WO1996016721A1 - Method and apparatus for liquid regulation in wet cleaning of a gas - Google Patents
Method and apparatus for liquid regulation in wet cleaning of a gas Download PDFInfo
- Publication number
- WO1996016721A1 WO1996016721A1 PCT/SE1995/001404 SE9501404W WO9616721A1 WO 1996016721 A1 WO1996016721 A1 WO 1996016721A1 SE 9501404 W SE9501404 W SE 9501404W WO 9616721 A1 WO9616721 A1 WO 9616721A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- liquid
- stage
- dioxide
- sulphur
- air
- Prior art date
Links
- 239000007788 liquid Substances 0.000 title claims abstract description 199
- 238000004140 cleaning Methods 0.000 title claims abstract description 49
- 238000000034 method Methods 0.000 title claims abstract description 26
- 238000001704 evaporation Methods 0.000 claims abstract description 25
- 230000008020 evaporation Effects 0.000 claims abstract description 24
- 230000001105 regulatory effect Effects 0.000 claims abstract description 8
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 claims description 102
- 239000004291 sulphur dioxide Substances 0.000 claims description 51
- 235000010269 sulphur dioxide Nutrition 0.000 claims description 51
- 239000003546 flue gas Substances 0.000 claims description 31
- 239000007789 gas Substances 0.000 claims description 25
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 23
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 19
- 229910000041 hydrogen chloride Inorganic materials 0.000 claims description 19
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 claims description 19
- 229910052602 gypsum Inorganic materials 0.000 claims description 15
- 239000010440 gypsum Substances 0.000 claims description 15
- 238000000926 separation method Methods 0.000 claims description 11
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 9
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 9
- 239000004571 lime Substances 0.000 claims description 9
- 238000001816 cooling Methods 0.000 claims description 7
- 238000001556 precipitation Methods 0.000 claims description 7
- 238000010438 heat treatment Methods 0.000 claims description 6
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims description 3
- 239000001257 hydrogen Substances 0.000 claims description 3
- 229910052739 hydrogen Inorganic materials 0.000 claims description 3
- 238000005406 washing Methods 0.000 description 58
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 10
- 239000007921 spray Substances 0.000 description 10
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 9
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 9
- 238000009833 condensation Methods 0.000 description 8
- 230000005494 condensation Effects 0.000 description 8
- 229910021653 sulphate ion Inorganic materials 0.000 description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 8
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 7
- 238000010521 absorption reaction Methods 0.000 description 6
- 230000008929 regeneration Effects 0.000 description 6
- 238000011069 regeneration method Methods 0.000 description 6
- 239000000126 substance Substances 0.000 description 6
- 239000011780 sodium chloride Substances 0.000 description 5
- 239000002253 acid Substances 0.000 description 4
- 230000003647 oxidation Effects 0.000 description 4
- 238000007254 oxidation reaction Methods 0.000 description 4
- 229920006395 saturated elastomer Polymers 0.000 description 4
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 3
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 3
- 241000196324 Embryophyta Species 0.000 description 3
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 3
- 239000003513 alkali Substances 0.000 description 3
- 229910001424 calcium ion Inorganic materials 0.000 description 3
- 150000001805 chlorine compounds Chemical class 0.000 description 3
- 229910001385 heavy metal Inorganic materials 0.000 description 3
- 239000010446 mirabilite Substances 0.000 description 3
- 239000012452 mother liquor Substances 0.000 description 3
- 238000006386 neutralization reaction Methods 0.000 description 3
- 239000002244 precipitate Substances 0.000 description 3
- 150000003839 salts Chemical class 0.000 description 3
- 229910052938 sodium sulfate Inorganic materials 0.000 description 3
- 235000011152 sodium sulphate Nutrition 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 2
- 241000183024 Populus tremula Species 0.000 description 2
- 238000009825 accumulation Methods 0.000 description 2
- 150000001339 alkali metal compounds Chemical class 0.000 description 2
- 229910052925 anhydrite Inorganic materials 0.000 description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 2
- 239000000292 calcium oxide Substances 0.000 description 2
- 235000012255 calcium oxide Nutrition 0.000 description 2
- 239000013505 freshwater Substances 0.000 description 2
- XLYOFNOQVPJJNP-ZSJDYOACSA-N heavy water Substances [2H]O[2H] XLYOFNOQVPJJNP-ZSJDYOACSA-N 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 238000012856 packing Methods 0.000 description 2
- 230000001376 precipitating effect Effects 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- LSNNMFCWUKXFEE-UHFFFAOYSA-L sulfite Chemical compound [O-]S([O-])=O LSNNMFCWUKXFEE-UHFFFAOYSA-L 0.000 description 2
- -1 sulphate ions Chemical class 0.000 description 2
- 150000003568 thioethers Chemical class 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 150000001341 alkaline earth metal compounds Chemical class 0.000 description 1
- 229960000510 ammonia Drugs 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 150000003868 ammonium compounds Chemical class 0.000 description 1
- 239000011260 aqueous acid Substances 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 235000011116 calcium hydroxide Nutrition 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 230000001143 conditioned effect Effects 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 150000002681 magnesium compounds Chemical class 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 150000003112 potassium compounds Chemical class 0.000 description 1
- 230000001172 regenerating effect Effects 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 150000003388 sodium compounds Chemical class 0.000 description 1
- GRVFOGOEDUUMBP-UHFFFAOYSA-N sodium sulfide (anhydrous) Chemical compound [Na+].[Na+].[S-2] GRVFOGOEDUUMBP-UHFFFAOYSA-N 0.000 description 1
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
- B01D53/68—Halogens or halogen compounds
-
- 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
-
- 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
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/77—Liquid phase processes
- B01D53/78—Liquid phase processes with gas-liquid contact
Definitions
- the present invention relates to a method and an apparatus for liquid regulation in the wet cleaning of a gas, and more specifically concerns a method and an apparatus for regulating the amount of liquid in the wet cleaning of a flue gas containing hydrogen chloride and sulphur dioxide and being first wet-cleaned in a scrubber with a view to removing hydrogen chloride and then wet- cleaned with a view to removing sulphur dioxide.
- the gas When wet-cleaned, the gas is brought into contact with a liquid for removing impurities in the gas.
- the wet cleaning takes place in a wet-cleaning apparatus, also referred to as a scrubber or a washer, which operates in one or more stages with liquid as separating medium.
- the liquid In order to achieve a high degree of efficiency in the wet cleaning, the liquid should preferably be finely divided and brought into contact with the gas countercurrently.
- the liquid is often water-based and may con ⁇ tain an agent intended to improve the absorption of impu ⁇ rities in the gas.
- Wet cleaning is especially used for cleaning flue gases, such as flue gases generated upon refuse incinera ⁇ tion.
- flue gases contain, inter alia, hydrogen chlo ⁇ ride and sulphur dioxide, which have to be removed before the flue gases may be discharged into the surrounding atmosphere.
- SE 9300169-1 (Publ. No. 470,565) teaches an instance of the above-mentioned technique for the wet cleaning of flue gases.
- the flue gases are, in a first stage, washed with an aqueous acid washing solution for the absorption of hydrogen chloride and, in a second stage, washed with an aqueous alkaline washing solution for the absorption of sulphur dioxide.
- a partial flow of the acid washing solution is drawn off in the first stage and is regenerated in a secondary cir ⁇ cuit by neutralisation, separation of heavy metals and evaporation with a view to separating sodium chloride.
- a partial flow of the alkaline washing solu ⁇ tion is drawn off in the second stage and is regenerated in a secondary circuit by the addition of lime for the precipitation of gypsum and by the addition of soda for the precipitation of excess calcium.
- SE 9300169-1 is dis ⁇ tinguished by the fact that the washing liquid in the first stage is kept essentially separate from the washing liquid in the second stage, the condensate from the eva ⁇ poration in the secondary circuit of the first stage being recycled to the primary circuit of the first stage, and the fact that use is made of a so-called indirect lime process for regenerating the washing liquid in the secondary circuit of the second stage.
- liquid If liquid is to be removed by being discharged into the surroundings, it first has to be cleaned, for instance by evaporation, which is a costly procedure requiring special equipment. It is also con ⁇ ceivable to eliminate excess liquid in the stage at issue by transferring it to the first stage, which normally has a shortage of liquid owing to the evaporation. For seve ⁇ ral reasons, however, such a transfer of liquid is not without its problems. First, a transfer of liquid from the stage at issue would mean that chemicals dissolved in the liquid were drained from this stage. These chemicals naturally have to be replaced, which would render the cleaning process more expensive. In addition, the chemi- cals may cause problems in the first stage.
- the transfer of, say, dissolved sulphate to the first stage may give rise to scaling problems in the evaporation or distillation of liquid in the first stage.
- there may not be a balance between the first stage and the subsequent stage i.e. it is not absolutely certain that all the excess liquid in the subsequent stage can be transferred to the first stage.
- the invention provides a method for regulating the amount of liquid in the wet cleaning of a gas in at least two stages, said method being char ⁇ acterised in that liquid from at least one of the stages after the first stage is brought into contact with air, such that the liquid is partly evaporated and cooled, the evaporation being carried out to such an extent that the amount of liquid in the stage remains the same, whereupon the remaining liquid is heated before being recycled to said stage.
- the invention further provides an apparatus for regulating the amount of liquid in the wet cleaning of a gas, said apparatus comprising a scrubber having at least two stages and a liquid-circulation circuit in at least one of the stages after the first stage, said apparatus being characterised in that the liquid-circulation cir- cuit includes an evaporator adapted to evaporate liquid to such an extent that the amount of liquid in said stage remains the same and to cool liquid from said circuit by contacting it with air, as well as a heater adapted to heat the cooled liquid in the circuit.
- the gas being wet-cleaned is a flue gas containing hydrogen chloride and sulphur dioxide and being first wet-cleaned with a view to removing hydrogen chloride and then wet-cleaned with a view to removing sulphur dioxide, liquid from the sulphur-dioxide wet cleaning being partly evaporated and cooled, whereupon the remaining liquid is heated before being recycled for renewed sulphur-dioxide wet cleaning.
- the sulphur-dioxide wet cleaning takes place in a primary circuit and a secondary circuit in accordance with the indirect lime process as described in e.g. SE 9300169-1 mentioned above, and that the evaporation and the cooling of liquid take place in the secondary circuit before the liquid is treated with a view to separating absorbed sulphur dioxide, preferably by precipitation.
- heat can be supplied in optional manner to the liquid after the evaporation, it is especially preferred, in accordance with a special aspect of the invention, that heat be supplied by means of heat ex ⁇ change with the liquid in the first stage, i.e. the heat is indirectly taken from the flue gas itself.
- the evaporation can be so controlled that an optional amount of liquid is eva ⁇ porated. If, say, it is desirable that a certain amount of liquid be transferred to the first stage and a certain amount of liquid is in addition drawn off along with the precipitates formed, the evaporated amount of liquid need not correspond to the condensated amount of liquid, but should instead correspond to the condensated amount of liquid minus the transferred and the drawn-off amount of liquid. Regardless of whether liquid is transferred or drawn off, the liquid is, in accordance with the inven ⁇ tion, evaporated to such an extent that the amount of liquid in the stage remains the same.
- the apparatus according to the invention is a scrubber comprising a cleaning stage for hydrogen chloride and at least one cleaning stage for sulphur dioxide, the evaporator being connected to the cleaning stage for sulphur dioxide.
- the sulphur-dioxide cleaning is designed according to the indirect lime process, the evaporator being connected to the secondary circuit before the sepa ⁇ ration of sulphur dioxide, which preferably takes place in form of gypsum precipitation.
- the heater adapted to heat the cooled liquid is a heat exchanger for heat exchange with liquid from the first stage, and that this heat exchanger is disposed after the separation of sulphur dioxide in the secondary circuit.
- the evaporator according to the invention preferably comprises a tower for countercurrent contact between air and finely-divided liquid, the tower having a liquid inlet, a liquid outlet, an air inlet, an air outlet, as well as a fan for feeding the air.
- the evapora ⁇ tor which preferably is a cooling tower, serves not only to evaporate liquid, but also to oxidise the sulphite found in the liquid. In order that the evaporator should be able to perform this double function, the liquid flow, the air flow and the temperature have to be controlled, necessitating the use of a complicated control algorithm with ensuing problems.
- the required conditions can be met with the aid of simpler control algorithms.
- the air flowing through the evaporator is sufficient to enable the above-mentioned sulphite oxidation to be performed.
- the moisture content in the evaporator may be sufficiently high to enable the avoidance of crystalli ⁇ sation in the liquid, and the system can be so dimension ⁇ ed that all temperature and moisture conditions in the supplied air can be controlled.
- Fig. 1 schematically illustrates the method and the apparatus according to the invention when used for wet- cleaning a flue gas in two stages
- Fig. 2 schematically illustrates a preferred embodi ⁇ ment of the invention.
- Fig. 1 shows an apparatus for two-stage wet cleaning of a flue gas which contains, inter alia, impu ⁇ rities in the form of hydrogen chloride and sulphur dioxide.
- the flue gas 1 is conduct ⁇ ed into a quencher 2, where it is brought into contact with an acidic, aqueous washing liquid 3 which is fine ⁇ ly divided by means of spray nozzles 4 as well as spray nozzles 5 in the scrubber 6 itself.
- the washing liquid is circulated with the aid of a pump 7 to the spray nozzles 4 and with the aid of a pump 8 to the spray nozzles 5 via conduits 9 and 10, respectively.
- Fresh washing liquid can be supplied at 11.
- the flue gas 1 When entering the quencher 2, the flue gas 1 is cooled from approximately 150-200°C to approxi- mately 55-60°C by the cooler washing liquid sprayed through the nozzles 4. When the gas is thus cooled, part of the liquid evaporates, and the flue gas is saturated with water vapour. As the flue gas passes through the first stage and is contacted with the finely-divided washing liquid 3, the latter absorbs hydrogen chloride in the gas. The washing liquid containing hydrogen chloride is drawn off at 12 to be further treated and cleaned.
- the flue gas thus rid of hydrogen chloride is then conducted from the first stage to the second stage in the scrubber 6, where it is brought into contact with an alkaline, aqueous washing liquid 13, which is finely divided by means of spray nozzles 14.
- the washing liquid absorbs sulphur dioxide from the flue gas and is then collected and drawn off via a conduit 15 to a storage vessel 16, whence it can be recirculated to the spray nozzles 14 via a conduit 18 with the aid of a pump 17.
- the flue gas conduct ⁇ ed to the second stage is saturated with water vapour. When the flue gas is brought into contact with the cooler washing liquid, moisture in the flue gas is condensed.
- This condensed moisture is, along with the washing liquid, conducted to the storage vessel 16 and thus increases the volume of liquid in the second stage.
- a partial flow is drawn off from the conduit 18 via a con ⁇ duit 19 and is, in accordance with the invention, sup- plied to an evaporator 20.
- Excess water supplied to the washing liquid by condensation from the flue gas in the second scrubber stage is removed in this evaporator 20.
- the water is removed by bringing the washing liquid in the evaporator 20 into intimate contact with air.
- the washing liquid is introduced at the upper part of the evaporator 20 and is distributed over a considerable surface e.g.
- the evaporator is designed in the manner described above, such that part of the air flow through the evaporator is recirculated.
- this is indi ⁇ cated by the recirculation conduit 72.
- the size of the recirculated air flow is regulated with the aid of regu ⁇ lating valves, as indicated by the valves 73 and 74 in Fig. 1.
- the liquid is cooled, so that the liquid drawn off from the evaporator via the conduit 24 is cooler than the liquid supplied to the evaporator via the conduit 19 (approxi ⁇ mately 40"C and approximately 55°C, respectively).
- the washing liquid is rege- nerated by the removal of absorbed sulphur dioxide, which is carried out by precipitating the sulphur dioxide in the form of gypsum (CaS04•2H2O) .
- this regene ⁇ ration treatment is schematically indicated by the box 25.
- Some liquid may be drawn off from the regeneration treatment 25, for instance together with the separated gypsum precipitate, as indicated by the arrow 26.
- the washing liquid is recycled via a conduit 27 in order to be used once again in the wet cleaning of the second scrubber stage. As men- tioned above, the washing liquid has, however, been cool ⁇ ed in the evaporation in the evaporator 20.
- heat is supplied to the cooled washing liquid which thus is reheated by heat exchange in a heat exchanger 28.
- the heat in the heat exchange can be supplied from any suitable source. As illustrated in Fig. 1, it is, however, especially prefer ⁇ red in the invention that the heat is supplied from the washing liquid in the first stage, thus indirectly coming from the flue gas itself. This is carried out by drawing off a partial flow from the conduit 10 and conducting it via conduits 29, 30 through the heat exchanger 28.
- the heat exchange with washing liquid from the first wet- cleaning stage is advantageous in that it not only serves to reheat the washing liquid in the second stage but also to cool the washing liquid in the first stage, which reduces the need of fresh water in the first stage as well as improves the absorption of hydrogen chloride and other acid components in the first stage.
- the cool ⁇ ing of the remaining washing liquid improves the quality of the gypsum subsequently precipitated in the regenera- tion treatment 25, gypsum being stable at temperatures below approximately 40°C.
- a gas 1 containing hydrogen chloride and sulphur dioxide enters, in Fig. 2, a scrubber 6, where it is cleaned of hydrogen chloride in a first stage.
- the gas is brought into contact with an aqueous, acid washing liquid 3 sprayed through spray nozzles 5.
- the washing liquid 3 is circulated in a primary cir ⁇ cuit 31 from the scrubber 6 to the spray nozzles 5 via conduits 32 and 33.
- a partial flow of washing liquid is drawn off from the primary circuit 31 and conducted, via a conduit 34, to a secondary circuit 35 comprising a con ⁇ tainer 36 for neutralisation with the aid of soda ( a2C ⁇ 3), which is added to the liquid, as indicated by the arrow 37.
- the partial flow of washing liquid is conducted to a container 38, where sodium sulphide is added, as indicated by the arrow 39, with a view to precipitating heavy-metal impurities in the form of sulphides.
- the thus-precipitated heavy-metal sulphides are separated in a container 40 in the form of a sludge that is removed, as indicated by the arrow 41.
- the partial flow of washing liquid is conducted to an evaporation plant 42.
- the condensate obtained upon the evaporation is, via a conduit 43 and a heat exchanger 44, conducted to the primary circuit 31 of the first stage.
- sodium chloride crystallises and is separated at 45, for example by centrifugation or filtration.
- the thus-sepa ⁇ rated sodium chloride is recovered in the form of a pro ⁇ duct, as indicated by the arrow 46.
- the mother liquor obtained upon the separation of sodium chloride can be conducted directly back to the vessel 36 via a conduit 47.
- the mother liquor is first treated by being, via a conduit 49 and in a container 48, joined with a partial flow from the secondary circuit of the sulphur-dioxide cleaning.
- This partial flow contains sulphate and chlorides.
- sodium sulphate is precipitated in the form of Glauber salt, which is separated and, via the conduit 50, is recycled to the secondary circuit of the sulphur- dioxide cleaning.
- the purpose of thus feeding a partial flow from the secondary circuit of the sulphur-dioxide cleaning to the secondary circuit of the hydrogen-chlo ⁇ ride cleaning is to avoid an accumulation of chlorides in the washing liquid in the second stage. Even if the main part of the hydrogen chloride in the gas 1 is absorbed in the first stage in the scrubber 6, a residual amount of hydrogen chloride normally remains and is absorbed in the second stage of the scrubber (the sulphur-dioxide clean ⁇ ing stage).
- the above-mentioned preferred drawing-off of the partial flow from the secondary circuit of the sul ⁇ phur-dioxide cleaning is insignificant as to volume and constitutes but a per cent or so of the flow in the secondary circuit.
- the sulphur-dioxide cleaning which now will be described, consists of a so-called indirect lime process which, for example, may be designed as described in SE 9300169-1.
- a container 13 holds an aqueous, alkaline washing solution which to begin with, i.e. before the absorption of sulphur dioxide, consists of an alkaline aqueous solu ⁇ tion of an easily-soluble alkali, such as an easily- soluble alkali metal compound; an easily-soluble alkaline earth metal compound, such as a magnesium compound; ammo- nia; or an ammonium compound.
- an easily-soluble alkali use is preferably made of an easily-soluble alkali metal compound, such as an easily-soluble sodium or potassium compound. Using a sodium compound, such as sodium hydroxide (NaOH), is most preferred.
- the alkaline washing liquid is circulated in a primary circuit 51 through a conduit 18 to spray nozzles 14, through which the alkaline washing liquid is finely divided and brought into contact with the gas containing sulphur dioxide.
- the washing liquid absorbs sulphur dioxide and is then collected and recycled to the container 13 via a conduit 15. The gas thus rid of sulphur dioxide leaves at 52.
- the washing liquid is, in accordance with the invention, treated with a view to removing excess water having condensed in the second stage, i.e. the sulphur-dioxide cleaning stage, in the scrubber 6.
- the partial flow of wash ⁇ ing liquid in the conduit 19 is conducted to an evapora ⁇ tor 20 which, at the bottom, has a liquid supply 54, whence liquid can be supplied with the aid of a pump 55 to spray nozzles 56 and in a tower 57 be distributed over packing 58, thereby to achieve a considerable contact surface for the liquid.
- the evaporator 20 includes a suction fan 23 which sucks in air through louvres 59 in the lower part of the evaporator, whereupon the air is drawn upwards through the tower 57 and brought into intimate contact with the liquid flowing downwards.
- evaporator 20 shown in Fig. 2 may be designed to recirculate part of the air flow, as has been described in the foregoing as well as illustrated in connection with Fig. 1.
- the regeneration treatment chiefly amounts to the separation of absorbed sulphur dioxide in the form of gypsum (CaS04 • 2H2O) and the restoration of the alkali content of the washing liquid.
- the absorbed sulphur dioxide should be oxidised and be pre ⁇ sent in the form of sulphate ions.
- this prior-art air treatment does not correspond to the inventive treat ⁇ ment in the evaporator 20.
- the prior-art air treatment has only resulted in the oxidation of absorbed sulphur dioxide, which preferably has been carried out by introducing air in the form of bubbles into the liquid via nozzles, there being no evaporation of the liquid
- the inventive treatment involves an evaporation of liquid in the evaporator 20, causing liquid to be eliminated and the remaining liquid to be cooled.
- oxi- disable components of the liquid are oxidised.
- the evapo- ration according to the invention requires a considerable contact surface and a considerable contact time, as well as a high flow ratio of air to liquid. All in all, it should be emphasised that the evaporation treatment according to the invention bears no comparison with the oxidation treatment of the prior art.
- the remaining washing liquid is conducted to a container 62 via the conduit 61.
- calcium ions are added, as indicated by the arrow 63, preferably in the form of lime, for in ⁇ stance burnt lime (CaO) or, which is most preferred, slaked lime (Ca(0H)2).
- CaO in ⁇ stance burnt lime
- Ca(0H)2 slaked lime
- part of the sulphate content of the partial flow is precipitated as gypsum, which is left to sediment in a container 64 and then is separated, as indicated by the arrow 65.
- the thus-separated gypsum is dewatered and may, for instance, be used for producing gypsum board.
- the partial flow of washing liquid is con ⁇ ducted further in the secondary circuit to a container 66, where a minor amount of carbonate, preferably soda (Na2C ⁇ 3), is added, as indicated by the arrow 67.
- a minor amount of carbonate preferably soda (Na2C ⁇ 3)
- Na2C ⁇ 3 soda
- the thus-sedi ented precipitate is removed from the container 68 and recycled to the con ⁇ tainer 62 via a conduit 69.
- the partial flow of alkaline washing liquid thus rid of absorbed sulphur dioxide and regenerated with respect to its NaOH content, is then recycled via a conduit 70 to the container 13 for washing liquid in the primary circuit 51.
- the regenerated washing liquid is, in accordance with the invention, heated in the heat exchanger 44 through heat exchange with hot condensate from the secondary circuit 35 of the first stage, i.e. heat from the liquid in the first stage is used for heating the cooled washing liquid in the second stage.
- heat from the liquid in the first stage is used for heating the cooled washing liquid in the second stage.
- the heating of the cooled washing liquid in the second stage constitutes an important aspect of the invention, and even if the heat required for this purpose need not necessarily be taken from the washing liquid in the first stage, it is nevertheless especially preferred to do so, since it reduces the need of fresh water in the first stage and improves the absorption of hydrogen chlo ⁇ ride and other acid substances in the first stage.
- the drawing-off of liquid from the second stage such as the drawing- off of liquid from the secondary circuit of the second stage via the conduit 71
- the drawing-off of liquid from the second stage was in the prior art condition ⁇ ed by the increase in the amount of liquid due to the condensation in the second scrubber stage
- the drawing-off of liquid from the second stage may therefore be optional and instead be condition ⁇ ed by the salt concentration in the second stage, i.e. the need of removing salts, such as chlorides, from the second stage.
- this reduction according to the invention involves a highly significant sulphate reduction, which is of great impor- tance in plants having no separation of Glauber salt of the type shown in Fig. 2, since this reduces the risk of scaling.
- the amount of liquid drawn off, and hence the sulphate concentration may in accordance with the invention be reduced to such a level that the sul- phate concentration becomes subcritical, i.e. is well below the limit of approximately 1,000 mg/1 required for the precipitation of gypsum. It thus becomes possible to completely eliminate the difficult scaling problems pre ⁇ viously associated with the transfer of drawn-off liquid from the second stage to the first stage.
- a plant which generates approximately 100,000 Nm.3 of flue gas/h having a sulphur-dioxide con ⁇ centration of approximately 500 mg/h and a hydrogen-chlo- ride concentration of approximately 1,000 mg/h, yields approximately 700 1 of condensate/h in the second scrub ⁇ ber stage (the cleaning stage for sulphur dioxide) .
- a corresponding amount of liquid would have to be drawn off from the second stage which, when the indirect lime process is used in the second stage, would involve a chemical loss (of sodium sulphate) of approximately 40 kg/h.
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- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Treating Waste Gases (AREA)
- Gas Separation By Absorption (AREA)
- Separation Of Particles Using Liquids (AREA)
Abstract
Description
Claims
Priority Applications (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
EP95939456A EP0794825A1 (en) | 1994-11-28 | 1995-11-24 | Method and apparatus for liquid regulation in wet cleaning of a gas |
JP8517171A JP3009474B2 (en) | 1994-11-28 | 1995-11-24 | Method and apparatus for liquid conditioning in wet gas purification |
AU41265/96A AU4126596A (en) | 1994-11-28 | 1995-11-24 | Method and apparatus for liquid regulation in wet cleaning of a gas |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
SE9404101A SE504408C2 (en) | 1994-11-28 | 1994-11-28 | Methods and apparatus for fluid control in wet cleaning of a gas |
SE9404101-9 | 1994-11-28 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO1996016721A1 true WO1996016721A1 (en) | 1996-06-06 |
Family
ID=20396121
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/SE1995/001404 WO1996016721A1 (en) | 1994-11-28 | 1995-11-24 | Method and apparatus for liquid regulation in wet cleaning of a gas |
Country Status (5)
Country | Link |
---|---|
EP (1) | EP0794825A1 (en) |
JP (1) | JP3009474B2 (en) |
AU (1) | AU4126596A (en) |
SE (1) | SE504408C2 (en) |
WO (1) | WO1996016721A1 (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0798031A1 (en) * | 1996-03-29 | 1997-10-01 | Constructions Industrielles De La Mediterranee- Cnim | Process and device for treating flue gases |
WO1998016302A1 (en) * | 1996-10-17 | 1998-04-23 | ABB Fläkt AB | Method and apparatus for treating flue gas |
WO1998053900A1 (en) * | 1997-05-26 | 1998-12-03 | Boliden Contech | A method and apparatus for removing gaseous elementary mercury from a gas |
EP0930091A4 (en) * | 1997-04-25 | 2000-09-27 | Nippon Kokan Kk | PROCESS FOR THE TREATMENT OF GASEOUS EMANATIONS |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4366133A (en) * | 1981-06-01 | 1982-12-28 | Combustion Engineering, Inc. | Process for limiting chloride buildup in SO2 scrubber slurry |
SE429200B (en) * | 1978-10-31 | 1983-08-22 | Flaekt Ab | PROCEDURE FOR RECOVERY OF SODIUM CITRATE FROM WATER SOLUTIONS USED IN AN ABSORPTION / DRIVING PROCEDURE FOR SO? 712 RECOVERY |
EP0277246A1 (en) * | 1986-07-31 | 1988-08-10 | Chiyoda Chemical Engineering & Construction Company Limited | Wet-process stack gas purification method and apparatus |
SE470565B (en) * | 1993-01-21 | 1994-08-29 | Flaekt Ab | Method and apparatus for purifying hydrocarbon and sulfur dioxide containing gases |
-
1994
- 1994-11-28 SE SE9404101A patent/SE504408C2/en not_active IP Right Cessation
-
1995
- 1995-11-24 WO PCT/SE1995/001404 patent/WO1996016721A1/en not_active Application Discontinuation
- 1995-11-24 EP EP95939456A patent/EP0794825A1/en not_active Ceased
- 1995-11-24 AU AU41265/96A patent/AU4126596A/en not_active Abandoned
- 1995-11-24 JP JP8517171A patent/JP3009474B2/en not_active Expired - Fee Related
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
SE429200B (en) * | 1978-10-31 | 1983-08-22 | Flaekt Ab | PROCEDURE FOR RECOVERY OF SODIUM CITRATE FROM WATER SOLUTIONS USED IN AN ABSORPTION / DRIVING PROCEDURE FOR SO? 712 RECOVERY |
US4366133A (en) * | 1981-06-01 | 1982-12-28 | Combustion Engineering, Inc. | Process for limiting chloride buildup in SO2 scrubber slurry |
EP0277246A1 (en) * | 1986-07-31 | 1988-08-10 | Chiyoda Chemical Engineering & Construction Company Limited | Wet-process stack gas purification method and apparatus |
SE470565B (en) * | 1993-01-21 | 1994-08-29 | Flaekt Ab | Method and apparatus for purifying hydrocarbon and sulfur dioxide containing gases |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0798031A1 (en) * | 1996-03-29 | 1997-10-01 | Constructions Industrielles De La Mediterranee- Cnim | Process and device for treating flue gases |
WO1998016302A1 (en) * | 1996-10-17 | 1998-04-23 | ABB Fläkt AB | Method and apparatus for treating flue gas |
US6562303B1 (en) | 1996-10-17 | 2003-05-13 | Alstom Power Sweden Holding Ab | Method and apparatus for treating flue gas |
EP0930091A4 (en) * | 1997-04-25 | 2000-09-27 | Nippon Kokan Kk | PROCESS FOR THE TREATMENT OF GASEOUS EMANATIONS |
WO1998053900A1 (en) * | 1997-05-26 | 1998-12-03 | Boliden Contech | A method and apparatus for removing gaseous elementary mercury from a gas |
EA000771B1 (en) * | 1997-05-26 | 2000-04-24 | Булиден Контех Аб | A method and apparatus for removing gaseous elementary mercury from a gas |
CZ298739B6 (en) * | 1997-05-26 | 2008-01-16 | Boliden Contech Ab | Method for removing gaseous elementary mercury from gas and apparatus for making the same |
Also Published As
Publication number | Publication date |
---|---|
SE9404101L (en) | 1996-05-29 |
JP3009474B2 (en) | 2000-02-14 |
SE504408C2 (en) | 1997-02-03 |
AU4126596A (en) | 1996-06-19 |
EP0794825A1 (en) | 1997-09-17 |
SE9404101D0 (en) | 1994-11-28 |
JPH10500065A (en) | 1998-01-06 |
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