WO1993000983A1 - Verfahren zum reinigen eines schwefeldioxid und ggf. andere schadstoffe enthaltenden abgases - Google Patents

Verfahren zum reinigen eines schwefeldioxid und ggf. andere schadstoffe enthaltenden abgases Download PDF

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Publication number
WO1993000983A1
WO1993000983A1 PCT/EP1992/001074 EP9201074W WO9300983A1 WO 1993000983 A1 WO1993000983 A1 WO 1993000983A1 EP 9201074 W EP9201074 W EP 9201074W WO 9300983 A1 WO9300983 A1 WO 9300983A1
Authority
WO
WIPO (PCT)
Prior art keywords
mercury
gypsum
washing liquid
exhaust gas
washing
Prior art date
Application number
PCT/EP1992/001074
Other languages
German (de)
English (en)
French (fr)
Inventor
Ulrich Mohn
Ryszard Kubisa
Original Assignee
L. & C. Steinmüller Gmbh
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by L. & C. Steinmüller Gmbh filed Critical L. & C. Steinmüller Gmbh
Publication of WO1993000983A1 publication Critical patent/WO1993000983A1/de

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Classifications

    • 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
    • B01D53/64Heavy metals or compounds thereof, e.g. mercury
    • 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
    • B01D53/501Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F11/00Compounds of calcium, strontium, or barium
    • C01F11/46Sulfates
    • C01F11/464Sulfates of Ca from gases containing sulfur oxides
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G13/00Compounds of mercury
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G13/00Compounds of mercury
    • C01G13/003Preparation involving a liquid-liquid extraction, an adsorption or an ion-exchange

Definitions

  • the invention relates to a method for purifying an exhaust gas containing sulfur dioxide, mercury and possibly other pollutants, in which the exhaust gas is dedusted and washed in at least one stage with a calcium-containing washing liquid and in which the calcium sulfite formed with the addition of air in calcium sulfate (gypsum) is converted and then calcium sulfate-containing washing liquid is removed and gypsum is separated from the removed washing liquid.
  • gypsum calcium sulfate
  • a cleaning method with two-stage wet washing is known.
  • the first wash stage is used for cooling the flue gas and for the separation of other harmful gases such as HF, HC1 and heavy metals, while the second wash stage is used for S0 2 separation and the adjustment of the clean gas values.
  • Solids-containing washing liquid is drawn off from the bottom of both washing stages and fed to a thickener.
  • the thickened washing liquid is fed to a filter press. If mercury is contained to a large extent in the flue gas as a divalent ion, mercury is introduced in the known method via the thickener into the solid matter withdrawn from the filter press, which consists essentially of gypsum. This mercury entry limits the use of gypsum.
  • This object is achieved in that a chemical which converts the mercury into a water-insoluble compound and / or an adsorbent which adsorbs the mercury is added to the exhaust gas before the washing or the washing liquid itself and the water-insoluble compound or the laden adsorbent when the gypsum is separated off from the withdrawn washing liquid is discharged with the waste water.
  • Alkali sulfide compounds and selenium sulfide compounds, as well as iodine or sulfur in solid form, in particular sulfur bloom, are preferably suitable as the chemical leading to a water-insoluble mercury compound, which is preferably added to the flue gas before the first washing stage.
  • Sodium sulfides such as sodium polysulfide Na 2 S ⁇ or sodium monosulfide Na2S are particularly preferred.
  • the selenium compounds include in particular the selenium disulfide SeS2. mixtures of the chemicals can be used.
  • Granular carbon-containing adsorbents such as lignite or hard coal activated coke / coal, or other fine-particle adsorbents such as diatomaceous earth or activated Al2O3 are particularly suitable as adsorbents.
  • About the adsorbents in the sense of the present invention also include gels such as B silica gel, which can absorb the mercury.
  • the chemical or the adsorbent leading to the sparingly soluble mercury compound is preferably added to the exhaust gas before the first stage.
  • Mercury compounds or the mercury-laden adsorbent when separating the gypsum from the removed washing liquid is possible because the particles of the sparingly soluble mercury compound and the adsorbent particles differ in terms of their particle size distribution, shape and / or density from that in the main scrubber and possibly in the pre-scrubber differentiate produced plaster. It can A different parameter may be sufficient to achieve the separation with the waste water from the gypsum.
  • the particles of the poorly soluble mercury compounds have a flaky shape and thus differ significantly from the gypsum crystals, which in particular have an elongated shape.
  • the adsorbent particles can be assumed to have a much lower density than the gypsum crystals. In this way, it is possible to separate the mercury compounds or the adsorbed mercury from the gypsum when the gypsum is separated from the washing liquid with the wastewater from the dewatering and separation stage.
  • a method is thus specified in which, surprisingly, with a process step which is already present per se, namely the separation of gypsum with drainage, it is also possible to keep the mercury away from the gypsum; the dewatering and separation stage only has to respond to at least one of the parameters shown above.
  • a combination of a cyclone station with a downstream belt filter or a centrifuge, in particular an overflow centrifuge, is particularly suitable for separating the mercury from the gypsum while draining the gypsum.
  • the addition is to be carried out in such a way that a reaction time which is sufficient for the reaction to the water-insoluble mercury compounds is achieved before entering the at least one washing stage.
  • the aftertreatment of the waste water to remove the insoluble mercury compounds or the activated carbon particles loaded with mercury is carried out in a known manner.
  • Fig. 1 shows a procedure in which the dewatering takes place with the aid of a cyclone station and downstream band filter
  • Fig. 2 shows a procedure in which the dewatering takes place with a centrifuge.
  • the dedusted raw gas to be cleaned is fed via line 1 to an HCl scrubber 2, to which a scrubbing circuit 3 is assigned. Via a line 4 At a predetermined distance from the head 2a of the HCl scrubber, sodium monosulfite is supplied, which together with the mercury contained in the raw gas stream in the form of HgCl 2 according to the following equation:
  • the water-insoluble mercury compounds are introduced into the liquid of the washing circuit 3.
  • the gas cooled in the HC1 washer and freed from HC1 and possibly other pollutants is transferred via line 5 into a SO ⁇ ashtray 6, to which a washing circuit 7 is assigned and in which the main part of S0 2 is removed from the exhaust gas.
  • Lime milk is fed to both washers via a line 8 with branch lines 8a and 8b, this being fed via line 8a to adjust the pH in the HC1 scrubber 2, while the larger part is fed via line 8b to the SC ⁇ scrubber to form calcium sulfite is fed.
  • Both washers are still supplied with air via lines 9 leading to the laundry sump in order to convert the calcium sulfite formed to calcium sulfate.
  • a chemical such as the product marketed under the trade name METALLCLEAN is fed to the scrubber via line 10, while one is fed via line 11 to the scrubber 6
  • Chemical such as the product sold by Degussa under the name TMT 15, a 2.4.6-trimercaptotriazine, trisodium solution.
  • Washing liquid is discharged from the circuits 3 and 7 via the lines 12 and 13 and fed to a collecting container 14.
  • Loaded washing liquid is fed to a dewatering assembly 15 from this collecting container 14. which consists of a cyclone station 16 and a downstream band filter 17.
  • the overflow of the cyclone station is fed via a line 18 and the waste water of the belt filter 17 via a line 19 to a collecting tank 20 from which the waste water is drawn off.
  • the poorly soluble mercury compound is discharged with the overflow liquid via line 18.
  • washing liquid is fed from the collecting container 14 to a drainage assembly 16 which has an overflow centrifuge 21.

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Inorganic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Treating Waste Gases (AREA)
PCT/EP1992/001074 1991-07-13 1992-05-15 Verfahren zum reinigen eines schwefeldioxid und ggf. andere schadstoffe enthaltenden abgases WO1993000983A1 (de)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
DEP4123258.5 1991-07-13
DE19914123258 DE4123258A1 (de) 1991-07-13 1991-07-13 Verfahren zum reinigen eines schwefeldioxid und ggf. andere schadstoffe enthaltenden abgases

Publications (1)

Publication Number Publication Date
WO1993000983A1 true WO1993000983A1 (de) 1993-01-21

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Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/EP1992/001074 WO1993000983A1 (de) 1991-07-13 1992-05-15 Verfahren zum reinigen eines schwefeldioxid und ggf. andere schadstoffe enthaltenden abgases

Country Status (2)

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DE (1) DE4123258A1 (GUID-C5D7CC26-194C-43D0-91A1-9AE8C70A9BFF.html)
WO (1) WO1993000983A1 (GUID-C5D7CC26-194C-43D0-91A1-9AE8C70A9BFF.html)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100366326C (zh) * 2000-12-08 2008-02-06 奥托库姆普联合股份公司 从气体中除去汞的方法
US11319233B2 (en) 2018-08-17 2022-05-03 Steve Feeney Consulting, Llc Control of aqueous arsenic, selenium, mercury or other metals from flue gas

Families Citing this family (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DK170887B1 (da) * 1993-01-21 1996-03-04 Fls Miljoe A S Fremgangsmåde og anvendelse af et anlæg til rensning af restprodukter fra røggasrensningsanlæg
DE4326279A1 (de) * 1993-08-05 1995-02-16 Veba Kraftwerke Ruhr Verfahren zum Abscheiden von Quecksilber aus Rauchgas
SE502159C2 (sv) * 1993-12-22 1995-09-04 Flaekt Ab Sätt och anordning att framställa gips med hög renhet
DE4437781A1 (de) * 1994-10-25 1996-05-02 Steinmueller Gmbh L & C Verfahren zum Entfernen von Quecksilber aus einem quecksilberhaltigen Abgas
DE4441090A1 (de) * 1994-11-18 1996-05-23 Steag Ag Verfahren und Vorrichtung zum Reinigen von Verbrennungsabgasen
DE19542065C2 (de) * 1995-11-13 1997-10-23 Steag Ag Verfahren und Vorrichtung zum Reinigen von Verbrennungsabgasen aus Feuerungsanlagen
DE19730909A1 (de) * 1997-07-18 1999-01-21 Babcock Anlagen Gmbh Verfahren zur Entfernung von Schad- und Spurenstoffen aus Rauchgas insbesondere von Müllverbrennungsanlagen
DE19800726C1 (de) * 1998-01-12 1999-09-23 Metallgesellschaft Ag Verfahren zur Abscheidung von elementaren Schwermetallen aus Abgasen
EP1077757B1 (en) * 1998-05-08 2003-03-19 Isca Management Limited Mercury removal from flue gas
JP3711229B2 (ja) 2000-06-30 2005-11-02 株式会社日本触媒 廃液処理方法
DE102012214065A1 (de) 2012-08-08 2014-02-13 EnBW Energie Baden-Württemberg AG Verfahren zum Entfernen von Quecksilber aus Rauchgas in einem Nasswäscher
DE102015218462A1 (de) 2015-09-25 2017-03-30 EnBW Energie Baden-Württemberg AG Apparative Ergänzung von Nasswäschern in Kohlekraftwerken zur besseren und sichereren Abscheidung von Quecksilber und seinen Verbindungen
CN106241384B (zh) * 2016-09-12 2019-03-19 中国电力工程顾问集团西南电力设计院有限公司 一种石灰石粉气力输送系统及控制方法

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DE3119749C2 (de) * 1981-05-18 1984-11-08 Steag Ag, 4300 Essen Verfahren zur Herstellung von Calciumsulfathalbhydrat aus Rauchgasgips
DD236459A1 (de) * 1985-04-25 1986-06-11 Leipzig Chemieanlagen Verfahren zur nassen so tief 2- abscheidung aus rauch- oder abgasen
DE2728692C2 (de) * 1976-08-19 1986-12-04 Dowa Mining Co. Ltd., Tokio/Tokyo Verfahren zur Entfernung von quecksilberhaltigen Verunreinigungen aus sauren Gasen

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DE3827831A1 (de) * 1988-08-17 1990-02-22 Thyssen Industrie Verfahren und anlage zur aufbereitung von abwasser, insbesondere aus der rauchgasentschwefelung
DE4032249C2 (de) * 1989-10-14 1998-09-24 Knauf Westdeutsche Gips Verfahren zur Aufhellung von Rauchgasgips

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DE2728692C2 (de) * 1976-08-19 1986-12-04 Dowa Mining Co. Ltd., Tokio/Tokyo Verfahren zur Entfernung von quecksilberhaltigen Verunreinigungen aus sauren Gasen
DE3119749C2 (de) * 1981-05-18 1984-11-08 Steag Ag, 4300 Essen Verfahren zur Herstellung von Calciumsulfathalbhydrat aus Rauchgasgips
DD236459A1 (de) * 1985-04-25 1986-06-11 Leipzig Chemieanlagen Verfahren zur nassen so tief 2- abscheidung aus rauch- oder abgasen

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100366326C (zh) * 2000-12-08 2008-02-06 奥托库姆普联合股份公司 从气体中除去汞的方法
US11319233B2 (en) 2018-08-17 2022-05-03 Steve Feeney Consulting, Llc Control of aqueous arsenic, selenium, mercury or other metals from flue gas

Also Published As

Publication number Publication date
DE4123258C2 (GUID-C5D7CC26-194C-43D0-91A1-9AE8C70A9BFF.html) 1993-07-01
DE4123258A1 (de) 1993-01-14

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