AT360967B - METHOD AND DEVICE FOR REDUCING THE CHLORIDE CONTENT OF MAGNESIUM BISULFITE - Google Patents
METHOD AND DEVICE FOR REDUCING THE CHLORIDE CONTENT OF MAGNESIUM BISULFITEInfo
- Publication number
- AT360967B AT360967B AT424778A AT424778A AT360967B AT 360967 B AT360967 B AT 360967B AT 424778 A AT424778 A AT 424778A AT 424778 A AT424778 A AT 424778A AT 360967 B AT360967 B AT 360967B
- Authority
- AT
- Austria
- Prior art keywords
- magnesium
- bisulfite
- stage
- monosulfite
- chloride
- Prior art date
Links
- LPHFLPKXBKBHRW-UHFFFAOYSA-L magnesium;hydrogen sulfite Chemical compound [Mg+2].OS([O-])=O.OS([O-])=O LPHFLPKXBKBHRW-UHFFFAOYSA-L 0.000 title claims description 12
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 title claims 5
- 238000000034 method Methods 0.000 title claims 4
- JESHZQPNPCJVNG-UHFFFAOYSA-L magnesium;sulfite Chemical compound [Mg+2].[O-]S([O-])=O JESHZQPNPCJVNG-UHFFFAOYSA-L 0.000 claims description 17
- LSNNMFCWUKXFEE-UHFFFAOYSA-M Bisulfite Chemical compound OS([O-])=O LSNNMFCWUKXFEE-UHFFFAOYSA-M 0.000 claims description 8
- 239000007788 liquid Substances 0.000 claims description 7
- 238000010521 absorption reaction Methods 0.000 claims description 5
- 239000012535 impurity Substances 0.000 claims description 5
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 claims description 4
- 238000004140 cleaning Methods 0.000 claims description 4
- 238000002485 combustion reaction Methods 0.000 claims description 3
- 239000013505 freshwater Substances 0.000 claims description 3
- 238000011084 recovery Methods 0.000 claims description 3
- 239000000725 suspension Substances 0.000 claims description 3
- 239000003513 alkali Substances 0.000 claims description 2
- 238000003776 cleavage reaction Methods 0.000 claims description 2
- 239000013078 crystal Substances 0.000 claims description 2
- 230000007017 scission Effects 0.000 claims description 2
- 239000007789 gas Substances 0.000 claims 5
- 238000005406 washing Methods 0.000 claims 3
- 239000000428 dust Substances 0.000 claims 2
- 239000000126 substance Substances 0.000 claims 2
- 230000002745 absorbent Effects 0.000 claims 1
- 239000002250 absorbent Substances 0.000 claims 1
- 150000001805 chlorine compounds Chemical class 0.000 claims 1
- 239000002245 particle Substances 0.000 claims 1
- 238000010438 heat treatment Methods 0.000 description 3
- 150000003841 chloride salts Chemical class 0.000 description 2
- 230000004992 fission Effects 0.000 description 2
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 2
- 239000000395 magnesium oxide Substances 0.000 description 2
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 2
- 238000005201 scrubbing Methods 0.000 description 2
- 238000005728 strengthening Methods 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- 230000003321 amplification Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 230000029142 excretion Effects 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000003199 nucleic acid amplification method Methods 0.000 description 1
- 150000003112 potassium compounds Chemical class 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
Classifications
-
- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21C—PRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
- D21C11/00—Regeneration of pulp liquors or effluent waste waters
- D21C11/06—Treatment of pulp gases; Recovery of the heat content of the gases; Treatment of gases arising from various sources in pulp and paper mills; Regeneration of gaseous SO2, e.g. arising from liquors containing sulfur compounds
- D21C11/063—Treatment of gas streams comprising solid matter, e.g. the ashes resulting from the combustion of black liquor
-
- 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
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F5/00—Compounds of magnesium
- C01F5/42—Magnesium sulfites
-
- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21C—PRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
- D21C11/00—Regeneration of pulp liquors or effluent waste waters
- D21C11/06—Treatment of pulp gases; Recovery of the heat content of the gases; Treatment of gases arising from various sources in pulp and paper mills; Regeneration of gaseous SO2, e.g. arising from liquors containing sulfur compounds
- D21C11/063—Treatment of gas streams comprising solid matter, e.g. the ashes resulting from the combustion of black liquor
- D21C11/066—Separation of solid compounds from these gases; further treatment of recovered products
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Analytical Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Inorganic Chemistry (AREA)
- Biomedical Technology (AREA)
- Treating Waste Gases (AREA)
Description
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333588),- -9--. Das im Trockenabscheider --2-- abgeschiedene Magnesiumoxyd ist durch wasserlösliche Salze verunreinigt und wird der Sulfitstufe --4-- zugeführt, wo es in Magnesiumsulfit umgewandelt wird.
Während die Verunreinigungen von Wasser gelöst werden, ist das Magnesiumsulfit im Wasser nur zu geringem Teil löslich. Das Magnesiumsulfit wird über die Leitung --20-- einem Absetzbehälter --7-- zugeführt, wo sich das Sulfit absetzt und mit Frischwasser gewaschen wird. Im Absetzbehälter --7-- fallen die Magnesiumsulfitkristalle im Gegenstrom zum aufsteigenden Frischwasser aus, so dass sie in gereinigter Form über die Leitung --10-- in die Bisulfitstufe --3-- der Absorptionsanlage eingebracht werden können.
Im Nasswäscher --5-- wird die Waschflüssigkeit im Kreis geführt, wobei sich die Waschflüssigkeit mit Verunreinigungen anreichert und gleichzeitig aus dem in geringen Mengen in diesen Wäscher einlangenden Magnesiumoxyd mit einem Teil des im Abgas vorhandenen S02 im wesentlichen Magnesiumbisulfit erzeugt wird. Diese mit Verunreinigungen angereicherte Lösung wird diskontinuierlich über die Leitung --13-einer Spaltungsanlage --6-- für Magnesiumbisulfit zugeführt, wo unter Wärmezufuhr in Form von Heizdampf über die Leitung --14--, der im Laugenverbrennungskessel --1-- erzeugt wird, die Spaltung des Magnesiumbisulfits in Magnesiummonosulfit und S02 erfolgt.
Zu diesem Zweck wird die Bisulfitlösung über eine Pumpe und die Leitung --15-- vom Boden der Spaltungsanlage --6-- in einen Fallkanal --16-geführt, in welchem sie mit dem Heizdampf in Berührung gebracht wird. Infolge der Wärmezufuhr erfolgt
EMI2.1
von wo es über die Leitung --18-- dem Absetzbehälter --7-- zugeführt wird. In dieser Suspension sind in gelöster Form auch die Chloride, die im Nasswäscher --5-- aus dem Abgas ausgewaschen werden, enthalten.
Zur Verringerung der Verluste an gelöstem Magnesiummonosulfit und zur Vermeidung von
Inkrustationen in der Leitung --24-- kann die Lösung im Absetzbehälter --7-- und/oder im Zuge der
Zuführungsleitungen --18 und 20-- zum Absetzbehälter in den Wärmetauschern --21 und 22-- gekühlt werden. Hiedurch sinkt die Löslichkeit des Magnesiumsulfits und es wird Magnesiumsulfit aus der übersättigten Lösung ausgeschieden. Ein Teil der Klarflüssigkeit wird zur Deckung der Verdampfungsverluste über die Leitung --23-- in den Nasswäscher --5-- zurückgeführt. Über die Leitung --24-- wird der andere Teil der Klarflüssigkeit mit den gelösten Verunreinigungen, wie z. B. Chloriden und/oder Kaliumverbindungen, abgeführt.
Die Spaltungsanlage --6-- und die Aufstärkanlage --8-- sind apparategleich ausgeführt und durch Armaturen so verbunden, dass sie jederzeit ausgetauscht werden können. Das Vertauschen bewirkt eine Funktionsumkehrung, so dass die etwa entstandenen Ausscheidungen von Magnesiumsulfit in der Spaltungsanlage --6-- bei Verwendung in einer Aufstärkstufe --8-- wieder gelöst werden können, wodurch eine selbsttätige Reinigung der Apparatur gewährleistet ist. Der Aufstärkbehälter --8-- weist somit ebenfalls einen Fallkanal --16-- auf, in welchem die im Kreislauf geführte Lösung anstelle von Heizdampf mit S02-Wasserdampf-Gemisch aus der Spaltungsanlage --6-- über die Leitung --17-- in Berührung gebracht wird.
Im Schaltbild sind die durchlässigen Ventile durch Dreiecke symbolisiert, während die nichtdurchlässigen Ventile durch schwarze Dreiecke gekennzeichnet sind.
Über die Leitung --10-- wird somit das im Nasswäscher --5-- und in der Monosulfitstufe --4-erzeugte Magnesiummonosulfit der Bisulfitstufe --3-- zugeführt, wo es durch SO2-Aufnahme in Bisulfit übergeführt wird. Die Bisulfitlösung wird über die Leitung --11-- in die Aufstärkstufe --8-- geleitet, dort mit S02 aufgesättigt, wodurch etwaiges Restmonosulfit in Bisulfit umgewandelt wird. Die aufgesättigte Bisulfitlösung wird über die Leitung --12-- einer Reinigung und schliesslich der Kocherei zu ihrer Wiederverwendung zugeführt.
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EMI1.1
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333588), - -9--. The magnesium oxide separated in the dry separator --2-- is contaminated by water-soluble salts and is fed to the sulfite stage --4--, where it is converted into magnesium sulfite.
While the impurities are dissolved by water, the magnesium sulfite is only slightly soluble in the water. The magnesium sulfite is fed via line --20-- to a settling tank --7--, where the sulfite settles and is washed with fresh water. In the settling tank --7--, the magnesium sulfite crystals precipitate in countercurrent to the rising fresh water, so that they can be introduced in purified form via line --10-- into the bisulfite stage --3-- of the absorption system.
The scrubbing liquid is circulated in the wet scrubber --5--, the scrubbing liquid being enriched with impurities and at the same time being generated from the magnesium oxide arriving in small amounts in this scrubber with part of the S02 present in the exhaust gas, essentially magnesium bisulfite. This solution, which is enriched with impurities, is fed intermittently via line --13 - to a splitting plant --6-- for magnesium bisulfite, where, under the addition of heat in the form of heating steam via line --14--, which is generated in the alkali combustion boiler --1-- the magnesium bisulfite is split into magnesium monosulfite and S02.
For this purpose, the bisulfite solution is fed via a pump and the line --15-- from the bottom of the fission system --6-- into a drop channel --16-, in which it is brought into contact with the heating steam. As a result of the supply of heat
EMI2.1
from where it is fed via line --18-- to the settling tank --7--. This suspension also contains the chlorides, which are washed out of the exhaust gas in the wet scrubber --5--.
To reduce the loss of dissolved magnesium monosulfite and to avoid
Incrustations in the line --24-- can be the solution in the settling tank --7-- and / or in the course of
Supply lines --18 and 20-- to the settling tank in the heat exchangers --21 and 22-- should be cooled. This reduces the solubility of the magnesium sulfite and magnesium sulfite is excreted from the supersaturated solution. Part of the clear liquid is returned to the wet scrubber --5-- to cover evaporation losses via line --23--. The other part of the clear liquid with the dissolved impurities, such as e.g. B. chlorides and / or potassium compounds.
The splitting system --6-- and the amplification system --8-- are designed in the same way and connected by fittings so that they can be replaced at any time. The interchanging causes a reversal of the function, so that any magnesium sulfite excretions in the cleavage system --6-- when used in a strengthening stage --8-- can be resolved again, which guarantees automatic cleaning of the equipment. The recovery tank --8-- thus also has a drop channel --16-- in which the circulated solution instead of heating steam with S02-water vapor mixture from the fission system --6-- via line --17- - is brought into contact.
In the circuit diagram, the permeable valves are symbolized by triangles, while the non-permeable valves are marked by black triangles.
The magnesium monosulfite generated in the wet scrubber --5-- and in the monosulfite stage --4 is fed to the bisulfite stage --3-- via line --10--, where it is converted into bisulfite by SO2 absorption. The bisulfite solution is fed via line --11-- to the strengthening stage --8--, where it is saturated with S02, whereby any residual monosulfite is converted into bisulfite. The saturated bisulfite solution is fed via line --12-- to a cleaning facility and finally to the cookery for reuse.
Claims (1)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| AT424778A AT360967B (en) | 1977-07-01 | 1978-06-12 | METHOD AND DEVICE FOR REDUCING THE CHLORIDE CONTENT OF MAGNESIUM BISULFITE |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| AT468677A AT352692B (en) | 1977-07-01 | 1977-07-01 | PROCESS AND EQUIPMENT FOR REDUCING THE CHLORIDE CONTENT OF MAGNESIUM BISULPHITE |
| AT424778A AT360967B (en) | 1977-07-01 | 1978-06-12 | METHOD AND DEVICE FOR REDUCING THE CHLORIDE CONTENT OF MAGNESIUM BISULFITE |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| ATA424778A ATA424778A (en) | 1980-07-15 |
| AT360967B true AT360967B (en) | 1981-02-10 |
Family
ID=25600975
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| AT424778A AT360967B (en) | 1977-07-01 | 1978-06-12 | METHOD AND DEVICE FOR REDUCING THE CHLORIDE CONTENT OF MAGNESIUM BISULFITE |
Country Status (1)
| Country | Link |
|---|---|
| AT (1) | AT360967B (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109502866B (en) * | 2018-08-27 | 2024-05-31 | 启迪环境科技发展股份有限公司 | A processing system and method for recycling nanofiltration concentrate |
-
1978
- 1978-06-12 AT AT424778A patent/AT360967B/en not_active IP Right Cessation
Also Published As
| Publication number | Publication date |
|---|---|
| ATA424778A (en) | 1980-07-15 |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| ELJ | Ceased due to non-payment of the annual fee |