Air pollution control system and method

Abstract

SO.sub.x removal equipment for reducing sulfur oxides from flue gas from a boiler, a cooler which is provided on a downstream side of the SO.sub.x removal equipment for reducing the sulfur oxides that remain in the flue gas and for decreasing a gas temperature, CO.sub.2 recovery equipment which includes a CO.sub.2 absorber, and an absorption liquid regenerator, and mist generation material reduction equipment for reducing a mist generation material which is a generation source of mist that is generated in the CO.sub.2 absorber of the CO.sub.2 recovery equipment before introducing the flue gas to the CO.sub.2 recovery equipment are included.

Claims

1. A preventing method of scattering of a CO.sub.2 absorption liquid from a CO.sub.2 absorber comprising: a NO.sub.x removal step of reducing nitrogen oxides (NO.sub.x) in the flue gas by using a NO.sub.x removal equipment; an air heating step of heating air supplied to a boiler with the flue gas by using an air heater; a SO.sub.x removal step of reducing sulfur oxides (SO.sub.x) in the flue gas; after the SO.sub.x removal step, a cooling step of decreasing a gas temperature of the flue gas while reducing the sulfur oxides that remain in the flue gas; and after the cooling step, a CO.sub.2 recovery step of introducing the flue gas into a CO.sub.2 absorber and bringing the flue gas into contact with a CO.sub.2 absorption liquid to recover CO.sub.2, wherein the preventing method further comprising: prior to the CO.sub.2 recovery step, a mist generation material reduction step of reducing a mist generation material, the mist generation material being contained in the flue gas and having a property of incorporating the CO.sub.2 absorption liquid thereinto in the CO.sub.2 absorber to generate mist that contains the CO.sub.2 absorption liquid; and prior to the SO.sub.x removal step, a dust collecting and reducing step of reducing dust in the flue gas, and wherein the mist generation material reduction step is performed prior to the dust collecting and reducing step, and at the mist generation material reduction step, sodium bisulfate is injected to the flue gas between the NO.sub.x removal equipment and the air heater and downstream of the air heater, and an additional mist generation material reduction step of reducing the mist generation material is performed by reducing the mist generation material with a wet type electric dust collector at the cooling step and including a finishing SO.sub.x removal step of further reducing the sulfur oxides (SO.sub.x) remaining in the flue gas with a finishing SO.sub.x removal unit and a cooling step of decreasing the gas temperature of the flue gas with a cooling unit, wherein the wet type electric dust collector is provided between the finishing SO.sub.x removal unit and the cooling unit.

2. The preventing method according to claim 1, wherein the mist generation material contains SO.sub.3.

3. The preventing method according to claim 1, wherein the dust collecting and reducing step is performed by using a dry type electric dust collector.

Description

BRIEF DESCRIPTION OF DRAWINGS

(1) FIG. 1 is a schematic diagram of an air pollution control system of an embodiment according to the present invention.

(2) FIG. 2 is a conceptual diagram of a mechanism of mist generation.

(3) FIG. 3-1 is a photograph illustrating a state where white smoke is decreased in a CO.sub.2 absorber.

(4) FIG. 3-2 is a photograph illustrating a state where white smoke is generated in the CO.sub.2 absorber.

(5) FIG. 4-1 is a schematic diagram of an air pollution control system according to Embodiment 1.

(6) FIG. 4-2 is a schematic diagram of another air pollution control system according to Embodiment 1.

(7) FIG. 5 is a schematic diagram of an air pollution control system according to Embodiment 2.

(8) FIG. 6 is a schematic diagram of an air pollution control system according to Embodiment 3.

(9) FIG. 7 is a schematic diagram of an air pollution control system according to Embodiment 4.

(10) FIG. 8 is a schematic diagram of an air pollution control system according to Embodiment 5.

(11) FIG. 9 is a schematic diagram of an air pollution control system according to Embodiment 6.

(12) FIG. 10 is a schematic diagram of an air pollution control system according to Embodiment 7.

(13) FIG. 11 is a schematic diagram of an air pollution control system according to Embodiment 8.

DESCRIPTION OF EMBODIMENTS

(14) Hereinafter, the present invention will be described in detail with reference to the drawings. Note that, the present invention is not limited by embodiments and examples. In addition, components in the embodiments and the examples include those that may be easily assumed by those skilled in the art or are practically the same.

(15) FIG. 1 is a schematic diagram of an air pollution control system of an embodiment according to the present invention.

(16) As illustrated in FIG. 1, in an air pollution control system 10 of the embodiment according to the present invention, flue gas 12 from a boiler 11 is subjected to a reduction in nitrogen oxides (NO.sub.x) from the flue gas 12 by NO.sub.x removal equipment 13, and thereafter is first guided to an air heater AH to heat air supplied to the boiler 11. Thereafter, the flue gas 12 is introduced to a dry type electric dust collector 14 which is dust reduction equipment so as to reduce particulates. Next, the flue gas 12 is introduced to SO.sub.x removal equipment 15 to reduce sulfur oxides (SO.sub.x). Then, the flue gas 12 is cooled by a cooler 16, is thereafter introduced to CO.sub.2 recovery equipment 17 to reduce carbon dioxide, and purified gas 18 is emitted from the top portion of a CO.sub.2 absorber to the air which is outside the system. Note that, the particulates reduced by the electric dust collector 14 are subjected to an additional ash treatment 14a.

(17) In the present invention, before introducing the flue gas 12 to the CO.sub.2 recovery equipment 17, mist generation material reduction equipment 20 which reduces a mist generation material that is a generation source of mist generated in the CO.sub.2 absorber of the CO.sub.2 recovery equipment 17 is provided.

(18) According to the air pollution control system 10 according to the present invention, since the mist generation material reduction equipment 20 is provided before the introduction to the CO.sub.2 recovery equipment 17, the amount of mist generation material in the flue gas 12 when being introduced to the CO.sub.2 absorber of the CO.sub.2 recovery equipment 17 is significantly decreased. As a result, the amount of CO.sub.2 absorption liquid (hereinafter, also referred to as absorption liquid) entrained by mist and dispersed to the outside may be significantly decreased. As a result, the loss of the absorption liquid that scatters to the outside of the system is significantly decreased, and thus an unnecessary replenishment is eliminated, thereby suppressing an increase in running cost during the air pollution control.

(19) The mist generation material reduced by the mist generation material reduction equipment 20 according to the present invention is SO.sub.3 mist, nitric acid mist, hydrochloric acid mist, water vapor mist, or the like and is referred to as a material that becomes a mist generation factor in the CO.sub.2 absorber. Note that, equipment that performs a reduction in a gas state before becoming mist is also included in the mist generation material reduction equipment 20 according to the present invention.

(20) Since the flue gas 12 from the boiler 11 is in a high-temperature state, the mist generation material is present in a gas state at first. Thereafter, in a process of passing through the electric dust collector and the SO.sub.x removal equipment, the flue gas is cooled, and thus the mist generation material changes from the gas state to a mist state.

(21) The particle size of the mist of the mist generation material in the present invention is referred to as a size of equal to or smaller than 3.0 m.

(22) The form of mist generation and entraining of the absorption liquid in the CO.sub.2 absorber of the CO.sub.2 recovery equipment 17 will be described using FIGS. 2, 3-1, and 3-2.

(23) FIG. 2 is a conceptual diagram of a mechanism of entraining of the absorption liquid by mist generation. FIG. 3-1 is a photograph illustrating a state where white smoke is decreased in the CO.sub.2 absorber, and FIG. 3-2 is a photograph illustrating a state where white smoke is generated in the CO.sub.2 absorber. Although, SO.sub.3 mist is exemplified as the mist generation material in the description, descriptions with other kinds of mist will be the same. The flue gas 12 from the boiler 11 is subjected to a gas purifying treatment such as NO.sub.x removal, a reduction in particulates, and SO.sub.x removal, and the flue gas 12 is cooled by the cooler 16, resulting in a gas temperature of about 50 C. Since this temperature state is equal to or less than the acid dew point, there is SO.sub.3 mist (for example, 0.1 to 1.0 m).

(24) A SO.sub.3 mist 50 has SO.sub.3 as a nucleus 51 and water vapor 52 that is incorporated into the periphery thereof.

(25) In the CO.sub.2 absorber, the absorption liquid is sprayed from nozzles and falls, and the falling absorption liquid and the flue gas are subjected to countercurrent contact such that CO.sub.2 is absorbed by the absorption liquid. On the other hand, the flue gas 12 is introduced from the lower side of the CO.sub.2 absorber and is discharged to the upper side. Here, the SO.sub.3 mist 50 is not absorbed by the absorption liquid and ascends along with the gas stream of the flue gas 12.

(26) Here, in the CO.sub.2 absorber, when the absorption liquid is supplied from the nozzles, the absorption liquid falls and a part of the absorption liquid and moisture evaporates, and thus a gaseous absorption liquid 41G and water vapor 42 are generated.

(27) In addition, the amount of gaseous absorption liquid 41G and the water vapor 42 further increases as the temperature of the absorption liquid is increased due to, for example, the exothermic reaction of the absorption liquid when CO.sub.2 is absorbed.

(28) Then, the gaseous absorption liquid 41G and the water vapor 42 are incorporated into the SO.sub.3 mist 50, resulting in a SO.sub.3 mist (bloated mist) 53 including a bloated (for example, about 0.5 to 2.0 m) absorption liquid.

(29) As described above, the SO.sub.3 mist 50 in the flue gas 12, before being introduced to the CO.sub.2 recovery equipment 17, incorporates the gaseous absorption liquid 41G and the water vapor 42 in the CO.sub.2 absorber, becomes the SO.sub.3 mist 53 including the absorption liquid, and scatters from the top portion of the CO.sub.2 absorber while being entrained by the flue gas 12. Therefore, the loss of the absorption liquid occurs.

(30) The form of white smoke generation in the CO.sub.2 absorber is illustrated in FIGS. 3-1 and 3-2.

(31) FIG. 3-1 illustrates a case where the amount of mist generation material is decreased to a predetermined amount or less by providing the mist generation material reduction equipment 20 for the flue gas 12 introduced to the CO.sub.2 absorber and a state where the scatting of the SO.sub.3 mist (bloated mist) 53 including the absorption liquid in the CO.sub.2 absorber is significantly reduced and thus generation of white smoke is suppressed. FIG. 3-2 illustrates a case where the flue gas 12 is introduced as it is without providing the mist generation material reduction equipment 20 for the flue gas 12 introduced to the CO.sub.2 absorber and a state where the scatting of the SO.sub.3 mist (bloated mist) 53 including the absorption liquid in the CO.sub.2 absorber occurs and thus white smoke is generated.

(32) That is, in the present invention, the mist generated in the CO.sub.2 absorber is referred to as the SO.sub.3 mist (bloated mist) 53 including the absorption liquid. Confirming the presence or absence of the generation of bloated mist is referred to as the presence or absence of generation of white smoke, and by suppressing the bloated mist in the CO.sub.2 absorber, generation of white smoke is eliminated. Furthermore, the scattering of the absorption liquid is prevented.

(33) In addition, regarding the bloated mist, as illustrated in FIG. 2, there may be cases where the gaseous absorption liquid 41G and the gaseous water vapor 42 are separately incorporated into the SO.sub.3 mist 50 in the flue gas 12 in the CO.sub.2 absorber to respectively form a SO.sub.3 mist (bloated mist) 53A including the absorption liquid and a SO.sub.3 mist (bloated mist) 53B including the water vapor.

(34) Here, in the case of the mist (bloated mist) 53B including the water vapor, there is no loss of the absorption liquid. However, since generation of white smoke of the purified gas 18 to be discharged to the outside of a system occurs, a reduction in the mist generation material is also needed.

(35) Therefore, according to the present invention, by providing the mist generation material reduction equipment 20 before introduction to the CO.sub.2 recovery equipment 17, entraining of the CO.sub.2 absorption liquid may be significantly reduced when the flue gas 12 from which CO.sub.2 is reduced is discharged to the outside of the system, and an appropriate air pollution control may be performed.

(36) Therefore, in the present invention, by providing the mist generation material reduction equipment 20 that reduces the mist generation material which is the generation source of the mist (the SO.sub.3 mist including the absorption liquid which is the bloated mist) generated in the CO.sub.2 absorber of the CO.sub.2 recovery equipment 17 before introducing the flue gas 12 to the CO.sub.2 recovery equipment 17, the loss of the absorption liquid that scatters to the outside of the system from the CO.sub.2 absorber may be significantly decreased.

(37) The mist generation material reduction equipment 20 may be provided on the upstream side of the dry type electric dust collector 14, between the dry type electric dust collector 14 and the SO.sub.x removal equipment 15, or in either of the front and the rear of the cooler 16, or to be integrated into the cooler 16.

(38) Here, before introducing the flue gas 12 to the CO.sub.2 recovery equipment 17, it is preferable that the amount of SO.sub.3 mist 50 be decreased to 3 ppm or less for prevention of white smoke and prevention of scattering of the absorption liquid in the CO.sub.2 absorber. This is because when the amount of SO.sub.3 mist 50 is decreased to 3 ppm or less, scattering is suppressed, and deterioration of, for example, an amine-based absorption liquid due to SO.sub.3 is prevented.

(39) According to the present invention, since the scattering of the absorption liquid is prevented and the deterioration of the absorption liquid is prevented, a decrease in the number of regeneration treatments performed in the regeneration equipment (reclaiming equipment) for the absorption liquid may be achieved, and the loss of the absorption liquid is further significantly decreased, so that a decrease in the amount of the replenished absorption liquid may be achieved. Therefore, the system efficiency of the air pollution control system may be significantly enhanced.

(40) Note that, in this embodiment, the electric dust collector is exemplified as the dust reduction equipment in the description. However, the present invention is not limited to this as long as particulates are reduced from the flue gas 12, and besides the electric dust collector, for example, a bag filter or a venturi scrubber may be exemplified.

(41) In the following embodiment, specific embodiments of the mist generation material reduction equipment that reduces the mist generation material will be described.

Embodiment 1

(42) The air pollution control system including the CO.sub.2 recovery equipment according to an embodiment of the present invention will be described with reference to the drawings. FIG. 4-1 is a schematic diagram of the air pollution control system according to Embodiment 1. FIG. 4-2 is a schematic diagram of another air pollution control system according to Embodiment 1. Note that, in the following embodiments, SO.sub.3 is exemplified as the mist generation material in the description, but the present invention is not limited thereto.

(43) As illustrated in FIG. 4-1, an air pollution control system 10A according to Embodiment 1 includes the NO.sub.x removal equipment 13 which reduces nitrogen oxides from the flue gas 12 from the boiler (for example, coal-fired boiler) 11, the electric dust collector 14 which is provided on the downstream side of the NO.sub.x removal equipment 13 and reduces particulates from the flue gas 12, the SO.sub.x removal equipment 15 which is provided on the downstream side of the electric dust collector 14 and reduces sulfur oxides from the flue gas 12, the cooler 16 which is provided on the downstream side of the SO.sub.x removal equipment 15 and has a cooling unit 16a that decreases the gas temperature, and the CO.sub.2 recovery equipment 17 which includes an CO.sub.2 absorber 17A that brings CO.sub.2 in the flue gas 12 into contact with the absorption liquid so as to be reduced and an absorption liquid regenerator 17B that causes the absorption liquid to emit CO.sub.2 to recover the CO.sub.2 and regenerate the absorption liquid.

(44) In this embodiment, before introducing the SO.sub.3 mist 50 to the CO.sub.2 recovery equipment 17, as a countermeasure for a reduction, sodium bisulfite injection equipment 21 which injects sodium bisulfite (SBS; Sodium bisulfite) between the NO.sub.x removal equipment 13 and the electric dust collector 14 is provided. The sodium bisulfite injection equipment 21 according to this embodiment functions as the mist generation material reduction equipment 20.

(45) As a result, by supplying SBS into the flue gas 12 having a gas temperature of about 120 C. to 160 C. on the downstream side of the air heater AH, SO.sub.3 in the gas state is reduced. As a result, the amount of the SO.sub.3 mist 50 introduced to the CO.sub.2 recovery equipment 17 is decreased.

(46) That is, in this embodiment, SBS is sprayed from the sodium bisulfite injection equipment 21 to convert SO.sub.3 in the gas state to NaHSO.sub.4 or Na.sub.2SO.sub.4 solids so as to be arrested thereafter by the dry type electric dust collector 14 along with particulates in the flue gas 12. The form of this reaction is shown as follows.
SO.sub.3+NaHSO.sub.3.fwdarw.NaHSO.sub.4+SO.sub.2(1)
SO.sub.3+2NaHSO.sub.3.fwdarw.Na.sub.2SO.sub.4+2SO.sub.2+H.sub.2O(2)

(47) Note that, the particulates arrested by the electric dust collector 14 are subjected to an ash treatment 14a.

(48) Injection of sodium bisulfite (SBS) may be performed anywhere on the upstream side of the electric dust collector 14, and for example, sodium bisulfite (SBS) may be supplied between the NO.sub.x removal equipment 13 and the air heater AH (broken line in FIG. 4-1).

(49) In addition, the flue gas 12 from which particulates are reduced in the electric dust collector 14 is subjected to a reduction in sulfur oxides from the flue gas 12 in the SO.sub.x removal equipment 15, limestone (CaCO.sub.3) 15a and oxidation air 15b are supplied to cause the reduced sulfur oxides to become gypsum 15c through a limestone-gypsum method, and desulfurized waste water 15d is additionally treated. Note that, in the figures, reference numerals 17a, 17b, 17c, 17d, 17e, and 17f denote a reboiler, saturated water vapor, condensed water, a separation drum, recovered CO.sub.2, and an absorption liquid heat exchanger, respectively.

(50) The flue gas 12 desulfurized by the SO.sub.x removal equipment 15 is cooled by the cooler 16 to cause the flue gas temperature to be 50 C. or less, and is introduced to the CO.sub.2 recovery equipment 17 including the CO.sub.2 absorber 17A and the absorption liquid regenerator 17B. Here, CO.sub.2 in the flue gas 12 is reduced by, for example, the amine-based absorption liquid 41. At this time, in this embodiment, as a result of reducing SO.sub.3 in the gas state which is the mist generation material in the flue gas 12, a decrease in the amount of the SO.sub.3 mist 50 introduced to the CO.sub.2 recovery equipment 17 is achieved. Therefore, the generation of white smoke of the purified gas 18 discharged from the CO.sub.2 absorber 17A, which is caused by the mist, is suppressed, and the entraining of the absorption liquid 41 is suppressed.

(51) As a result, an air pollution control system in which the loss of the absorption liquid 41 is significantly decreased may be provided.

(52) Here, in this embodiment, the amine-based absorption liquid is exemplified as the absorption liquid 41. However, the absorption liquid of the present invention is not limited to the amine-based absorption liquid. As the absorption liquid, besides the amine-based absorption liquid, for example, an amino acid-based absorption liquid, an ionic liquid absorption liquid, a hot potassium carbonate absorption liquid made of potassium carbonate and amines, and the like may be exemplified.

(53) FIG. 4-2 is a schematic diagram of an air pollution control system of a modified embodiment of Embodiment 1. In the cooler 16 illustrated in FIG. 4-1, the flue gas 12 is cooled. However, as illustrated in FIG. 4-2, a finishing SO.sub.x removal unit 16b is provided on the lower side of the cooler 16, and the limestone (CaCO.sub.3) 15a and the oxidation air 15b are supplied to form the gypsum 15c through the limestone-gypsum method. Accordingly, sulfur oxides that remain in the flue gas 12 from the SO.sub.x removal equipment 15 are reduced to further enhance the SO.sub.x removal efficiency, and thus most of the residual sulfur oxides may be reduced. Note that, a strong alkaline agent such as sodium hydroxide (NaOH) may be added instead of the limestone.

(54) In this embodiment, in the finishing SO.sub.x removal unit 16b, a liquid column type is used as a method of supplying a SO.sub.x removal absorption liquid. However, the present invention is not limited thereto, and any of sprinkling type, jet type, and filling type may also be used.

(55) Here, as the SO.sub.x removal absorption liquid used in the finishing SO.sub.x removal unit 16b, besides the limestone (CaCO.sub.3), a strong alkaline agent such as NaOH, Na.sub.2CO.sub.3, NaHCO.sub.3, Ca(OH).sub.2, or Mg(OH).sub.2 may be exemplified. By using the strong alkaline agent, further enhancement of the SO.sub.x removal performance may be achieved, and this is particularly effective in a case where the flue gas 12 having a high sulfur oxide concentration is introduced, thereby decreasing the concentration of sulfur oxides in the flue gas 12 introduced to the CO.sub.2 recovery equipment 17 to an extremely low concentration. The SO.sub.x removal performance is increased compared to the limestone-gypsum method. Therefore, even in a case where the concentration of sulfur oxides in the introduced flue gas 12 is high, favorable SO.sub.x removal performance is exhibited, which is preferable.

Embodiment 2

(56) An air pollution control system including the CO.sub.2 recovery equipment according to an embodiment of the present invention will be described with reference to the drawings.

(57) FIG. 5 is a schematic diagram of an air pollution control system according to Embodiment 2. As illustrated in FIG. 5, the air pollution control system 10B according to Embodiment 2 is provided with ammonia injection equipment 22 on the upstream side of the dry type electric dust collector 14 instead of the sodium bisulfite injection equipment 21 used in Embodiment 1 so as to spray ammonia into the flue gas 12. The ammonia injection equipment 22 according to this embodiment functions as the mist generation material reduction equipment 20.

(58) On the upstream side of the electric dust collector 14, ammonia (NH.sub.3) gas is sprayed to form ammonium sulfate (NH).sub.4SO.sub.4 and this is arrested by the dry type electric dust collector 14 along with particulates. In this embodiment, as a result of reducing SO.sub.3 in the gas state which is the mist generation material from the flue gas 12, a decrease in the amount of the SO.sub.3 mist introduced to the CO.sub.2 recovery equipment 17 is achieved. Therefore, the generation of white smoke of the purified gas 18 discharged from the CO.sub.2 absorber 17A, which is caused by the mist, is suppressed, and the entraining of the absorption liquid 41 is suppressed. As a result, an air pollution control system in which there is no loss of the absorption liquid 41 may be provided.

(59) In a case where the NO.sub.x removal equipment 13 is present on the upstream side of the air pollution control system, by increasing a supply amount of ammonia (NH.sub.3) used in the NO.sub.x removal equipment 13, an ammonia (NH.sub.3) injection equipment does not need to be newly provided and may be replaced.

Embodiment 3

(60) An air pollution control system including the CO.sub.2 recovery equipment according to an embodiment of the present invention will be described with reference to the drawings.

(61) FIG. 6 is a schematic diagram of an air pollution control system according to Embodiment 3. As illustrated in FIG. 6, the air pollution control system 10C according to Embodiment 3 is provided with dissolved salt spraying equipment 23 between the dry type electric dust collector 14 and the SO.sub.x removal equipment 15 instead of the sodium bisulfite injection equipment 21 used in Embodiment 1 so as to spray a dissolved salt 24 into the flue gas 12. The dissolved salt spraying equipment 23 according to this embodiment functions as the mist generation material reduction equipment 20.

(62) In this embodiment, an aqueous solution of the dissolved salt 24, which is soluble, such as Na.sub.2SO.sub.4 and MgSO.sub.4 is sprayed on the upstream side of the SO.sub.x removal equipment 15. As the dissolved salt solution is sprayed into the flue gas 12 having a gas temperature of, for example, about 130 C. to 150 C. on the downstream side of the dry type electric dust collector 14, fine dry dissolved salt particles are formed, and SO.sub.3 in the gas state is adsorbed and fixed onto the dissolved salt particles, thereby reducing the SO.sub.3 in the gas state from the flue gas 12. As a result, the amount of the SO.sub.3 mist 50 introduced to the CO.sub.2 recovery equipment 17 is decreased.

(63) As the dissolved salt 24, for example, there are NaCl, NaOH, Na.sub.2SO.sub.4, Na.sub.2CO.sub.3, KCl, KOH, K.sub.2SO.sub.4, K.sub.2CO.sub.3, KHCO.sub.3, MgCl.sub.2, MgSO.sub.4, CaCl.sub.2, and the like.

(64) Here, when Na.sub.2SO.sub.4 is used as the dissolved salt 24, a reaction between dissolved salt particles (Na.sub.2SO.sub.4) and SO.sub.3 as in Expression (3) below proceeds. As a result, NaHSO.sub.4.Math.H.sub.2O (solid) is formed.
Na.sub.2SO.sub.4+SO.sub.3+3H.sub.2O.fwdarw.2NaHSO.sub.4.Math.H.sub.2O(3)

(65) Both Na.sub.2SO.sub.4 and NaHSO.sub.4.Math.H.sub.2O are soluble and thus are dissolved in the SO.sub.x removal equipment 15 on the downstream side. Therefore, compared to a case of Embodiment 2 in which ammonia is injected, a solid material treatment including ammonia of the dry type electric dust collector 14 is unnecessary. In this embodiment, as a result of reducing SO.sub.3 in the gas state which is the mist generation material from the flue gas 12, a decrease in the amount of the SO.sub.3 mist 50 introduced to the CO.sub.2 recovery equipment 17 is achieved. Therefore, the generation of white smoke of the purified gas 18 discharged from the CO.sub.2 absorber 17A, which is caused by the mist, is suppressed, and the entraining of the absorption liquid 41 is suppressed. As a result, an air pollution control system in which the loss of the absorption liquid 41 is significantly decreased may be provided.

Embodiment 4

(66) An air pollution control system including the CO.sub.2 recovery equipment according to an embodiment of the present invention will be described with reference to the drawings.

(67) FIG. 7 is a schematic diagram of an air pollution control system according to Embodiment 4. As illustrated in FIG. 7, the air pollution control system 10D according to Embodiment 4 is provided with a wet type electric dust collector 25 between the SO.sub.x removal equipment 15 and the cooler 16 instead of the sodium bisulfite injection equipment 21 used in Embodiment 1. The wet type electric dust collector 25 according to this embodiment functions as the mist generation material reduction equipment 20. The wet type electric dust collector 25 may be provided on the downstream side of the SO.sub.x removal equipment 15 to charge and reduce the SO.sub.3 mist 50 from the flue gas 12. In this embodiment, the wet type electric dust collector 25 is provided on the upstream side of the cooler 16 (between the SO.sub.x removal equipment 15 and the cooler 16). However, the present invention is not limited thereto, and the wet type electric dust collector 25 may also be provided on the downstream side of the cooler 16 (between the cooler 16 and the CO.sub.2 recovery equipment 17).

(68) In this embodiment, as a result of reducing SO.sub.3 in the mist state which is the mist generation material in the flue gas 12, a decrease in the amount of the SO.sub.3 mist 50 introduced to the CO.sub.2 recovery equipment 17 is achieved. Therefore, the generation of white smoke of the purified gas 18 discharged from the CO.sub.2 absorber 17A, which is caused by the mist, is suppressed, and the entraining of the absorption liquid 41 is suppressed. As a result, an air pollution control system in which the loss of the absorption liquid 41 is significantly decreased may be provided.

Embodiment 5

(69) An air pollution control system including the CO.sub.2 recovery equipment according to an embodiment of the present invention will be described with reference to the drawings.

(70) FIG. 8 is a schematic diagram of an air pollution control system according to Embodiment 5. As illustrated in FIG. 8, the air pollution control system 10E according to Embodiment 5 is provided with a wet type electric dust collection unit 25a between the SO.sub.x removal unit 16b and the cooling unit 16a inside the cooler 16 of Embodiment 5 so as to configure a wet type electric dust collector-integrated cooler 27. Accordingly, finishing SO.sub.x removal equipment that performs a finish of SO.sub.x removal is constructed. The wet type electric dust collection unit 25a of the cooling unit 16a according to this embodiment functions as the mist generation material reduction equipment 20. Compared to the system of Embodiment 4, it is unnecessary to separately install the wet type electric dust collector 25, and thus there is no need to secure the installation space thereof.

(71) In this embodiment, by configuring the wet type electric dust collector-integrated cooler 27, the SO.sub.3 mist 50 may be reduced from the flue gas 12. In this embodiment, as a result of reducing SO.sub.3 in the mist state which is the mist generation material from the flue gas 12, a decrease in the amount of the SO.sub.3 mist 50 introduced to the CO.sub.2 recovery equipment 17 is achieved. Therefore, the generation of white smoke of the purified gas 18 discharged from the CO.sub.2 absorber 17A, which is caused by the mist, is suppressed, and the entraining of the absorption liquid 41 is suppressed. As a result, an air pollution control system in which the loss of the absorption liquid 41 is significantly decreased may be provided.

Embodiment 6

(72) An air pollution control system including the CO.sub.2 recovery equipment according to an embodiment of the present invention will be described with reference to the drawings.

(73) FIG. 9 is a schematic diagram of an air pollution control system according to Embodiment 6. As illustrated in FIG. 9, the air pollution control system 10F according to Embodiment 6 is provided with a demister 26 inside the cooler 16 instead of the sodium bisulfite injection equipment 21 used in Embodiment 1. The demister 26 according to this embodiment functions as the mist generation material reduction equipment 20.

(74) By providing the demister 26 at the top portion on the upper side of the downstream of the cooling unit 16a of the cooler 16, the SO.sub.3 mist 50 may be reduced from the flue gas 12. In this embodiment, as a result of reducing SO.sub.3 in the mist state which is the mist generation material from the flue gas 12, a decrease in the amount of the SO.sub.3 mist 50 introduced to the CO.sub.2 recovery equipment 17 is achieved. Therefore, the generation of white smoke of the purified gas 18 discharged from the CO.sub.2 absorber 17A, which is caused by the mist, is suppressed, and the entraining of the absorption liquid 41 is suppressed. As a result, an air pollution control system in which the loss of the absorption liquid 41 is significantly decreased may be provided.

(75) In this embodiment, the wire diameter of the wire mesh that constitutes the demister 26 may be 1 to 20 m, and more preferably 3 to 10 m, but the present invention is not limited thereto. In addition, it is preferable that the void fraction of the demister 26 be about 90 to 97%, but the present invention is not limited thereto.

Embodiment 7

(76) An air pollution control system including the CO.sub.2 recovery equipment according to an embodiment of the present invention will be described with reference to the drawings.

(77) FIG. 10 is a schematic diagram of an air pollution control system according to Embodiment 7. As illustrated in FIG. 10, the air pollution control system 10G according to Embodiment 7 is provided with calcium carbonate spraying equipment 31 between the electric dust collector 14 and the SO.sub.x removal equipment 15 instead of the sodium bisulfite injection equipment 21 used in Embodiment 1 so as to spray calcium carbonate (CaCO.sub.3) into the flue gas 12. In addition, on the upstream side of the SO.sub.x removal equipment 15 which is on the downstream side where spraying is performed, a first heat exchanger 32 which decreases the flue gas temperature is provided. The calcium carbonate spraying equipment 31 and the first heat exchanger 32 according to this embodiment function as the mist generation material reduction equipment 20.

(78) On the upstream side of the SO.sub.x removal equipment 15, as the temperature of the flue gas 12 is decreased to a sulfuric acid dew point or less by the first heat exchanger 32, gaseous SO.sub.3 is converted to mist-like SO.sub.3, and the mist-like SO.sub.3 is neutralized by CaCO.sub.3 (limestone) sprayed into the flue gas 12, thereby reducing the mist-like SO.sub.3 from the flue gas 12.

(79) In this embodiment, as a result of converting SO.sub.3 which is the mist generation material in the flue gas 12 from the gas state to the mist state and reducing the mist-like mist generation material, a decrease in the amount of the SO.sub.3 mist 50 introduced to the CO.sub.2 recovery equipment 17 is achieved. Therefore, the generation of white smoke of the purified gas 18 discharged from the CO.sub.2 absorber 17A, which is caused by the mist, is suppressed, and the entraining of the absorption liquid 41 is suppressed. As a result, an air pollution control system in which the loss of the absorption liquid 41 is significantly decreased may be provided.

Embodiment 8

(80) An air pollution control system including the CO.sub.2 recovery equipment according to an embodiment of the present invention will be described with reference to the drawings.

(81) FIG. 11 is a schematic diagram of an air pollution control system according to Embodiment 8. As illustrated in FIG. 11, the air pollution control system 10H according to Embodiment 8 is provided with a second heat exchanger 33 which decreases the gas temperature of the flue gas 12, on the upstream side of the dry type electric dust collector 14 instead of the first heat exchanger 32 provided in Embodiment 7. The second heat exchanger 33 according to this embodiment functions as the mist generation material reduction equipment 20.

(82) In this embodiment, by providing the second heat exchanger 33, the flue gas 12 is decreased to about, for example, 80 to 110 C., and thus the SO.sub.3 gas is decreased to a sulfuric acid dew point or less and becomes mist-like SO.sub.3. The mist-like SO.sub.3 adheres to particulates in the flue gas 12, and this is arrested by the electric dust collector 14 so as to reduce SO.sub.3.

(83) In this embodiment, as a result of converting SO.sub.3 which is the mist generation material in the flue gas 12 from the gas state to the mist state and reducing the mist generation material in the mist state, a decrease in the amount of the SO.sub.3 mist 50 introduced to the CO.sub.2 recovery equipment 17 is achieved. Therefore, the generation of white smoke of the purified gas 18 discharged from the CO.sub.2 absorber 17A, which is caused by the mist, is suppressed, and the entraining of the absorption liquid 41 is suppressed. As a result, an air pollution control system in which the loss of the absorption liquid 41 is significantly decreased may be provided.

(84) As described above in the embodiments, according to the present invention, since various forms of mist generation material reduction equipment 20 are provided, an air pollution control system in which the entraining of the absorption liquid 41 is significantly reduced when the flue gas 12 from which CO.sub.2 is reduced is discharged to the outside of the system may be provided.

(85) Even in various combinations of Embodiments 1 to 8, the effect of the present invention may be exhibited. Specifically, a combination of any one of the sodium bisulfite injection equipment 21 of Embodiment 1, the ammonia injection equipment 22 of Embodiment 2, and the dissolved salt spraying equipment 23 of Embodiment 3, and the wet type electric dust collector 25 of Embodiment 4 and/or the demister 26 of Embodiment 6 may be achieved.

(86) In addition, a combination of any one of the sodium bisulfite injection equipment 21 of Embodiment 1, the ammonia injection equipment 22 of Embodiment 2, and the dissolved salt spraying equipment 23 of Embodiment 3 and the first heat exchanger 32 of Embodiment 7, and moreover, a combination of the former combination and the wet type electric dust collector 25 of Embodiment 4 and/or the demister 26 of Embodiment 6 may be achieved.

(87) In addition, a combination of the second heat exchanger 33 of Embodiment 8 and the wet type electric dust collector 25 of Embodiment 4 and/or the demister 26 of Embodiment 6 may be achieved.

(88) Here, it is preferable that the first and second heat exchangers 32 and 33 not be general heat exchange members made of steel but be made of a corrosion-resistant material. This is because when SO.sub.3 which is the mist generation material is changed from the gas state to the mist state, resistance to corrosion due to sulfurous acid or sulfuric acid is necessary for long-term stable operation.

(89) Here, as the corrosion-resistant material in the present invention, an acid-resistant organic material or inorganic material may be used. For example, as the organic material, Teflon (registered trademark) such as polytetrafluoroethylene (PTFE) may be exemplified.

(90) In this case, the constituent member of the heat exchanger may be treated by coating with the corrosion-resistant material, or the constituent member itself may be manufactured of a corrosion-resistant material.

REFERENCE SIGNS LIST

(91) 10, 10A to 10H AIR POLLUTION CONTROL SYSTEM 11 Boiler 12 Flue Gas 13 NO.sub.x Removal Equipment 14 Electric Dust Collector 15 SO.sub.x Removal Equipment 16 Cooler 16a Cooling Unit 16b Finishing SO.sub.x Removal Unit 17 CO.sub.2 Recovery Equipment 17A CO.sub.2 Absorber 17B Absorption Liquid Regenerator 18 Purified Gas 20 Mist Generation Material Reduction Equipment 21 Sodium Bisulfite Injection Equipment 22 Ammonia Injection Equipment 23 Dissolved Salt Spraying Equipment 24 Dissolved Salt 25 Wet Type Electric Dust Collector 25a Wet Type Electric Dust Collection Unit 26 Demister 31 Calcium Carbonate Spraying Equipment 32 First Heat Exchanger 33 Second Heat Exchanger 41 Absorption Liquid