A PROCESS OF CLEANING FLUE GASES FROM HEATING PLANTS,AND A CLEANING PLANT FOR CARRYING OUT THE PROCESS

Abstract: By a process of cleaning flue gases, both solid particles and nitrogen oxides and sulphur dioxide are removed from the flue gas prior to the discharging into the atmospheric air. In order to ensure that almost all the content of sulphur dioxide and nitrogen oxides is removed from the flue gas, said flue gas is initially carried through a rain of aqueous liquid and subsequently through a heat exchanger, in which its temperature is lowered at about 20-30`C, and then through a film of alkaline liquid, and finally through a second rain of aqueous liquid to pass a sulphuric acid neutralizing liquid in a container before the discharging into the atmospheric air. As a result a simultaneous possibility of utilizing the heat of the flue gas is ensured by means of the heat exchanger. A cleaning plant for carrying out the process comprises an apparatus (2), through which the flue gas cleaned of solid particles is carried. When seen in the flow direction, this apparatus comprises a first flue scrubber (8), in which the flue gas is subjected to a rain of liquid, a two-step heat exchanger (9, 10) permitting a reduction of the temperature of the flue gas to 20-30`C. After the two-step heat exchanger (9, 10), the apparatus (2) comprises a rotating, conical disc (11) providing a film of milk of lime, through which the flue gas is forced to pass during the continuous flow through the apparatus. After this film of milk of lime, the flue gas passes a rain of liquid emitted from a second flue scrubber (14), and upon said scrubber the flue gas is forced to pass a limy liquid in a container (15).

Description: Title: A Process of Cleaning Flue Gases From Heating Plants, and a Cleaning Plant for Carrying Out the Process. Technical Field The invention relates to a process of cleaning flue gases from heating plants such as oil burners , whereby it is substantially ensured that solid particles such as fly ash are initially removed from the flue gas , whereafter nitrogen oxides and sulphur dioxide are re- moved from the flue gas prior to the discharging to the atmospheric air, optionally through a neutralizing device. The in¬ vention __urthermore relates to a plant for carrying out the process. Background Art It is known to clean flue gases both of solid particles and of nitrogen oxides and sulphur dioxide, as well as it is known to utilize the heat of the flue gas. The previously known plants ensure a reduction of about 90% of the amount of sulphur dioxide in the flue gas. The remaining amount of sulphur dioxide implies that the flue discharged into the atmospheric air is particularly aggressive, said flue usually being discharged at a temp¬ erature of about 60-70°C. Disclosure of Invention The object of the invention is to provide a process en- suring a reduction of the amount of sulphur dioxide of 98-100% at the same time as the flue is cooled almost to room temperature. The process according to the invention is characterised in that initially the flue gas cleaned of solid particles is carried through an optionally intermittent, firs _^3>rg of aqueous liquid, subsequently through a heat exchanger, in which the temperature of the flue gas is reduced to about 2O-30°C, optionally through a film of an alkaline liquid such as milk of lime or chloride of lime, through a second rain of aqueous liquid, and finally through a sulphuric acid neutralizing liquid in a container prior to the exhaust to the atmospheric air or an additional neutralizing device. As a result, the discharged flue is cleaned to such an extent that it is comparable with the atmospheric air as to the content of combustion gases. The content of sulphur dioxide and sulphuric acid is almost com¬ pletely removed, i.e. only from 0 to 2% thereof remain. Only a small amount of nitrogen and carbon dioxide re- main, and the result of the cleaning is that the expen¬ ses involved in building large chimneys are completely avoided. At the same time the heat of the flue gas can be completely utilized as low as to 20-30 C for heating purposes since a temperature of at least about 150 C to 160 C in the flue gas is no longer required during the passage of said flue gas through a chimney. This high temperature was necessary in connection with the pre¬ vious plants in order to ensure that the content of sulphuric acid of the flue gas did not turn aggressive within the chimney. This effect is due to a co-opera¬ tion of the various liquids and the great reduction of the temperature which the flue gas is subjected to. A reduction of the temperature of the partly cleaned flue gas after the first treatment with a rain of aqueous liquid involves an intensely accelerating effect con¬ cerning the conversion of S0_ - SO, into H-SO.. and H_S0.. The film with alkaline liquid ensures a neutra¬ lization of the previously formed H-SO. and an oxida¬ tion of present nitrogen oxides. The later rain of aqueous liquid ensures a conversion of the remaining amounts of S0 2 and SO3 into H2SO3 and H2ΞO4 being re- moved during the passage through the sulphuric acid neu¬ tralizing liquid in a container before the discharging into the atmospheric air. As an additional security mea¬ sure, the flue gas cleaned may optionally pass through an additional neutralizing device. The low temperature of the cooled flue gas ensures an essential increase of the capacity of the sulphur dioxide of being absorbed in the amount in question of aqueous liquid. By a usual liquefaction of sulphur dioxide at O C with water, the dissolving or absorbing is carried out with the follow¬ ing ratios, viz. 1 part of water to 80 parts of S0 2 , and each time an increase of temperature of 20 C takes place, the number of parts of SO_ is halved. The present 20-30 C of the flue gas thus implies that considerably higher amounts of SO- can be absorbed by the aqueous liquid than in the previously known plants, whereby the consumption of aqueous liquid is relatively low compared to usual scrubbers operating at temperatures of about 70 C to 80 C. The heat exchanger permits heating of for instance water for district heating or of boiler water, as well as a preheating of air for combustion. The preheating of the air for combustion improves the combustion, said combus¬ tion being improved by 1.4% per 10 increase of the temp¬ erature of the air for the combustion. The loss of heat from the plant is thereby very low compared to the loss occurring in connection with plants with chimneys. The lower amount of necessary liquid renders it possible to make the plant necessary for carrying out the process very small and compact. Furthermore, the higher efficien- 3 cy per m of flue gas and the efficient utilization of the heat reduce the working expenses. According to the invention the flue gas may together with the first rain of liquid be carried in a substantially vertical direction downwards through the heat exchanger until it is contacted with the film of alkaline and the second rain of liquid. As a result it is possible to utilize the gravity efficiently and to obtain a par¬ ticularly good heat transition to the heat exchanger. Furthermore according to the invention, the liquid of the first and the second rain of aqueous liquid may be a mix¬ ture of water and hydrogen peroxide, whereby a particu¬ larly efficient oxidation of the sulphur dioxide into the sulphur trioxide is ensured. According to the invention it is particularly preferred that the second rain of liquid is emitted in a direction opposite the flow direction of the gas. The invention furthermore relates to a cleaning plant for carrying out the process, and this cleaning plant comprises an apparatus, in which it is ensured that solid particles such as fly ash are removed from the flue gas, and an apparatus for the removal of nitrogen oxides and sulphur dioxide from the flue gas, the latter apparatus optionally being coupled to a neutralizing device. This cleaning plant is according to the inven- tion characterised in that the apparatus for the removal of nitrogen oxides and sulphur dioxide, when seen in the flow direction, comprises a first flue scrubber subject¬ ing the passing flue gas to a rain of liquid, a two-step heat exchanger lowering the temperature of the flue gas to 20-30 C and comprising both a high temperature heat exchanger and a low temperature heat exchanger, whereby said high temperature heat exchanger is adapted to trans¬ fer heat from the flue gas to water such as boiler water or district heating water, and whereby said low tempera- ture heat exchanger is adapted to transfer heat from the flue gas to air supplied to the combustion, that after the two-step heat exchanger means are located for spreading a film of supplied alkaline liquid such as milk of lime or chloride of lime across the apparatus on O PI the place in question, and that a second flue scrubber is provided after these means, said second flue scrubber spraying a rain of liquid on the passing flue gas, and that the apparatus for the removal of nitrogen oxides and sulphur dioxide at the discharge end comprises a contain¬ er provided with outlets and catching the liquid from the flue scrubbers and the means, and in which the flue gas is forced to pass the liquid present in the contain¬ er before the discharging. This cleaning plant operates particularly efficiently and when employing appropriate sensors and regulating means, a very reliable control of this plant is rendered possible. In this connection it is noted that the flue gas being treated as mentioned initially is cleaned of solid particles such as fly ash. This cleaning may be performed in many various manners, • e.g. by means of a particle-separating apparatus in the form of a multi- cyclon or filters. In case of oil heating, the particle- separating apparatus may be replaced by an emulsion plant located before the oil burner. In this emulsion plant, the water is in a manner known per se emulsified in the oil in such a manner that the surface tension of the oil is changed, and a usual drop of oil is changed into about lO to 20 small drops of oil within the burner. In this manner a better division into fine particles of the oil during the combustion is obtained, which implies that all carbon particles disappear from the flue gas and an optimum combustion is obtained. According to the invention the high temperature heat ex- changer may be adapted to cause a reduction of the temp¬ erature of the flue gas to about 70-80 C, and the low temperature heat exchanger may be adapted to cause an additional reduction of the temperature of the flue gas to about 20-30°C, whereby a particularly efficient uti- lization of the heat is obtained. Finally according to the invention, the first flue scrubber, the two-step heat exchanger, the means, and the second flue scrubber may be located successively and substantially vertically on top of each other with the first flue scrubber at the top, whereby the plant is particularly compact. Brief Description of Drawing The invention will be described below with reference to the accompanying drawing, in which Fig. 1 is a diagrammatic view of a large flue gas clean- ing plant for carrying out the process according to the invention, and Fig. 2 on a larger scale is a sectional view through part of the plant of Fig. 1. Best Mode for Carrying Out the Invention The flue gas cleaning plant illustrated in Fig. 1 shows in succession a particle-separating apparatus 1, an appa¬ ratus 2 for the removal of sulphur dioxide and nitrogen oxides as well as for utilization of the heat of the flue gas, a neutralizing device 3, and a drop collector 4 such as a cyclon drop collector. Fromthis drop collector, the flue gas flows directly into the atmosphere. The neutralizing device or optionally only the bottom of the apparatus 2 is downwardly connected to a separation appa¬ ratus 5 in which the milk of lime used within the neutra- lizing device and co-operating in neutralizing the sul¬ phuric acid in the flue gas, is separated from CaSO. in a generally known manner. The hydrated calcium sulphate is discharged whereas the remaining milk of lime is re¬ turned through a pipe 6 for use in the cleaning plant, optionally during addition of fresh milk of lime. In the illustrated embodiment, the bottom of the apparatus 2 -£!JRE OMP communicates as mentioned with the neutralizing device 3 through a pipe 7 , whereby liquid collected at the bottom of the apparatus 2 can flow into the neutralizing device 3. Since it is only as a security measure that the plant according to the invention may be coupled to a neutralizing device, the connection 7 may be adapted to carry liquid directly downwards to the separation apparatus 5, which is a generally known type too such as a separator. The drop collector 4 removes possible residues of milk of lime from the cleaned flue gas prior to the discharging into the atmosphere. As illustrated in Fig. 2, which is a vertical, section¬ al view through the apparatus 2 for the removal of sul¬ phur dioxide and nitrogen oxides and for the utilization of the heat of the flue gas, the flue gas flowing from the particle-separating apparatus is contacted with a first flue scrubber at the inlet of the apparatus 2. This first flue scrubber is followed by a two-step heat exchanger comprising a high temperature heat exchanger 9 and a low temperature heat exchanger 10. A short distance below the low temperature heat exchanger 10, a conical disc 11 of a generally known type is located, and which by means of an electromotor 12 is caused to rotate. Immediately above the centre of this conical disc 11, a pipe 13 ends for the supply of an alkaline liquid such as milk of lime or chloride of lime to the rotating disc 11. The apparatus 2 ends in a container- forming bend 15 receiving liquid from the two flue scrubbers and the rotating disc. Since this part of the apparatus 2 forms a bend, the flue gas is at an appro¬ priately regulated liquid level forced to flow through the liquid collected in said bend before it flows but through the outlet 16 of the apparatus. As illustrated, the container-forming bend 15 is downwardly provided with outlets for the liquid collected, which is carried away through the previously mentioned pipe 7. The two OMPI flue scrubbers 8 and 14 are of any appropriate type adapted to spray a rain of water containing hydrogen peroxide on the passing flue gas, the flow direction of said flue gas everywhere being indicated by means of substantially vertical arrows. The first flue scrubber 8 furthermore sprays the rain of liquid on the low tempera¬ ture heat exchanger, and together with the flue gas said liquid gives off heat to the water passing through a pipe system into a boiler or a district heating. Before the flowing into the apparatus 2, the flue gas has a temperature of 200-260°C, and upon passage through the high temperature heat exchanger said flue gas has a temp¬ erature of 70-80 C whereby the temperature of the water within the heat exchanger has risen to 95-105 C. After the high temperature heat exchanger, the liquid and the flue gas are contacted with the low temperature heat exchanger preferably present in the form of a large num¬ ber of transverse glass tubes preferably made of Pyrex glass^stand¬ ing up to high temperatures and sulphuric acid. Atmosphe- ric air passes these glass tubes at 10-25 C, and during the passage through the heat exchanger the temperature of said air is risen to 45-55 C, whereby it is suited for use as air for the combustion. Having passed the low temperature heat exchanger, the temperature of the flue gas is 20-30 C, and between the rotating disc and the wall 17 of the apparatus here being funnel-shaped, the flue gas is contacted with a film of milk of lime or chloride of lime emitted from the rotating disc so as immediately thereupon to be contacted with the rain of liquid from the second flue scrubber 14. During the passage of the flue gas through the upper portion of the apparatus 2, i.e. the portion comprising the first flue scrubber 8 and the high temperature heat exchanger 9, part of the sulphur dioxide content is con- tacted with the water from the "flue scrubber and convert¬ ed into H2SO3, whereas other parts of the sulphur dioxide OM are oxidized by the hydrogen peroxide into S0_ and sub¬ sequently converted into H-SO, during the contact with the water. The water of the flue scrubber simultaneous¬ ly ensures a continuous rinsing of the two heat exchan- gers. During the passage of the flue gas through the por¬ tion of the apparatus 2 comprising the low temperature heat exchanger 10, the temperature of said flue gas is as mentioned lowered to about 20-30 C. At this tempera¬ ture the capacity of the water of absorbing sulphur dioxide is intensely increased compared to the capacity thereof at higher temperatures. At 20 C, 40 volumes of S0„ are dissolved in one volume of water. At the present temperatures, a high degree of dissolving is therefore ensured though the water consumption is very small. At the contact of the flue gas with the film of milk of lime or the like, a considerable part of the sulphuric acid now present in the flue gas is neutralized, as well as the present part of nitrogen is catched and oxidized. During the further flow of the flue gas past the second flue scrubber 1 , the remaining amounts of SO- and SO., are catched and oxidized and converted into H.-S0.. In the container-forming bend 15 of the apparatus, the flue gas is subsequently forced into intense contact with the limy liquid present therein, said liquid neu- tralizing the remaining residues of H-SO.. Subsequently, the flue gas flows out of the apparatus 2 through the outlet 16 , and in this place the flue gas only comprises from 0 to about 2% of sulphur dioxide. This unusually low amount of sulphur dioxide can, if desired, be addi- tionally reduced by means of the neutralizing device illustrated in Fig. 1. The invention has been described with reference to a preferred embodiment. Many modifications may be perform¬ ed without thereby deviating from the scope of the in- vention. The hydrogen peroxide used in the two flue scrubbers is a 3% hydrogen peroxide. The operation and OMPI lO capacity of the individual members such as the flue scrubbers and the rotating disc are adjusted in an appropriate manner by means of sensors and regulating means not shown. The rotating disc may be replaced by other means for spreading an alkaline liquid.

Claims: Claims ; 1. A process of cleaning flue gases from heating plants such as oil burners, whereby it is substantially ensured that solid particles such as fly ash are initi- ally removed from the flue gas, whereafter nitrogen oxides and sulphur dioxide are removed from the flue gas prior to the discharging to the atmospheric air, optionally through a neutralizing device, c h a r a c ¬ t e r i s e d in that initially the flue gas cleaned of solid particles is carried through an optionally in¬ termittent, first rain of aqueous liquid, subsequently through a heat exchanger (9, 10), in which the tempera¬ ture of the flue gas is reduced to about 20-30 C, op¬ tionally through a film of an alkaline liquid such as milk of lime or chloride of lime, through a second rain of aqueous liquid, and finally through a sulphuric acid neutralizing liquid in a container prior to the exhaust to the atmospheric air or an- additional neutra¬ lizing device (3) . 2. A process as claimed in claim 1, c h a r a c ¬ t e r i s e d in that the flue gas together with the first rain of liquid is carried in a substantially ver¬ tical direction downwards through the heat exchanger un¬ til it is contacted with the film of alkaline liquid and the second rain of liquid. 3. A process as claimed in claim 1 or 2, c h a r a c t e r i s e d in that the liquid of the first and the second rain of aqueous liquid is a mixture of water and hydrogen peroxide. . A process as claimed in claim l, 2 or 3, c h a r ¬ a c t e r i s e d in that the second rain of liquid is emitted in a direction opposite the flow direction of the gas. OMH 5. A cleaning . plant for carrying out the process ac¬ cording to the invention and comprising an apparatus (1) , in which it is ensured that solid particles such as fly ash are removed from the flue gas, and an apparatus (2) for the removal of nitrogen oxides and sulphur dioxide from the flue gas, the latter apparatus optionally being coupled to a neutralizing device (3), c h a r a c t e r ¬ i s e d in that the apparatus (2) for the removal of nitrogen oxides and sulphur dioxide, when seen in the flow direction, comprises a first flue scrubber (8) sub¬ jecting the passing flue gas to a rain of liquid, a two- step heat exchanger lowering the temperature of the flue gas to 20-30 C and comprising both a high temperature heat exchanger (9) and a low temperature heat exchanger (10) , whereby said high temperature heat exchanger (9) is adapted to transfer heat from the flue gas to water such as boiler water or district heating water, and whereby said low temperature heat exchanger (10) is adapt¬ ed to transfer heat from the flue gas to air supplied to the combustion, that after the two-step heat exchanger (9, 10) means (11) are located for spreading a film of supplied alkaline liquid such as milk of lime or chlor¬ ide of. lime across the apparatus on the place in question, and that a second flue scrubber " (14) is provided after these means (11) , said second flue scrubber spraying a rain of liquid on the passing flue gas, and that the apparatus for the removal of nitrogen oxides and sulphur dioxide at the discharge end comprises a container pro¬ vided with outlets (7) and catching the liquid from the flue scrubbers and the means (11) , and in which the flue gas is forced to pass the liquid present in the container before the discharging. 6. A cleaning plant as claimed in claim 5, c h a r a c¬ t e r i s e d in that the liquid sprayed within the first and the second flue scrubber is water, to which an oxygen- ating agent such as hydrogen peroxide is added. 7. A cleaning plant as claimed in claim 5 or 6, c h a r a c t e r i s e d in that the second flue scrubber (14) sprays its liquid in a direction opposite the flow direction of the flue gas. 8. A cleaning plant as claimed in claim 5, 6 or 7, c h a r a c t e r i s e d in that the high temperature heat exchanger is adapted to cause a reduction of the temperature of the flue gas to about 70-80 C, and that the low temperature heat exchanger is adapted to cause an additional reduction of the temperature of the flue gas to about 20-30°C. 9. A cleaning plant as claimed in claim 5, c h a r ¬ a c t e r i s e d in that the means (11) for spreading alkaline liquid comprise a rotating disc. 10. A cleaning plant as claimed in claim 5, 6, 7, 8 or 9, c h a r a c t e r i s e d in that the first flue scrubber (8) , the two-step heat exchanger (9, 10) , the means (11) , and the second flue scrubber (14) are lo- cated- successively and substantially vertically on top of each other with the first flue scrubber (8) at the top.

Inventors: ANDERSSON FINN
Applicants: ANDERSSON FINN, RODSGAARD JES MATHIAS
Application year: 1981
Main classification: B01D53
IPC codes: B01D53