DK154008B - PROCEDURE FOR CLEANING HOT ROEGGAS FOR SULFUR DIOXIDE OR OTHER UNWANTED ACID GAS COMPONENTS FROM HOT ROEGGAS AND APPARATUS FOR EXERCISING THE PROCEDURE - Google Patents

PROCEDURE FOR CLEANING HOT ROEGGAS FOR SULFUR DIOXIDE OR OTHER UNWANTED ACID GAS COMPONENTS FROM HOT ROEGGAS AND APPARATUS FOR EXERCISING THE PROCEDURE Download PDF

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DK154008B
DK154008B DK442780A DK442780A DK154008B DK 154008 B DK154008 B DK 154008B DK 442780 A DK442780 A DK 442780A DK 442780 A DK442780 A DK 442780A DK 154008 B DK154008 B DK 154008B
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filter
chamber
flue gas
absorbent
sulfur dioxide
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DK442780A
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DK442780A (en
DK154008C (en
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Stefan Aahman
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Flaekt Ab
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    • 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
    • B01D53/507Sulfur oxides by treating the gases with other liquids

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  • 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)

Description

iin

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Den foreliggende opfindelse angår en fremgangsmåde til rensning af varm røggas for svovldioxid eller andre uønskede sure gaskomponenter, ved hvilken en absorbent i 5 form af en vandig opløsning eller vandig suspension bringes i kontakt med røggassen under tørring af reaktionsprodukterne, som dannes af absorbenten og svovldioxiden, hvorpå reaktionsprodukterne udskilles i et tekstilspærrefilter, samt et apparat til udøvelse af 10 fremgangsmåden.The present invention relates to a process for the purification of hot flue gas from sulfur dioxide or other undesirable acidic gas components, in which an absorbent in the form of an aqueous solution or aqueous suspension is contacted with the flue gas while drying the reaction products formed by the absorbent and sulfur dioxide. whereupon the reaction products are separated into a textile barrier filter, and an apparatus for carrying out the method.

Der kendes adskillige fremgangsmåder til at fjerne svovldioxid fra røggas fra kulfyrede kraftværker. De mest almindelige fremgangsmåder er baseret på vådrensning med kalk eller kalksten som absorptionsmiddel. Gasvaskeren 15 udformes da sædvanligvis som et tårn med dyser, i hvilket der recirkuleres store mængder absorptionsvæske. Denne fremstilles af findelt kalk eller kalksten, som med absorberet svovldioxid danner reaktionsprodukter i form af calciumsulfit og -sulfat. Disse forbindelser er relativt 20 tungtopløselige, og vaskevæsken forbliver derfor rig på faste partikler, selv om størsteparten af kalken udnyttes til reaktion med absorberet SO2· Risikoen for tilstopning af apparaturet med disse forbindelser foreligger derfor altid, selv om der i de senere år er gjort betydelige 25 fremskridt med hensyn til at eliminere bl.a. dette problem ved vådskrubning med kalk. Effektforbruget ligger også relativt højt, da der skal transporteres store væskemængder. Væsken, dvs. opslæmningen, indeholder desuden slidende faste partikler, som bevirker væsentlige ved-30 ligeholdelsesomkostninger til f.eks. pumper, rørledninger og dyser. I gasvaskeren afkøles gassen omtrent til mætningstemperaturen - eller ca. 50-55°C - hvilket bevirker, at der ofte må foretages genopvarmning af gassen for at undgå generende nedslag af røggas i nærheden af 35 skorstenen.Several methods are known for removing sulfur dioxide from flue gas from coal-fired power plants. The most common methods are based on wet cleaning with lime or limestone as absorbent. The gas washer 15 is then usually designed as a tower with nozzles in which large quantities of absorbent liquid are recycled. This is made of finely divided limestone or limestone which, with absorbed sulfur dioxide, forms reaction products in the form of calcium sulphite and sulphate. These compounds are relatively heavily soluble and therefore the washing liquid remains rich in solid particles, although most of the lime is utilized for reaction with absorbed SO2 · Therefore, the risk of clogging the apparatus with these compounds is always present, although in recent years considerable 25 progress in eliminating, inter alia, this problem with wet scrubbing with lime. Power consumption is also relatively high, since large volumes of liquid are to be transported. The liquid, ie. the slurry additionally contains abrasive solid particles which cause substantial maintenance costs to e.g. pumps, pipelines and nozzles. In the gas washer, the gas is cooled approximately to saturation temperature - or approx. 50-55 ° C - which means that the gas often needs to be reheated to avoid annoying flue gas near the chimney.

En alternativ fremgangsmåde til dette helt våde system bevirker betydelig forenkling og giver væsentlige fordeleAn alternative approach to this completely wet system significantly simplifies and offers significant benefits

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2 i forhold dertil. Ved dette alternativ udnyttes røggassens varme til fuldstændig fordampning af vandet i absorptionsvæsken samtidig med at reaktionsprodukterne tørres til et 5 tørt pulver, som derefter udskilles sammen med indgående stof, f.eks. flyveaske, efter den kombinerede tørrings- og absorptionsfremgangsmåde. Absorptionsmidlet indsprøjtes under findeling i en dyse eller en roterende atomiseringsenhed i det første trin, som består af et særskilt reak-10 tionskammer, som er helt adskilt fra stofudskilleren, som udgør det andet trin. Som stofudskiliere anvendes såvel tekstilfiltre som elektrofiltre af konventionelle typer.2 in relation thereto. In this alternative, the heat of the flue gas is utilized to completely evaporate the water in the absorption liquid while drying the reaction products to a dry powder which is then separated together with the incoming substance, e.g. fly ash, following the combined drying and absorption process. The absorbent is injected during comminution into a nozzle or rotary atomizer in the first stage which consists of a separate reaction chamber which is completely separate from the substance separator constituting the second stage. As fabric separators, both textile filters and electro filters of conventional types are used.

Fremgangsmåden ifølge opfindelsen er ejendommelig ved, at absorbenten indføres i et filterkammer i finfordelt form 15 og blandes med den til filterkammeret tilførte røggas-strøm, og at blandingen bibringes en opholdstid i filterkammeret på mellem 1 og 15 sekunder under tilnærmelsesvis fuldstændig overfladefordampning hos reaktionsprodukterne, hvorefter røggasstrømmen føres 20 igennem filtermaterialet i det i filterkammeret anbragte filter under afsætning af de dannede reaktionsprodukter på filtermaterialet.The process of the invention is characterized in that the absorbent is introduced into a filter chamber in finely divided form 15 and mixed with the flue gas stream supplied to the filter chamber, and the mixture is imparted for a residence time in the filter chamber of between 1 and 15 seconds during approximately complete surface evaporation of the reaction products. the flue gas stream is passed through the filter material in the filter placed in the filter chamber during deposition of the reaction products formed on the filter material.

Fremgangsmåden ifølge opfindelsen resulterer i en høj virkningsgrad, er driftssikker og kræver kun lave inves-25 teringsomkostninger i forhold til de hidtil kendte fremgangsmåder .The process according to the invention results in a high efficiency, is reliable and requires only low investment costs compared to the known methods.

Ved en fordelagtig udførelsesform for fremgangsmåden ifølge opfindelsen opnås en særlig god adskillelse, når kapillært bundet vand bringes til at fordampe fra reak-30 tionsprodukterne efter deres afsætning på filtermaterialet under videre reaktion mellem tilbageværende svovldioxid i røggassen, absorbenten og det frigjorte vand.In an advantageous embodiment of the process according to the invention, a particularly good separation is obtained when capillary bound water is evaporated from the reaction products after their deposition on the filter material during further reaction between residual sulfur dioxide in the flue gas, the absorbent and the released water.

Apparatet ifølge opfindelsen omfatter et reaktionskammer med indløb for gassen og en forstøver for tilførsel af en 3The apparatus of the invention comprises a reaction chamber with inlet for the gas and an atomizer for supplying a 3

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absorbent i form af en absorbent i form af en vandig opløsning eller vandig suspension til røggassen i reaktionskammeret og et filterkammer med aggregater til 5 udskillelse af de dannede reaktionsprodukter fra gassen. Apparatet ifølge opfindelsen er ejendommeligt ved, at reaktionskammeret er integreret i filterkammeret, hvori udskillelsesaggregatet består af spærrefilter af tekstilstof, og at rumfanget af reaktionskammeret mellem 10 gasindløbet og filtermaterialet er dimensioneret således, at røggasstrømmen får en gennemsnitlig opholdstid på mellem 1 og 15 sekunder i kammerdelen.absorbent in the form of an absorbent in the form of an aqueous solution or aqueous suspension for the flue gas in the reaction chamber and a filter chamber with aggregates for separating the reaction products formed from the gas. The apparatus according to the invention is characterized in that the reaction chamber is integrated in the filter chamber, in which the separating assembly consists of a fabric filter barrier, and that the volume of the reaction chamber between the gas inlet and the filter material is dimensioned so that the flue gas flow has an average residence time of between 1 and 15 seconds in the chamber. .

Opfindelsen er baseret på den overraskende erkendelse, at tørringstrinet og adskillelsestrinet kan udføres i et 15 integreret kammer, til forskel fra kendte fremgangsmåder, hvor der altid udnyttes særskilte apparaturenheder ved fremgangsmåden. Årsagen til dette er først og fremmest, at risikoen for tilstopning af filtermaterialet har været bedømt til at være meget stor, når et vandholdigt 20 absorptionsmiddel skal tilsættes direkte i filterkammeret, hvilket da kunne formodes at give en stærk forhøjet gasmodstand over adskilleren. Ifølge opfindelsen anbringes dyser eller andre organer til atomisering af absorbenten inden i selve filterkammeret, på en sådan måde, at 25 indkommen varm gas omskyller disse og rettes således, at blandingen af væskedråber og afkølet gas ikke direkte når filtermediet uden først at have strømmet frit i kammeret i et tidsrum på 1-15 sekunder. Størsteparten af vandet i den indsprøjtede absorbent fordamper herved, og et vist rest-30 indhold af fugt findes i stoffet, selv efter at der er udskilt på filtermediet.The invention is based on the surprising realization that the drying step and the separation step can be carried out in an integrated chamber, unlike known methods, whereby separate apparatus units are always utilized in the process. The reason for this is first and foremost that the risk of clogging of the filter material has been judged to be very high when an aqueous absorbent is to be added directly into the filter chamber, which could then be assumed to give a strong increased gas resistance over the separator. According to the invention nozzles or other means for atomizing the absorbent within the filter chamber itself are arranged in such a way that incoming hot gas flushes them and is directed so that the mixture of liquid droplets and cooled gas does not directly reach the filter medium without first flowing freely in the filter chamber. chamber for a period of 1-15 seconds. Most of the water in the injected absorbent evaporates, and a certain residual moisture content is found in the fabric even after it has been filtered out on the filter medium.

Det har endvidere overraskende vist sig, at et stort restindhold af vand kan accepteres i det udskilte stof, uden at der har kunnet iagttages ulemper i form af et øget 35 trykfald over filteret. Ved disse forsøg med et apparatur af den angivne type har man tilmed bevidst gjort væskedo-Furthermore, it has surprisingly been found that a large residual content of water can be accepted in the separated substance without any inconvenience in the form of an increased pressure drop across the filter. In addition, in these experiments with an apparatus of the type specified,

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4 seringen så stor, at filtermediet har været helt vådt, uden at de forventede ulemper har kunnet iagttages. I modsætning til, hvad der måtte forventes, synes perme-5 abiliteten ikke at påvirkes negativt af tilstedeværende fugt.4 is so large that the filter media has been completely wet, without the expected disadvantages being observed. Contrary to what might be expected, the permeability does not appear to be adversely affected by the moisture present.

Som følge af at et højere fugtindhold i stoffet kan accepteres, kan man forvente en væsentlig højere udskillelsesgrad for SC>2 i systemet ifølge opfindelsen. Forsøg har 10 vist, at man med røggasser fra fyring med kul med lavt svovlindhold kan forøge udskillelsesgraden fra ca. 75% til ca. 97% ved at gennemføre processen med et højere fugtig-hedsindhold i stoffet i filteret. Opfindelsen medfører tillige en væsentlig formindskelse af investeringsomkost-15 ningerne i forhold til den konventionelle teknik, da det kun er nødvendigt at bygge et kammer, med de betydelige besparelser dette indebærer for stålkonstruktioner, trapper og gangarealer samt ikke mindst isolering.As a higher moisture content of the fabric is acceptable, a significantly higher excretion rate of SC> 2 can be expected in the system of the invention. Experiments have shown that with flue gases from combustion with low sulfur content coal can increase the excretion rate from approx. 75% to approx. 97% by completing the process with a higher moisture content of the substance in the filter. The invention also results in a substantial reduction in investment costs over the conventional technique, since it is only necessary to build a chamber, with the considerable savings this entails for steel structures, stairs and corridors, and not least insulation.

Opfindelsen forklares nærmere i det følgende under hen-20 visning til tegningen, som skematisk viser et apparat ifølge opfindelsen. På tegningen er vist et filterkammer 1, hvortil den varme røggas føres gennem et gasindløb 2.The invention is explained in more detail below with reference to the drawing, which schematically shows an apparatus according to the invention. In the drawing, a filter chamber 1 is shown to which the hot flue gas is passed through a gas inlet 2.

Ved dettes overgang til kammeret er anbragt en forstøver 3, hvortil absorbenten i form af en vandig opløsning eller 25 vandig suspension føres gennem en væskeledning 4. I filterkammeret 1 er anbragt et spærrefilter 6 af tekstil i form af et antal filterslanger 7. Rummet mellem gasindløbet 2 og spærrefilteret 6 danner et reaktionskammer V, i hvilket reaktionen mellem absorbenten og svovldioxiden i 30 røggassen finder sted under tørring af reaktionsprodukterne. Reaktionskammeret V er dimensioneret således i forhold til røggasmængden Q, at den gennemsnitlige opholdstid for røggassen i reaktionskammeret V er mellem 1 og 15 sekunder. Forholdet mellem rumfanget af reaktions-35 kammeret V i m^ og røggasmængden Q i m^ pr. sekund er således mellem 1 og 15 sekunder. Ved anbringelse af forstøveren 3 ved gasindløbets 2 overgang til reaktions- 5At its transition to the chamber is provided a nebulizer 3 to which the absorbent in the form of an aqueous solution or aqueous suspension is passed through a liquid conduit 4. In the filter chamber 1 is placed a textile barrier filter 6 in the form of a number of filter hoses 7. The space between the gas inlet 2 and the barrier filter 6 form a reaction chamber V in which the reaction between the absorbent and the sulfur dioxide in the flue gas takes place during drying of the reaction products. The reaction chamber V is dimensioned so as to the amount of flue gas Q that the average residence time of the flue gas in the reaction chamber V is between 1 and 15 seconds. The ratio of the volume of the reaction chamber V in m 2 to the amount of flue gas Q in m Thus, the second is between 1 and 15 seconds. By placing the nebulizer 3 at the transition of the gas inlet 2 to the reaction 5

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kammeret V opnås en effektiv blanding af den tilførte absorbent i røggasmængden Q. Det tilnærmelsesvis tørre stof bestående af de dannede reaktionsprodukter afsættes 5 på filterslangerne 7, når den rensede gas passerer gennem filtermaterialet og forlader filterkammeret 1 via et udløb for renset gas 8, som er forsynet med organer 9 til rensning af slangerne. Under filterslangerne 7 er anbragt bundlommer 10 til opsamling af det udskilte stof, som 10 senere udtages gennem.sluseaggregater 11.chamber V is obtained an effective mixture of the feed absorbent in the flue gas Q. The substantially dry substance consisting of the reaction products formed is deposited 5 on the filter hoses 7 as the purified gas passes through the filter material and leaves the filter chamber 1 via an outlet for purified gas 8 which is provided with means 9 for cleaning the hoses. Underneath the filter hoses 7 are placed bottom pockets 10 for collecting the separated material, which 10 is later taken out through lock assemblies 11.

Opfindelsen illustreres nærmere i det følgende udførelseseksempel .The invention is further illustrated in the following embodiment.

En gasmængde på ca. 15500 m^/h med en temperatur på 148°C tilføres en forsøgsanordning, som består af et modificeret 15 slangefilter, fra hvilket der er fjernet slanger, således at der dannes et tomt rum i filterkammerets midte. Filterets højde er ca. 6,5 m, og det har et kvadratisk tværsnit på 2,3 x 2,3 m. Filteret indeholder i alt 75 filterslanger svarende til en filteroverflade på 150 m^. Gassen indføres 20 gennem filterkammerets top i en lodret anbragt kanal, som udmunder ca. 0,2 m neden for filterkammerets top. I samme højde er anbragt en dyse af konventionel to-medie type. Svovldioxidindholdet 1 den indgående gas måles til ca. 500 ppm. Ved tilførsel af ca. 6,5 1/min. af en ca. 4%'s sus-25 pension af calciumhydroxid falder svovldioxidindholdet i den udgående gas til ca. 75 ppm ved en temperatur i afgangsgassen på 75°C. Trykfaldet over filteret varierer mellem 102 og 118 mm vandsøjle, afhængigt af rensningen af filterslangerne, som foretages ved hjælp af trykluft. 1A gas quantity of approx. 15500 m 2 / h with a temperature of 148 ° C is fed to a test device consisting of a modified 15 hose filter from which hoses have been removed so that an empty space is formed in the center of the filter chamber. The height of the filter is approx. 6.5 m and it has a square cross section of 2.3 x 2.3 m. The filter contains a total of 75 filter tubes corresponding to a filter surface of 150 m ^. The gas is introduced through the top of the filter chamber into a vertically disposed channel which opens approx. 0.2 m below the top of the filter chamber. At the same height is arranged a nozzle of conventional two-media type. The sulfur dioxide content of the incoming gas is measured at approx. 500 ppm. By applying approx. 6.5 l / min. of a ca. The 4% suspension of calcium hydroxide reduces the sulfur dioxide content of the outgoing gas to approx. 75 ppm at a temperature in the exhaust gas of 75 ° C. The pressure drop across the filter varies between 102 and 118 mm water column, depending on the cleaning of the filter hoses, which is done by compressed air. 1

Opfindelsen er ovenfor beskrevet i forbindelse med fjernelse af svovldioxid fra en gasstrøm. Opfindelsen er imidlertid ikke begrænset hertil, men er inden for rammerne af patentkravene anvendelig til fjernelse af andre uønskede sure gaskomponenter.The invention is described above in connection with the removal of sulfur dioxide from a gas stream. However, the invention is not limited thereto, but is within the scope of the claims applicable to the removal of other undesirable acidic gas components.

Claims (3)

1. Fremgangsmåde til rensning af varm røggas for svovldioxid eller andre uønskede sure gaskomponenter, ved 5 hvilken en absorbent i form af en vandig opløsning eller vandig suspension bringes i kontakt med røggassen under tørring af reaktionsprodukterne, som dannes af absor-benten og svovldioxiden, hvorpå reaktionsprodukterne udskilles i et tekstilspærrefilter, kendetegnet ved, at 10 absorbenten indføres i et filterkammer (1) i finfordelt form og blandes med den til filterkammeret tilførte røggasstrøm (Q), og at blandingen bibringes en opholdstid i filterkammeret (V) på mellem 1 og 15 sekunder under tilnærmelsesvis fuldstændig overfladefordampning hos 15 reaktionsprodukterne, hvorefter røggasstrømmen føres igennem filtermaterialet i det i filterkammeret anbragte filter (6) under afsætning af de dannede reaktionsprodukter på filtermaterialet (7).A process for purifying hot flue gas from sulfur dioxide or other undesirable acidic gas components, in which an absorbent in the form of an aqueous solution or aqueous suspension is contacted with the flue gas during drying of the reaction products formed by the absorbent and sulfur dioxide, the reaction products are separated into a textile barrier filter, characterized in that the absorbent is introduced into a filter chamber (1) in finely divided form and mixed with the flue gas stream (Q) supplied to the filter chamber, and that the mixture is given a residence time in the filter chamber (V) of between 1 and 15. seconds during approximately complete surface evaporation of the reaction products, after which the flue gas flow is passed through the filter material in the filter (6) disposed in the filter chamber while depositing the reaction products formed on the filter material (7). 2. Fremgangsmåde ifølge krav 1, kendetegnet ved, at 20 kapillært bundet vand bringes til at fordampe fra reaktionsprodukterne efter deres afsætning på filtermaterialet (7) under videre reaktion mellem tilbageværende svovldioxid i røggassen, absorbenten og det frigjorte vand.Process according to claim 1, characterized in that 20 capillary bonded water is evaporated from the reaction products after their deposition on the filter material (7) during further reaction between residual sulfur dioxide in the flue gas, the absorbent and the released water. 3. Apparat til rensning af varm røggas for svovldi-25 oxid eller andre uønskede sure gaskomponenter omfattende et reaktionskammer (V) med indløb for gassen og en forstøver (3) for tilførsel af en absorbent i form af vandig opløsning eller vandig suspension til røggassen i reaktionskammeret (V) og et filterkammer (1) med 30 aggregater (6) til udskillelse af de dannede reaktionsprodukter fra gassen, kendetegnet ved, at reaktionskammeret (V) er integreret i filterkammeret (1), hvori udskillelsesaggregatet består af spærrefiltre (6) af tekstilstof, og at rumfanget af reaktionskammeret (V) 35 mellem gasindløbet (2) og filtermaterialet (7) er dimen- DK 154008 B sioneret således, at røggasstrømmen får en gennemsnitlig opholdstid på mellem 1 og 15 sekunder i kammerdelen (V).An apparatus for purifying hot flue gas for sulfur dioxide or other undesirable acidic gas components comprising a reaction chamber (V) with inlet for the gas and an atomizer (3) for supplying an absorbent in the form of aqueous solution or aqueous suspension to the flue gas. the reaction chamber (V) and a filter chamber (1) with 30 aggregates (6) for separating the reaction products formed from the gas, characterized in that the reaction chamber (V) is integrated into the filter chamber (1), in which the separating assembly consists of blocking filters (6) of and the volume of the reaction chamber (V) 35 between the gas inlet (2) and the filter material (7) is dimensioned such that the flue gas flow has an average residence time of between 1 and 15 seconds in the chamber part (V).
DK442780A 1979-10-19 1980-10-17 PROCEDURE FOR CLEANING HOT ROEGGAS FOR SULFUR DIOXIDE OR OTHER UNWANTED ACID GAS COMPONENTS FROM HOT ROEGGAS AND APPARATUS FOR EXERCISING THE PROCEDURE DK154008C (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
SE7908673A SE429010B (en) 1979-10-19 1979-10-19 SET TO CLEAN A HEAT GAS FROM SULFUR DIOXIDE OR OTHER NON-REQUIRED SURA GAS COMPONENTS AND DEVICE PERFORMANCE
SE7908673 1979-10-19

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DK442780A DK442780A (en) 1981-04-20
DK154008B true DK154008B (en) 1988-10-03
DK154008C DK154008C (en) 1989-02-20

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
SE454142B (en) * 1985-04-23 1988-04-11 Flaekt Ab CONTACT REACTOR

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE2140130A1 (en) * 1971-08-10 1973-02-15 Franz Kosar FILTER TO REMOVE SOOT AND GASES FROM EXHAUST AIR
DE2314145A1 (en) * 1972-03-27 1973-10-18 Asahi Glass Co Ltd METHOD OF REMOVING SULFUR OXYDES, DUST AND MIST COMBUSTION GASES
DE2752833A1 (en) * 1977-11-26 1979-06-07 Heinz Hoelter Flue gas purification - by filtering through metal cloth combining dust removal with catalytic conversion of toxic components

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE2725436A1 (en) * 1977-06-04 1978-12-21 Heinz Hoelter Dust and sulphur oxide removal from hot gas - by lime slurry injection and cloth filtering

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE2140130A1 (en) * 1971-08-10 1973-02-15 Franz Kosar FILTER TO REMOVE SOOT AND GASES FROM EXHAUST AIR
DE2314145A1 (en) * 1972-03-27 1973-10-18 Asahi Glass Co Ltd METHOD OF REMOVING SULFUR OXYDES, DUST AND MIST COMBUSTION GASES
DE2752833A1 (en) * 1977-11-26 1979-06-07 Heinz Hoelter Flue gas purification - by filtering through metal cloth combining dust removal with catalytic conversion of toxic components

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DK442780A (en) 1981-04-20
SE429010B (en) 1983-08-08
DE3038014C2 (en) 1990-04-12
SE7908673L (en) 1981-04-20
DE3038014A1 (en) 1981-04-30
DK154008C (en) 1989-02-20

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