realization of the flue gas cleaning.
Ved fremstillingen af cement har man også alle-20 rede forsøgt at rerse røggasserne tørt ved 300 til S30°C. Herved har det imidlertid vist sig, at røggasserne ved temperaturer over 500°C hyppigt indeholder mindre end 100 mg/Nin af det her principalt skadelige stof SC^, mens den største del af det med brændslet i cementfremstillings-25 processen indførte svovl i dette temperaturområde adsor-beres af råmelet og bindes i klinkerne.In the manufacture of cement, attempts have also already been made to stir the flue gases dry at 300 to S30 ° C. Hereby, however, it has been found that at temperatures above 500 ° C, the flue gases frequently contain less than 100 mg / Nin of the principally harmful substance SC 2, while most of the sulfur introduced into the temperature range by the fuel in the cement-making process adsorbed by the raw flour and bound in the clinker.
Sådanne gunstige forhold foreligger ikke ved andre brændingsprocesser i silikatindustrien. Dér må der ydermere ved siden af brændselssvovlet overvejende fjer-30 nes andre skadelige stoffer såsom chlorider og fluorider fra røggassen, uden at det egentlige produkt udviser en nævneværdig adsorptionsevne for de skadelige stoffer.Such favorable conditions do not exist in other firing processes in the silicate industry. There, besides the fuel sulfur, other harmful substances such as chlorides and fluorides must be removed from the flue gas without the actual product exhibiting a significant adsorption capacity for the harmful substances.
Ved cementfremstillingsprocessen bliver svovl imidlertid også indført i forbrændingsprocessen gennem råmelet. Dette svovl stammer tildels fra organiske eller sulfidiske svovlforbindelser, der allerede nedbrydes vedIn the cement-making process, however, sulfur is also introduced into the combustion process through the raw flour. This sulfur is partly derived from organic or sulphidic sulfur compounds which are already decomposed by
DK 165736 BDK 165736 B
2 lave temperaturer og fører til frigivelse af S02 under forvamningen af råmelet, hvorved der kan optræde S0-- 3 ^ -indhold på indtil 6000 mg/Nm . Da der ved de i cementprocessen sædvanlige røggastemperaturer praktisk talt 5 ikke sker nogen adsorption af S02 ved hjælp af råmaterialet, må der også til cementfremstillingslæg være tilvejebragt en røggasafsvovlingsindretning, selv om det med brændslet indførte svovl betinget af fremgangsmåden kun for en ringe del er indeholdt i røggassen.2 low temperatures and leads to the release of SO2 during the pre-steaming of the raw flour, whereby SO3 content of up to 6000 mg / Nm can occur. Since, at the usual flue gas temperatures in the cement process, practically no adsorption of SO2 by the feedstock is effected, a flue gas desulphurisation device must also be provided, although the sulfur introduced sulfur is subject to the process only for a minor part. flue gas.
10 En tørrensning ved temperaturer fra 200 til 400°C10 Dry cleaning at temperatures of 200 to 400 ° C
er, uafhængigt af det anvendte adsorptionsmiddel og uafhængigt af forholdet mellem adsorptionsmiddel og skadelige stoffer, imidlertid ikke særlig virksom. I almindelighed kan kun mindre end 60% af de skadelige stoffer fjer-15 nes fra røggassen, hvis man ikke vil gå over til dyre og på grund af den oftest store støvmængde kun betinget driftssikre rensningsfremgangsmåder med katalysatorer.however, independent of the adsorbent used and independent of the ratio of adsorbent to harmful substances, is not very effective. In general, only less than 60% of the harmful substances can be removed from the flue gas if one does not want to switch to expensive and, because of the usually large amount of dust, only conditional reliable cleaning processes with catalysts.
Der foreligger således det formål at foreslå en fremgangsmåde til fjernelse af skadelige stoffer fra røg-20 gasserne fra brændingsprccesser i silikatindustrier., som er almindeligt anvendelig og mere økonomisk end de kendte fremgangsmåder.Thus, the object is to propose a method for removing harmful substances from the flue gases from firing processes in silicate industries, which are generally applicable and more economical than the known methods.
Fremgangsmåden ifølge opfindelsen er ejendommelig ved, at røggasserne i et af en hvirvellagsreaktor, 25 en faststoffraskiller og en tilbageføringsledning dannet faststofcirkulationssystem ved 50 til 100°C bringes i kontakt med et adsorptionsmiddel i form af faststofpartikler, og når det fremkomne produkt fuldstændigt eller næsten fuldstændigt tilføres en cementfremstillingsproces.The process according to the invention is characterized in that the flue gases in a solid circulation system formed by a vortex reactor, a solid separator and a return line formed at 50 to 100 ° C are contacted with an adsorbent in the form of solid particles and when the resulting product is supplied completely or almost completely. a cement-making process.
30 Med fremgangsmåden ifølge opfindelsen kan ikke blot den ved andre tørrensningsfremgangsmåder med lavt temperaturområde hyppigt for korte kontakttid forøges vilkårligt, men der tilvejebringes også et produkt, der ikke kræver nogen særlig forarbejdning eller deponering, hvor-35 med økonomien af de sædvanlige fremgangsmåder ofte er meget belastet.With the process of the invention, not only can it be arbitrarily increased arbitrarily in other low-temperature drying processes frequently for short contact time, but also a product which requires no special processing or deposition, which, with the economics of the usual methods, is often very congested.
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3 Røggasserne har før indstrømning i faststofcirkulationssystemet fortrinsvis en temperatur på fra 50 til 100°C. Såfremt dette ikke er muligt, kan røggasserne også køles til 50 til 100°C i hvirvellagsreaktoren ved 5 indsprøjtning af vand. Da der i anlæg til brænding af silikatprodukter sædvanligvis findes en slutstøvfraskiller, kan denne anvendes som faststoffraskiller i faststofcirkulationssystemet.3 The flue gases preferably have a temperature of from 50 to 100 ° C prior to flow into the solid-state circulation system. If this is not possible, the flue gases can also be cooled to 50 to 100 ° C in the vortex reactor by injection of water. Since in silica burning systems, there is usually a final dust separator, it can be used as a solid separator in the solid circulation system.
Hovedfordelen ved fremgangsmåden ifølge opfindel-10 sen består i, at der som adsorptionsmiddel anvendes til fremstilling af cement brugte materialer såsom råmel, kalksten med mere end 90% CaCOg, brændt kalk, kalkhydrat eller delvis kalcineret råmel, som derefter igen kan tilføres til en cementfremstillingsproces.The main advantage of the process according to the invention consists in the use of adsorbents used in the manufacture of cement materials such as raw flour, limestone with more than 90% CaCOg, burnt lime, lime hydrate or partially calcined raw flour, which can then be added again to a cement-making process. .
15 Endelig foretrækkes det også, at temperaturen i hvirvellagsreaktoren reguleres til en optimal værdi, og adsorptionsmiddeltilsætningen reguleres i afhængighed af indholdet af skadelige stoffer i den rensede gas.Finally, it is also preferred that the temperature of the fluidized bed reactor is controlled to an optimum value and the adsorbent addition is adjusted depending on the content of harmful substances in the purified gas.
Opfindelsen skal i det følgende beskrives nær-20 mere ud fra afsvovling af røggasser fra en cementfremstillingsproces, idet der henvises til tegningen, hvor fig. 1 viser et forenklet gengivet fremgangsmådestrømbil-lede.BRIEF DESCRIPTION OF THE DRAWINGS The invention will now be described in more detail with reference to the desulfurization of flue gases from a cement-making process, with reference to the drawing, in which fig. 1 shows a simplified reproduced process flow image.
Det af en hvirvellagsreaktor 1, en faststof-25 fraskiller 2 og en tilbageføringsledning 3 bestående faststofcirkulationssystem tilføres via en ledning 4 forstøvningsvand, via en ledning 5 adsorptionsmiddel og via en ledning 6 den røggas, som skal afsvovles. Den i vidt omfang afsvovlede røggas forlader hvirvellagsreaktoren 1 30 foroven, befries i faststoffraskilleren 2 for støv og kommer via en blæser 8 og en ledning 9 til skorstenen.The solids circulation system of a fluidized bed reactor 1, a solid separator 2 and a return line 3 is supplied via a conduit 4 atomizing water, via a conduit 5 adsorbent and via a conduit 6 the flue gas to be desulfurized. The largely desulfurized flue gas leaves the vortex reactor 1 30 at the top, is freed from the solid dust separator 2 for dust and comes to the chimney via a blower 8 and a conduit 9.
Under faststoffraskilleren 2 er anbragt en transportindretning, med hvilken det fraskilte støv transporteres til tilbageføringsledningen 3 og sluttelig igen afgives i hvirvellagsreaktoren 1. En delmængde af de cirkulerende faststofpartikler udsluses via en ledning 7 fra fast-Underneath the solid separator 2 is arranged a transport device by which the separated dust is transported to the return line 3 and finally again discharged into the fluidised-bed reactor 1. A subset of the circulating solid particles is discharged via a conduit 7 from the solid.
DK 165736BDK 165736B
44
OISLAND
stofcirkulationssystemet og tilføres på et egnet sted cementfremstillingsprocessen.the fabric circulation system and is applied to the cement manufacturing process at a suitable location.
Enkelte i faststoffet indeholdte komponenter, f.eks. tungmetaller, kan efter selektiv fraskillelse ud-5 føres adskilt fra de øvrige stoffer via en ledning 10.Some components contained in the solid, e.g. heavy metals, after selective separation can be carried out separately from the other substances via a conduit 10.
Røggasserne forekommer, alt efter om og hvilke varmegenvindingsindretninger (spildvarmekedel, varmt-vandstilberedning, mølle) der er tilvejebragt, med en temperatur på fra 100 til 450°C. Deres støvindhold andrager 10 indtil 100 g/Nm^, når de ikke ledes over en mølle. I sidstnævnte tilfælde kan støvbelastningen andrage indtil 1000 g/Nm , og en forudgående støvfjernelse ved hjælp af elek-trofilter eller mekanisk fraskiller kan være hensigtsmæssig for at kunne begrænse faststofcirkulationen i fast-15 stofcirkulationssystemet til den for afsvovling optimale mængde. Eventuelt kan der i sådanne tilfælde ses helt eller delvis bort fra den særskilte tilsætning af adsorptionsmidler. Støvindholdet i røggassen reduceres i fast-stoffraskilleren til mindre end 50 mg/Nm^.The flue gases occur, depending on whether and which heat recovery devices (waste heat boiler, hot water preparation, mill) are provided, with a temperature of from 100 to 450 ° C. Their dust content is 10 to 100 g / Nm 2 when not passed over a mill. In the latter case, the dust load may be up to 1000 g / Nm, and a prior dust removal by means of an electro-filter or mechanical separator may be appropriate in order to limit the solids circulation in the solids circulation system to the optimum amount of desulphurisation. Optionally, in such cases, the separate addition of adsorbents may be disregarded. The dust content of the flue gas is reduced in the solid separator to less than 50 mg / Nm 2.
23 SO^-indhcldet i røggassen andrager alt efter rå- , “ o materialesammensætningen indtil 6000 mg/Nm . Det kan med fremgangsmåden ifølge opfindelsen sænkes til en værdi mindre end 50 mg/Nm^ i den rensede gas. De efter de lovmæssige forskrifter tilladelige mængder af SO~ ligger 3 ^ 25 for tiden i Tyskland på 400 mg/Nm og i Schweiz på 500 3 mg/Nm .The content of SO 2 in the flue gas varies according to the raw material composition up to 6000 mg / Nm. It can be lowered to a value less than 50 mg / Nm 2 in the purified gas by the process of the invention. The permissible levels of SO ~ are currently 3 400 in Germany at 400 mg / Nm and in Switzerland at 500 3 mg / Nm.
En yderligere fordel ved fremgangsmåden består i, at der til forbedring af økonomien i brændingsprocesserne også kan anvendes sådanne brændsler, som indehol-30 der tungmetaller inklusive skadelige stoffer af klasse I såsom cadmium, thallium, kviksølv og lignende metaller.A further advantage of the method is that, in order to improve the economy of the burning processes, such fuels containing heavy metals including harmful Class I substances such as cadmium, thallium, mercury and similar metals can also be used.
Disse skadelige stoffer bindes i hvirvellagsreaktoren overvejende til de særlig finkornede faststofpartikler og kan i en klasserende arbejdende faststoffraskiller, 35 f.eks. et flerefeltselektrofilter, fraskilles næsten fuldstændig adskilt fra de øvrige reststoffer og udsluses u-These harmful substances are predominantly bonded in the fluidized-bed reactor to the particularly fine-grained solid particles and can, in a classy working solid separator, e.g. a multi-field electrofilter, is separated almost completely from the other residues and is excreted un-
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afhængigt af de til en cementfremstillingsproces tilbageførte reaktionsprodukter.depending on the reaction products returned to a cement manufacturing process.
De på denne måde udslusede faststofpartikler har på den ene side en høj koncentration af skadelige stof-5 fer men udgør på den anden side kun en ringe mængde af de totalt forekommende reaktionsprodukter. De kan, for så vidt det ikke er skadeligt for produktet af den pågældende brændingsproces, tilbageføres til et egnet sted i produktfremstillingsprocessen, hvor de selv bindes sta-10 bilt og vanduopløseligt. Ved cementfremstillingen frem-byder det sig at iblande dem ved klinker- eller cementformalingen. Eventuelt kommer også en behandling med henblik på genvinding af de skadelige stoffer i metallisk eller anden anvendelig form i betragtning. Med frem-15 gangsmåden ifølge opfindelsen kan 90% af de nævnte skadelige stoffer fraskilles fra røggassen og bortskaffes miljøvenligt.The solid particles thus extinguished have, on the one hand, a high concentration of noxious substances, but on the other hand constitute only a small amount of the total reaction products. They may, to the detriment of the product of the burning process in question, be returned to a suitable location in the product-making process where they themselves are bonded rigidly and water-insoluble. In the cement manufacture, it appears to mix them in the clinker or cement grinding. Optionally, a treatment for the recovery of the harmful substances in metallic or other useful form is also considered. By the method of the invention, 90% of the said harmful substances can be separated from the flue gas and disposed of in an environmentally friendly manner.
Fremgangsmåden ifølge opfindelsen blev forsøgsvis anvendt ved et cementfremstillingsanlæg. Sulfitind-20 holdet i råmaterialet androg 0,3 til 0,4% i forhold til vægten af råmaterialet, hvorved SO^-indholdet i den un-dersøgte røggasdelstrøm måltes til indtil 3600 mg/'Nm , når fremgangsmåder, ifølge opfindelsen ikke blev benyttet. Ved anvendelse af fremgangsmåden kunne SO,-indhol-25 det sænkes til værdier klart under 400 mg/Nm . Som adsorptionsmiddel anvendtes herved råmel, til hvilket der var iblandet kalkmel i en sådan mængde, at ca. 50% af det støkiometrisk nødvendige kalciumbehov hermed blev dækket.The process of the invention was experimentally used in a cement manufacturing plant. The sulphite content of the feedstock was 0.3 to 0.4% relative to the weight of the feedstock, whereby the SO . Using the process, the SO 2 content could be lowered to values clearly below 400 mg / Nm. As the adsorbent, crude flour to which there was mixed lime flour in an amount such that approx. 50% of the stoichiometric required calcium was thereby met.
30 3530 35
Claims (7)
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE3544764 | 1985-12-18 | ||
DE19853544764 DE3544764A1 (en) | 1985-12-18 | 1985-12-18 | METHOD FOR REMOVING POLLUTANTS FROM EXHAUST GAS |
Publications (4)
Publication Number | Publication Date |
---|---|
DK606386D0 DK606386D0 (en) | 1986-12-16 |
DK606386A DK606386A (en) | 1987-06-19 |
DK165736B true DK165736B (en) | 1993-01-11 |
DK165736C DK165736C (en) | 1993-06-14 |
Family
ID=6288750
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
DK606386A DK165736C (en) | 1985-12-18 | 1986-12-16 | PROCEDURE FOR THE REMOVAL OF HARMFUL MATERIALS FROM COGAS |
Country Status (11)
Country | Link |
---|---|
EP (1) | EP0228111B2 (en) |
JP (1) | JPH0753224B2 (en) |
AT (1) | ATE46088T1 (en) |
CA (1) | CA1284802C (en) |
CZ (1) | CZ280413B6 (en) |
DD (1) | DD252767A5 (en) |
DE (2) | DE3544764A1 (en) |
DK (1) | DK165736C (en) |
ES (1) | ES2011251T5 (en) |
HU (1) | HU200706B (en) |
SK (1) | SK278406B6 (en) |
Families Citing this family (14)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2624399B1 (en) * | 1987-12-14 | 1992-01-24 | Champagnole Ciments | PROCESS FOR DECONTAMINATION OF HOT GASES OR FUMES EMITTED BY A FIREPLACE, INSTALLATION FOR ITS IMPLEMENTATION AND PRODUCT OBTAINED |
DE3824880A1 (en) * | 1988-07-19 | 1990-01-25 | Noell Gmbh | METHOD AND DEVICE FOR TREATING GASES |
AT394660B (en) * | 1989-07-28 | 1992-05-25 | Staudinger Gernot | METHOD FOR REMOVAL OR REDUCTION OF GASEOUS POLLUTANTS AND DEVICE FOR CARRYING OUT THIS PROCESS |
DE3942092A1 (en) * | 1989-12-20 | 1991-06-27 | Metallgesellschaft Ag | METHOD FOR REDUCING NO (ARROW DOWN) X (ARROW DOWN) CONTENT IN EXHAUST GAS |
DE4000795A1 (en) * | 1990-01-12 | 1991-07-18 | Krupp Polysius Ag | METHOD FOR PURIFYING THE EXHAUST GASES FROM PLANTS FOR PRODUCING CEMENT CLINKER |
DE4018786A1 (en) * | 1990-06-12 | 1991-12-19 | Krupp Polysius Ag | METHOD FOR PURIFYING THE EXHAUST GASES FROM PLANTS FOR PRODUCING CEMENT CLINKER |
DE4034498A1 (en) * | 1990-09-06 | 1992-03-12 | Metallgesellschaft Ag | METHOD FOR SEPARATING HEAVY METALS AND DIOXINES FROM COMBUSTION EXHAUST GASES |
DE4206602C2 (en) * | 1992-03-03 | 1995-10-26 | Metallgesellschaft Ag | Process for removing pollutants from combustion exhaust gases and fluidized bed reactor therefor |
DE4330593A1 (en) * | 1993-09-09 | 1995-03-16 | Krupp Polysius Ag | Process for cleaning flue gases |
DE4401166A1 (en) * | 1994-01-17 | 1995-07-20 | Krupp Polysius Ag | Process for cleaning flue gases |
DE19532862A1 (en) * | 1995-09-06 | 1997-03-13 | Graf Epe Gmbh | Plant cleaning waste gases by solids contacting in recirculated fluidised bed |
CZ20014584A3 (en) * | 1999-06-18 | 2002-04-17 | F. L. Smidth & Co A/S | Desulfurizing process of exhaust gases and apparatus for making the same |
US7390357B2 (en) * | 2002-10-02 | 2008-06-24 | F.L.Smidth A/S | Method and plant for manufacturing cement clinker |
KR101015154B1 (en) * | 2010-10-05 | 2011-02-16 | 한국에너지기술연구원 | Internal and external circulating acid gas removal device for high temperature flue gas powder absorber containing sulfur oxide and boron compound and acid gas removal method using the same |
Family Cites Families (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE3038457C2 (en) * | 1980-10-11 | 1983-11-10 | L. & C. Steinmüller GmbH, 5270 Gummersbach | Use of a waste product from dry flue gas desulphurisation for the production of fly ash cement |
DE3215793A1 (en) * | 1982-04-28 | 1983-11-03 | Klöckner-Humboldt-Deutz AG, 5000 Köln | METHOD AND DEVICE FOR REDUCING THE SULFURING CIRCUIT AND / OR THE SO (ARROW DOWN) 2 (ARROW DOWN) EMISSION IN A PLANT FOR BURNING FINE GRAIN GOODS |
DE3235558A1 (en) * | 1982-09-25 | 1984-03-29 | Metallgesellschaft Ag, 6000 Frankfurt | METHOD FOR SEPARATING POLLUTANTS FROM EXHAUST GAS |
DE3235559A1 (en) * | 1982-09-25 | 1984-05-24 | Metallgesellschaft Ag, 6000 Frankfurt | Process for the removal of sulphur oxides from flue gas |
DE3322159A1 (en) * | 1983-06-21 | 1985-01-03 | Metallgesellschaft Ag, 6000 Frankfurt | METHOD FOR SEPARATING POLLUTANTS FROM EXHAUST GAS |
DE3326935A1 (en) * | 1983-07-26 | 1985-02-07 | Krupp Polysius Ag, 4720 Beckum | Process for the elimination of pollutants from the exhaust gases of a rotary kiln |
DK348583D0 (en) * | 1983-07-29 | 1983-07-29 | Smidth & Co As F L | METHOD AND APPARATUS FOR REMOVAL OF SULFUR OXIDES FROM HOT ROEGGAS BY THE TOUR METHOD |
DE3415210C2 (en) * | 1984-01-07 | 1995-06-22 | Kloeckner Humboldt Deutz Ag | Process for the desulfurization of the flue gas from a furnace |
-
1985
- 1985-12-18 DE DE19853544764 patent/DE3544764A1/en not_active Withdrawn
-
1986
- 1986-11-27 EP EP86202110A patent/EP0228111B2/en not_active Expired - Lifetime
- 1986-11-27 DE DE8686202110T patent/DE3665410D1/en not_active Expired
- 1986-11-27 ES ES86202110T patent/ES2011251T5/en not_active Expired - Lifetime
- 1986-11-27 AT AT86202110T patent/ATE46088T1/en active
- 1986-12-10 CZ CS869150A patent/CZ280413B6/en unknown
- 1986-12-10 SK SK9150-86A patent/SK278406B6/en unknown
- 1986-12-11 JP JP61295702A patent/JPH0753224B2/en not_active Expired - Lifetime
- 1986-12-16 DD DD86297685A patent/DD252767A5/en not_active IP Right Cessation
- 1986-12-16 DK DK606386A patent/DK165736C/en not_active IP Right Cessation
- 1986-12-17 HU HU865268A patent/HU200706B/en not_active IP Right Cessation
- 1986-12-17 CA CA000525587A patent/CA1284802C/en not_active Expired - Lifetime
Also Published As
Publication number | Publication date |
---|---|
DE3665410D1 (en) | 1989-10-12 |
CA1284802C (en) | 1991-06-11 |
ATE46088T1 (en) | 1989-09-15 |
EP0228111B1 (en) | 1989-09-06 |
JPH0753224B2 (en) | 1995-06-07 |
DK606386A (en) | 1987-06-19 |
ES2011251B3 (en) | 1990-01-01 |
CZ915086A3 (en) | 1995-11-15 |
JPS62144736A (en) | 1987-06-27 |
SK915086A3 (en) | 1997-04-09 |
EP0228111B2 (en) | 1994-06-15 |
DE3544764A1 (en) | 1987-06-19 |
SK278406B6 (en) | 1997-04-09 |
CZ280413B6 (en) | 1996-01-17 |
DD252767A5 (en) | 1987-12-30 |
DK606386D0 (en) | 1986-12-16 |
ES2011251T5 (en) | 1995-08-16 |
EP0228111A1 (en) | 1987-07-08 |
HU200706B (en) | 1990-08-28 |
HUT49057A (en) | 1989-08-28 |
DK165736C (en) | 1993-06-14 |
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