WO2000042359A1 - Method and device for reducing temperature of exhaust gas utilizing hot water - Google Patents
Method and device for reducing temperature of exhaust gas utilizing hot water Download PDFInfo
- Publication number
- WO2000042359A1 WO2000042359A1 PCT/JP1999/007162 JP9907162W WO0042359A1 WO 2000042359 A1 WO2000042359 A1 WO 2000042359A1 JP 9907162 W JP9907162 W JP 9907162W WO 0042359 A1 WO0042359 A1 WO 0042359A1
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- Prior art keywords
- exhaust gas
- hot water
- temperature
- water
- solution
- Prior art date
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Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/44—Details; Accessories
- F23G5/48—Preventing corrosion
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/02—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
- F23J15/04—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material using washing fluids
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/06—Arrangements of devices for treating smoke or fumes of coolers
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2900/00—Special arrangements for conducting or purifying combustion fumes; Treatment of fumes or ashes
- F23J2900/13001—Preventing or reducing corrosion in chimneys
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/30—Technologies for a more efficient combustion or heat usage
Definitions
- the present invention is used for treating exhaust gas discharged from a combustion device such as a refuse incinerator or a boiler.
- the present invention relates to a method and an apparatus for reducing the temperature of exhaust gas, which can prevent damage due to operation and troubles due to accumulation of dust, and can also remove acid gas in exhaust gas.
- Exhaust gas emitted from combustion equipment such as refuse incinerators and boilers is generally purified by gas purification equipment and then released to the atmosphere.
- an exhaust gas temperature reduction device configured to spray water into the exhaust gas and to reduce the exhaust gas temperature by using the sensible heat and latent heat of evaporation of the water is generally used.
- FIGS. 9 and 10 show examples of a conventional exhaust gas cooling device.
- 21 is a gas cooling chamber
- 21 a is an exhaust gas inlet
- 21 b is an exhaust gas cooling device.
- Exhaust gas outlet 2 1c is ash outlet
- 22 is dewarmed water tank
- 23 is pressurized pump
- 24 is dewarmed water nozzle
- 25 is temperature control device
- 25a is temperature detector
- 26 is reduced Hot water control valve
- 27 is an injection pump
- 28 is an air compressor
- 29 is a compressed air tank
- 30 is a mixer
- G h is high-temperature exhaust gas
- G 1 is low-temperature exhaust gas
- C is ash.
- high-pressure water from the cooling water tank 22 added by the pressurizing pump 23 is supplied to the cooling water nozzle installed near the exhaust gas inlet 21 a. It is sprayed into the gas cooling chamber 21 through 24. The temperature of the sprayed water rises when it comes into contact with the high-temperature exhaust gas Gh, and when it reaches the boiling point, it evaporates to steam.
- the high-temperature exhaust gas G h in the gas cooling chamber 21 is cooled by the sensible heat of the sprayed water, the latent heat of evaporation, and the sensible heat of water vapor, and is cooled to a predetermined temperature. And it is derived from the exhaust gas outlet 21b.
- the amount of water sprayed into the gas cooling chamber 21 is adjusted by the temperature detection signal from the temperature detector 25 a via the temperature control device 25 to adjust the opening of the temperature-reducing water flow control valve 26.
- the temperature of the low-temperature exhaust gas G 1 derived from the exhaust gas outlet 21 b is controlled by controlling the amount of water sprayed into the gas cooling chamber 21 by changing the amount of water returned to the desuperheated water tank 22. Is maintained at a desired temperature.
- the water sent from the temperature reduction water tank 22 by the injection pump 27 and the compressed air tank 29 from the compressed air tank 29 The water is atomized by mixing the high-pressure air and in the mixer 30. Thereafter, the atomized water is sprayed from the mixer 30 into the gas cooling chamber 21 through a desuperheated water nozzle 24 provided near the exhaust gas inlet 21a.
- the temperature of the sprayed water rises due to contact with the high-temperature exhaust gas G h and evaporates into steam when the boiling point is reached.
- the high-temperature exhaust gas G h in the gas cooling chamber 21 is sprayed. Cooled by the sensible heat of water, latent heat of vaporization, and the sensible heat of water vapor. That is, the temperature of the low-temperature exhaust gas G 1 is maintained at a set value by adjusting the amount of sprayed water, and the like, in exactly the same manner as in FIG.
- the conventional exhaust gas temperature-reducing devices shown in FIGS. 9 and 10 can reduce the temperature of the high-temperature exhaust gas Gh to a desired temperature using inexpensive water, and exhibit excellent practical utility. is there.
- the particle size of atomized desuperheated water is usually as small as about 30 to 100 / m, as shown in FIG. Compared with the one-fluid system, the frequency of inconvenience caused by the adhesion of water droplets is relatively low.
- the amount of exhaust gas 9 0, 0 0 O Nm 3 ZH, hot exhaust gas G h inlet exhaust gas temperature 2 4 0 ° C When the temperature of the exhaust gas is reduced to a low-temperature exhaust gas G1 at an outlet exhaust gas temperature of 180 ° C., when the exhaust gas temperature reducing device of the one-fluid type shown in FIG. 9 is used, the inner diameter is about 480 m.
- the heat load of the gas cooling chamber is usually 5, 0 00 ⁇ 1 0, OOO kcal / m 3 ⁇ H ( unit volume of the gas cooling chamber, unit of time per (The amount of heat that can be taken away from the exhaust gas).
- the heat load in the gas cooling room is 7 OOO kcal / m 3 ⁇ H. Disclosure of Invention I (Problem to be solved)
- the present invention has the above-mentioned problems in the conventional exhaust gas cooling apparatus, that is, (a) In the case of the one-fluid system, since the particle diameter of atomized reduced-temperature water is coarse, water droplets are deposited on the wall of the gas cooling chamber. Direct operation may damage the refractory material, or may make dust difficult to operate smoothly due to adhesion and accumulation of dust. (Mouth) In the case of the two-fluid system, compressed air equipment is required, equipment and running costs. (C) It takes a long time for the atomized water particles to evaporate, so that the gas cooling chamber cannot be downsized significantly. By reducing the particle size of water particles to a significantly smaller size than before, an exhaust gas temperature reduction method that can reduce the temperature of exhaust gas efficiently and inexpensively with an extremely small exhaust gas temperature reduction device. To provide an exhaust gas temperature reduction device used for this Than it is.
- the present inventor attempts to atomize water using a deheated water nozzle in a one-fluid type exhaust gas deheater using only water through the design, manufacture and testing of many exhaust gas deheaters. No matter how much the temperature-reduced water nozzle is improved or the pressure of the temperature-reduced water is increased, it is difficult to reduce the particle size of the atomized temperature-reduced water to about 100 m or less. I learned that the room volume could not be reduced significantly.
- the present inventor has made a common sense practice in the design of this kind of exhaust gas desuperheater, that is, ⁇ using room temperature water of about 20 to 30 ° C as desuperheated water, In addition, the latent heat of evaporation is effectively used for cooling the high-temperature exhaust gas.
- the pressurized hot water having a temperature equal to or higher than the boiling point of water or a gas-liquid two-phase flow containing steam in a part of the pressurized hot water is atomized and ejected from the conventional deheated water nozzle.
- the invention of the present application is based on the above-mentioned idea that overturns the ordinary technical common sense or practice of the present inventors.
- the invention of claim 2 has a basic configuration of the invention in which pressurized hot water having a temperature higher than the boiling point of water under atmospheric pressure is sprayed as desuperheated water into a gas cooling chamber or an exhaust gas duct. .
- hot water taken out of the deaerator or continuous blow water of the boiler is used as a part of the pressurized hot water. Things.
- the invention of claim 4 is the invention of claim 1, claim 2 or claim 3, wherein pressurized hot water containing steam as a part thereof is used as desuperheated water.
- hot pressurized water containing an alkaline solution is used as temperature-reduced water.
- the invention of claim 6 is the invention of claim 5, wherein the heated alkaline solution is mixed into hot water.
- the invention of claim 7 is the invention of claim 5 or claim 6, wherein the alkaline solution is an alkaline aqueous solution or an alkaline slurry solution.
- the alkaline aqueous solution is an aqueous solution containing sodium hydroxide (caustic soda)
- the alkaline slurry solution is a slurry solution containing calcium hydroxide (slaked lime).
- the invention of claim 9 provides a gas cooling chamber having a gas inlet, a gas outlet, and an ash outlet, and a hot water reservoir storing pressurized hot water having a temperature higher than the boiling point of water under atmospheric pressure.
- a deheated water nozzle that sprays hot water from the hot water tank into the gas cooling chamber, a deheated water control valve that regulates the amount of hot water supplied to the deheated water nozzle, and temperature detection of low-temperature exhaust gas flowing out of the gas outlet From the temperature detector And a temperature control device that controls the opening and closing of the temperature-reducing water flow control valve based on the detection signal.
- the invention of claim 10 is characterized in that an exhaust gas duct through which exhaust gas flows, a hot water reservoir storing pressurized hot water at a temperature higher than the boiling point of water under atmospheric pressure, and a hot water reservoir.
- a deheated water nozzle that sprays hot water into the exhaust gas duct, a deheated water amount control valve that adjusts the amount of hot water supplied to the deheated water nozzle, and a temperature detector for the low-temperature exhaust gas that flows out of the exhaust gas duct outlet.
- the basic configuration of the present invention is to include a temperature control device that controls opening and closing of the temperature-reducing water control valve based on a detection signal from the temperature detector.
- the invention of claim 11 is the invention according to claim 9 or claim 10, wherein hot water is supplied to the desuperheated water nozzle by the internal pressure of the hot water tank.
- the invention according to claim 12 is a gas cooling chamber having a gas inlet, a gas outlet, and an ash outlet, and a hot water reservoir storing pressurized hot water having a temperature higher than the boiling point of water under atmospheric pressure.
- Nku An alkaline solution tank storing an alkaline solution, a mixer for mixing the hot water from the hot water tank and the alkaline solution from the alkaline solution tank, and hot water containing the alkaline solution from the mixer.
- a temperature-reducing water nozzle sprayed into the gas cooling chamber a temperature-reducing water flow control valve that regulates the flow rate of hot water containing the alkaline solution supplied to the temperature-reducing water nozzle, and a flow rate of the alkaline solution supplied to the mixer Control valve for adjusting the temperature of the low-temperature exhaust gas flowing out from the gas outlet; an acid gas concentration detector for the low-temperature exhaust gas; and a reduced-temperature water amount based on a detection signal from the temperature detector.
- the basic structure of the present invention includes a temperature control device that controls opening and closing of a control valve, and an acid gas concentration control device that controls opening and closing of an alkaline solution amount control valve based on a detection signal from the acid gas concentration detector. Is shall.
- an alkaline solution heater for heating the alkaline solution is provided on the alkaline solution inlet side of the mixer.
- the invention of claim 14 is the invention of claim 12 or claim 13, wherein the alkaline solution tank stores an alkaline aqueous solution or an alkaline slurry solution. This is an alkaline solution tank.
- the invention according to claim 15 stores an exhaust gas duct through which exhaust gas flows, a hot water tank storing pressurized hot water at a temperature higher than the boiling point of water under atmospheric pressure, and an alkaline solution.
- a mixer for mixing the alkaline solution from the alkaline solution tank with the hot water from the alkaline solution tank; and hot water containing the alkaline solution from the mixer.
- Nozzle for spraying water into an exhaust gas duct, a temperature-reducing water control valve for adjusting the flow rate of hot water containing an alkaline solution to be supplied to the temperature-reducing water nozzle, and an alkaline solution to be supplied to the mixer.
- An alkaline solution amount control valve for adjusting the flow rate, a temperature detector for the low-temperature exhaust gas flowing out from the outlet of the exhaust gas duct, an acid gas concentration detector for the low-temperature exhaust gas, and a temperature-reducing water based on a detection signal from the temperature detector.
- Temperature control for opening and closing the quantity control valve Apparatus and acidic which controls the opening and closing of the Al force Li solution control valve by the detection signal from the acid gas concentration detector
- a gas concentration control device is a basic configuration of the present invention.
- the invention of claim 16 is the invention of claim 15, wherein an alkaline solution heater for heating the alkaline solution is provided on the alkaline solution inlet side of the mixer.
- the invention according to claim 17 is the invention according to claim 15 or claim 16, wherein the alkaline solution solution is stored with an alkaline solution or an alkaline slurry solution. This is a solution tank with a strong force.
- the discharge source of the high-temperature exhaust gas may be any combustion device such as a refuse incinerator or a boiler, and the present invention can be applied to all types of combustion exhaust gas.
- the temperature of the high-temperature exhaust gas Gh supplied to the gas cooling chamber can be set to a temperature of 1,000 to 150
- the temperature of the low-temperature exhaust gas G1 derived from the gas cooling chamber can be set to a temperature of 100 ° C or more.
- the temperature of the high-temperature exhaust gas Gh is about 900 ° C to 10000 ° C
- the temperature of the low-temperature exhaust gas G1 is 150 ° C to 250 ° C. ° C
- set the temperature of high-temperature exhaust gas Gh to 200 ° C to 400 ° C, and the temperature of low-temperature exhaust gas G1 to 120 to 250, respectively. can do.
- the shape of the gas cooling chamber may be either a vertical type or a horizontal type, and its cross-sectional shape can be freely selected from a circle, an ellipse, a square, and the like.
- the form of the exhaust gas duct may be either horizontally long or vertically long, and its cross-sectional shape may be any of a circle, an ellipse, and a square.
- the pressurized hot water Wt is water maintained at a temperature higher than the boiling point of water under atmospheric pressure (100 ° C.), and is so-called high-pressure high-temperature water.
- the pressure of the hot compressed water Wt is selected available-to a value of 1 kg / cm 2 ⁇ G or ⁇ 1 0 0 kgZcm 2 ⁇ G position physician, 3 considering the pressure resistance of the hot water tank 2, etc. It is desirable to choose between 10 kgZ cm 2 ⁇ G.
- pressurized hot water Wt is in a state in which steam is partially contained inside it (so-called two-phase fluid ), But the lower the steam content, the better.
- the hot water generated in the deaerator can be used as de-heated water as it is.
- the piping from the deaerator is required as the hot water Wt supply facility, and the exhaust gas temperature reduction device can be configured at extremely low cost.
- the combustion device is a boiler or an incinerator with a waste heat boiler
- continuous blow water from the boiler can be used as part of the hot water used as desuperheated water.
- boiler water hot water
- Part is discharged outside. Since the boiler water discharged to the outside is usually alkaline water with a pH of 8.5 to 11.8, it has a dechlorination and desulfurization effect in the exhaust gas, and is equipped with exhaust gas desalination 'desulfurization equipment. In, the amount of drug used for this can be reduced.
- the gas cooling chamber is vertical, it is desirable to install the desuperheater nozzle for atomizing the pressurized hot water near the gas inlet of the high-temperature exhaust gas Gh above it. It is selected as appropriate according to the configuration of the gas cooling chamber and the number of nozzles for cooling water. The same applies to the case where hot pressurized water is blown into the exhaust gas duct.
- the structure of the temperature-reducing water nozzle may be any structure, and for example, a known screw-type or collision-type water spray nozzle may be used.
- the number of nozzles for the cooling water nozzles depends on the shape of the gas cooling Force appropriately selected depending on the number of nozzles provided in the nozzles and the required amount of hot water to be ejected ⁇
- conventional industrial waste incinerators incineration amount 300 tonZD, exhaust gas amount 90
- 00 ONm 3 ZH exhaust gas secondary cooling
- hot water temperature 142.9 ° C, pressure 3 kg / cm 2 G saturated water
- the hot water sprayed from the desuperheated water nozzle has a high temperature and a high pressure considerably higher than the boiling point (10 ° C.) under the atmospheric pressure.
- the temperature-reduced water nozzle it rapidly boil under reduced pressure near the nozzle outlet and become fine particles, and evaporate instantaneously after being sprayed to become water vapor, so that water droplets do not evaporate Also, it does not directly hit the wall surface of the gas cooling chamber.
- the volume of the gas cooling chamber can be reduced, and the equipment cost and the installation space can be reduced.
- evaporation chamber heat load could be a 5 0, 0 0 0 ⁇ 1 5 0 , 0 00 kca 1 / m s ⁇ ⁇ .
- the exhaust gas cooling device of the present invention has There 50 the thermal load is, 0 0 0 ⁇ 1 5 0, 00 0 kca 1 / m 3 ⁇ can be selected from H, it is possible to reduce the volume of the gas cooling chamber 1 to 1 5-1 1 5 Was.
- a configuration may be adopted in which a desuperheated water nozzle is inserted into a high-temperature exhaust gas duct and a hot water is directly sprayed into the high-temperature exhaust gas duct without providing a gas cooling chamber in some cases. Is also possible.
- the amount of sprayed water is slightly larger than when using conventional low-temperature water due to the sensible heat of hot water.
- conventional exhaust gas temperature reduction equipment Required if the temperature of the desuperheated water in the device is 20 ° C and the temperature of the hot water in the exhaust gas desuperheater of the present invention is 142.9 ° C (saturated water at a pressure of 3 kg cm 2 G).
- the amount of hot water will be about 1.2 times.
- the alkaline solution may be in the form of an alkaline aqueous solution, or may be in the form of an alkaline slurry solution.
- the temperature of the hot water solution mixed into the hot water may be higher than the boiling point of water at atmospheric pressure when the temperature of the desuperheated water after mixing the hot water solution becomes higher than the boiling point of water at atmospheric pressure. Need not be heated to a high temperature. If the mixing of the alkaline solution causes the temperature of the desuperheated water to be lower than the boiling point of the water at atmospheric pressure, it is necessary to mix the alkaline solution into the hot water. It is desirable to heat to the temperature.
- the strength of the alkaline solution in the alkaline solution may be any. However, when used in the form of an alkaline aqueous solution, sodium hydroxide (caustic soda * NaOH) or magnesium hydroxide (Mg (OH) 2 ) is preferred. Further, when used in the form of an alkaline slurry solution, hydroxide calcium ⁇ (slaked lime 'Ca (OH) 2) or quicklime (CaO), calcium carbonate (C AC_ ⁇ 3) sodium carbonate (Na 2 COs), etc. Is preferred.
- the total amount of the alkaline agent in the alkaline solution mixed into the hot water is appropriately adjusted according to the type of the acidic gas in the exhaust gas to be removed, the amount of the acidic gas removed, and the exhaust gas temperature. In this way, an amount of 0.8 to 1.5 equivalent of an alkaline agent is mixed into the hot water.
- FIG. 1 is an explanatory view showing an embodiment of a method and apparatus for reducing exhaust gas according to the present invention.
- FIG. 2 is a partial vertical cross-sectional view of the desuperheated water nozzle used in the present invention.
- FIG. 3 is an ee view of FIG.
- FIG. 4 is a front view showing another embodiment of the exhaust gas temperature reducing method and apparatus according to the present invention.
- FIG. 5 is a diagram of FIG.
- FIG. 6 shows still another embodiment of the exhaust gas temperature reducing method and apparatus according to the present invention, and is an explanatory diagram in a case where an alkaline aqueous solution is mixed into hot water as an alkaline solution. is there.
- FIG. 7 shows still another embodiment of the exhaust gas temperature reduction method and apparatus according to the present invention, and is an explanatory diagram in a case where an alkaline slurry solution is mixed into hot water as an alkaline solution.
- FIG. 8 is a curve showing the acidic gas removal characteristics in the exhaust gas according to the example of the present invention.
- FIG. 9 is a system diagram showing an example of a conventional exhaust gas cooling device.
- FIG. 10 is a system diagram showing another example of the conventional exhaust gas cooling apparatus.
- 1 is a gas cooling chamber
- la is an exhaust gas inlet
- lb is an exhaust gas outlet
- lc is an ash outlet
- 1 d is an airtight holding device
- 2 is a hot water tank
- 3 is a pump
- 4 is a deheated water nozzle
- 4 a is a spout
- 4b is a main body
- 4c is a spiral
- 4d is a water culvert
- 5 is a temperature control device
- 5a is an exhaust gas temperature detector at the outlet side
- 5a is an exhaust gas temperature detector at the outlet side
- 6 is the amount of water reduction Control valve
- G h is high temperature exhaust gas
- G 1 is low temperature exhaust gas
- S is heated steam
- C is ash
- Wt is hot water
- 7 duct
- 7a is flange for mounting desuperheated water nozzle
- 7 b is duct outlet
- 8 is an alkaline solution tank
- 8a is an alkaline agent supply
- FIG. 1 shows an embodiment of the exhaust gas temperature reduction method and apparatus according to the present invention.
- 1 is a gas cooling chamber
- la is an exhaust gas inlet
- lb is an exhaust gas outlet
- lc is an ash outlet.
- Id is an airtight maintenance device
- 2 is a hot water tank
- 3 is a pump
- 4 is a deheated water nozzle
- 5 is a temperature control device
- 5 a is an exhaust gas temperature detector at the outlet side
- 5 b is an exhaust gas temperature detector at the inlet side Vessel
- 6 is a dewatering water control valve
- Gh is high temperature exhaust gas
- G1 is low temperature exhaust gas
- S is heated steam
- Wt hot water
- C is ash.
- gas cooling chamber 1 is formed in a so-called tower shape, and the wall surface is formed in a heat insulating structure using a known heat-resistant material.
- An exhaust gas inlet 1 a is located above the gas cooling chamber 1, an exhaust gas outlet 1 b is located below the gas cooling chamber 1, an ash outlet 1 c is located at the lower end of the inverted cone below, and an airtight holding device (open / close damper) 1 d is provided. Is provided.
- gas cooling chamber 1 may have a form other than the tower type shown in FIG.
- the high-temperature exhaust gas G h (temperature of about 240, flow rate of about 90 °) discharged from the waste heat boiler (not shown) of the industrial waste incinerator into the gas cooling chamber 1 is used. , 00 O Nm 3 / H), but the temperature of the high-temperature exhaust gas G h for which the temperature is to be reduced is desirably 100 ° C. to 150 ° C. or so.
- the exhaust gas to be cooled may be exhaust gas from any combustion device, and the flow rate thereof is not particularly limited.
- the hot water tank 2 is made of a metal heat-resistant and pressure-resistant ink tank having the required capacity and is protected by heat insulating material.
- water (pressurized hot water W t) having a temperature higher than the boiling point (at 100) under atmospheric pressure is stored. is temperature 1 4 2.
- Water Wt is stored in a hot water tank 2 having a pressure resistance of 1 O kgZcm 2 .
- steam S for heating is introduced into a hot water tank 2 from a waste heat boiler (not shown) provided in an industrial waste incinerator, and is heated by the heat of the heated steam S.
- the temperature of the hot water Wt is maintained at the value of 142.9.
- the heat of the combustion gas and the combustion exhaust gas are used. It is also possible to adopt a configuration utilizing
- the continuous water from the boiler is used as a part of hot water, or if the boiler equipment is provided with a deaerator, degassing is performed. It is also possible to use high-temperature and high-pressure water generated in the vessel as hot water Wt or a part of hot water Wt.
- the pump 3 is for supplying hot water Wt to the deheated water nozzle 4, and the pump 3 is configured to supply pressure loss of piping between the hot water tank 2 and the deheated water nozzle 4 and the position of the deheated water nozzle 4. It will be installed only when necessary due to the water head.
- the desuperheated water nozzle 4 is a known hollow cone type nozzle as shown in FIGS. 2 and 3, and in the present embodiment, three jet ports 4a are provided at an angular interval of 120 ° C.
- One nozzle is provided at the center of the upper part of the gas cooling chamber 1.
- 4b is a main body
- 4c is a spiral
- 4d is a water introduction hole.
- the injection angle of each outlet 4a of the cooling water nozzle 4 is about 60 ° (when the ejection pressure is 3 kgf Zcm 2 ), and the flow rate is about 3.8 IZm in (the ejection pressure 3 kgf Zcm
- a hollow cone type spray nozzle as shown in FIG. 2 is used as the desuperheated water nozzle 4, but the type and structure of the desuperheated water nozzle 4 may be any.
- conventional room temperature water can be sprayed with a particle size of about 190 to 300 m under a pressure of 2 to 3 kg f Zcm2, it can be used satisfactorily in the present invention. it can.
- the temperature control device 5 has an exhaust gas temperature detector 5b on the inlet side and an exhaust gas temperature detector on the outlet side.
- Low temperature exhaust gas G 1 discharged from the exhaust gas outlet 1 by adjusting the amount of hot water sprayed into the gas cooling chamber 1 by receiving the temperature detection signal from the temperature detector 5 a and controlling the opening and closing of the dewatering water amount control valve 6 Is maintained at a set value.
- a thermostat type temperature detector is used as the exhaust gas temperature detectors 5a and 5b, but the type of the temperature detector used is not limited. You may.
- the dewatering water control valve 6 is provided in the hot water supply pipe.
- the dewatering water flow is provided in the return pipe of the hot water Wt.
- the control valve 6 may be provided, and any method may be used as long as the amount of hot water supplied to the desuperheated water nozzle 4 can be adjusted.
- the hot water in the hot water tank 2 is sent to the reduced-temperature water nozzle 4 by the internal pressure in the hot water tank 2 and / or the pressurized water supply force of the pump 3.
- the water is sprayed from the desuperheater nozzle 4 into the high-temperature exhaust gas G h.
- the hot water Wt sprayed from the desuperheated water nozzle 4 is high-pressure water at a temperature significantly higher than the boiling point (100 ° C) under atmospheric pressure.
- the low-temperature exhaust gas G1 cooled to a predetermined temperature is attracted to the outside through the exhaust gas outlet 1b, and ash (dust and the like) C in the separated exhaust gas is discharged from the ash outlet 1c to the outside. It is discharged to.
- the required volume of the gas cooling chamber 1 is 3 0 0 0 mm and a height of 6000 mm.
- the high-temperature exhaust gas Gh described above was sufficiently reduced to a low-temperature exhaust gas G1 at a predetermined temperature (180 ° C).
- the required capacity of the gas cooling chamber was about 4800 mm0 X 900 OmmH, and it has been confirmed that the size of the gas cooling chamber 1 can be significantly reduced in the present invention.
- the spray water amount of the hot water Wt is increased by about 20% as compared with the case where conventional water (20 ° C) is used.
- FIGS. 4 and 5 show another embodiment of the exhaust gas temperature reducing method and apparatus according to the present invention.
- the exhaust gas duct 7 for deriving the high temperature exhaust gas Gh discharged from the waste incinerator is provided on the side surface of the exhaust gas duct 7.
- the configuration is such that a flange 7a for mounting the desuperheated water nozzle 4 is provided, and the hot water Wt is sprayed from the desuperheated water nozzle 4 mounted on the flange 7a into the hot exhaust gas Gh in the duct 7.
- FIGS. 4 and 5 The embodiment shown in FIGS. 4 and 5 is different from the embodiment shown in FIGS. 1 and 2 only in that the gas cooling chamber 1 is replaced by a vertically long exhaust gas duct 7. This is exactly the same as in FIGS. 1 and 2.
- the hot water Wt is sprayed into the duct 7 to produce 9 000 ONm 3 H.
- the high-temperature exhaust gas Gh at a temperature of 240 ° C is continuously connected to the low-temperature exhaust gas G 1 at about 180 ° C at the duct outlet 7 b. The temperature could be reduced.
- FIGS. 6 and 7 show a third embodiment of the exhaust gas temperature reduction method and apparatus according to the present invention.
- the hot water nozzle 4 injects hot water Wt with hot water into the high temperature exhaust gas Gh in the gas cooling chamber 1 to remove the acidic components in the exhaust gas at the same time as the temperature of the exhaust gas is reduced (or neutralized). ).
- 8 is an alkaline solution tank
- 8a is an alkaline agent supply device
- 8b is a stirrer
- 9 is an alkaline solution pump
- 10 is an alkaline solution flow control valve
- 1 1 is an alkaline solution heater
- 1 1a is a drain discharge valve
- 1 2 is a mixer of hot water Wt and an alkaline solution Wp
- 13 is an acid gas concentration control device
- 13 a is low temperature exhaust gas.
- G 1 acid gas concentration detector, S, is a heating steam
- P is an alkali
- Wp is an alkaline solution.
- the other components are the same as those in Figs. 1 and 2.
- an alkaline aqueous solution is used as the alkaline solution Wp mixed into the hot water Wt.
- sodium hydroxide (caustic soda ) Is dissolved in the alkaline solution tank 8 in which the alkaline solution P is dissolved.
- the alkaline agent P that forms the alkaline aqueous solution may be any other than sodium hydroxide as long as it is soluble in water.
- magnesium hydroxide (Mg (OH) 2) may be used. May be.
- the concentration of the alkaline agent in the aqueous alkaline solution stored in the tank 8 is appropriately selected according to the temperature of the water and the solubility of the alkaline agent P used in the water W, and the alkaline agent P is used.
- the alkaline agent concentration is selected to be 20 to 30%.
- the alkaline slurry solution used as the alkaline solution Wp to be mixed into the hot water Wt is used.
- a solid-liquid mixture (slurry) in which an alkaline agent P such as lime (slaked lime 'Ca (OH) 2) is suspended in a dispersed state is stored in the alkaline solution tank 8 ⁇
- alkali agent P, 7XW it may be one as long as it is distributed to the inner to form a slurry other than the above calcium hydroxide, for example slaked lime (CaO) or calcium carbonate (C AC_ ⁇ 3) , And sodium carbonate (Na 2 C ⁇ 3 ) can be used.
- CaO slaked lime
- Ca AC_ ⁇ 3 calcium carbonate
- Na 2 C ⁇ 3 sodium carbonate
- the mixing amount of the alkaline solution Wp into the hot water Wt is determined by the detection signal from the acidic gas concentration detector 13 a in the low temperature exhaust gas G 1 via the acidic gas concentration control device 13.
- the adjustment is performed by controlling the opening and closing of the aqueous solution flow control valve 10, whereby the concentration of the acidic gas in the low-temperature exhaust gas G1 is maintained at a predetermined set value.
- the mixing amount of the alkaline solution Wp in the hot water Wt is determined based on the temperature of the low-temperature exhaust gas G1, the type of acid gas to be removed, the target acid gas removal rate, and the like. 1.0 to 1.5 times as much as the amount of acid gas to be removed in the hot water Wt is mixed into the hot water Wt.
- the alkaline solution heater 11 heats the alkaline solution Wp mixed into the hot water Wt to a predetermined temperature, and the temperature of the alkaline deheated water flowing out of the mixer 12 is significantly increased. To prevent the drop.
- the mixing amount of the alkaline solution Wp is small or the temperature of the alkaline solution Wp is relatively high (for example, 80 ° (: up to 90 ° C), the disturbance to the hot water Wt during mixing is relatively small. Therefore, in such a case, the installation of the alkaline solution heater 11 can be omitted.
- the configuration is such that the alkaline desuperheated water is injected into the gas cooling chamber 1, but the alkaline desuperheated water is replaced by the gas cooling chamber 1.
- Exhaust gas flow rate 900,00 ONm 3 / h (exhaust gas from waste heat boiler of industrial waste incinerator ⁇ HC1 concentration in exhaust gas 800 ppm), high-temperature exhaust gas Gh at a temperature of 240 ° C 180
- a tower-type cooling device having a cylindrical gas cooling chamber was formed.
- the cooling chamber 1 has an inner diameter of 3000 mm and a height of 600 mm.
- the high temperature exhaust gas G h is sufficiently reduced by using the gas cooling chamber 1 at a predetermined temperature (180 ° C.). The temperature could be reduced.
- the supply amount of the alkaline agent P to the amount of HC1 in the exhaust gas was 1.0 in equivalent ratio, and the removal rate of HC1 detected by the acid gas concentration detector 13a was the low-temperature exhaust gas. It was about 93% when the temperature of G1 was 180 ° C.
- the calculation of the supply amount of the alkaline solution Wp is as follows.
- the removal of the acidic gas in the exhaust gas by spraying the NaOH aqueous solution is based on the following reaction formula.
- NaCI or the like is post-processed by an electrolysis method or the like. However, since these processing methods are already known, the description thereof is omitted here.
- the alkaline solution heater 11 in consideration of disturbance to hot water Wt when an alkaline solution (25% NaOH aqueous solution) Wp at room temperature (25 ° C.) is mixed, the alkaline solution heater 11 is used in the present embodiment.
- the heating solution Wp is heated to about 80 ° C and then supplied to the mixer 12 Even if the heater 11 is not used, the alkaline hot water at the outlet side of the mixer 11 Due to the temperature drop, the amount of spray water from the desuperheated water nozzle 4 only slightly decreased, and no particular problem occurred.
- FIG. 8 shows the state of the change in the acid gas (HC 1) removal rate when the supply amount of the Na ⁇ H aqueous solution Wp supplied to the mixer 12 was changed in Example 3.
- Curve A shows the value when the temperature of the low-temperature exhaust gas G1 is set to 180 ° C
- curve B shows the value when the temperature of the low-temperature exhaust gas G1 is set to 150 ° C.
- the vertical axis of the curve is the acid gas removal rate%
- the horizontal axis is the amount of supply expressed by the equivalent ratio of Na ⁇ H.
- the sprayed hot water since pressurized hot water is used as desuperheated water, the sprayed hot water rapidly decompresses and boil near the outlet of the desuperheated water nozzle, and has a particle size of several im. It becomes a spray with fine particles and evaporates instantaneously to water vapor.
- the instantaneous evaporation of the sprayed hot water greatly improves the cooling performance of the spray water and makes it possible to significantly reduce the size of the gas cooling chamber. That is, in the gas cooling chamber to decrease warm water prior cold water, to a thermal load force generally about 5 0 0 0 ⁇ 1 5 0 0 0 kca 1 / m 3 ⁇ about H of the gas cooling chamber in contrast, the in gas cooling chamber of the temperature reducing apparatus according to the present invention, to increase the gas cooling chamber heat load 5 0, 0 0 0 ⁇ 1 5 0 , 0 0 0 kca 1 / m 3 ⁇ about H This makes it possible to significantly reduce the size of the gas cooling chamber.
- the equipment can be configured very simply and running costs can be significantly reduced.
- the incinerator or boiler equipment is provided with a deaerator, the hot water from the deaerator can be used as it is. All you need is facilities. As a result, the exhaust gas cooling system can be configured at extremely low cost.
- the gas cooling chamber itself can be reduced in capacity, or hot water can be sprayed into a duct for high-temperature exhaust gas without providing a gas cooling chamber, so that equipment costs can be significantly reduced.
- the continuous blow water of the boiler can be used as part of hot water for cooling water, and the blow water is alkaline with energy saving. As a result, the amount of chemicals in the flue gas desalination and desulfurization equipment can be reduced.
- the acidic gas in the exhaust gas can be removed at a high removal rate with a smaller amount of alkaline agent, and the exhaust gas can be reduced. It is possible to further reduce the size of the acid gas removal equipment installed downstream of the heating device and reduce the amount of chemicals used.
- the alkaline solution to be mixed into the hot water does not need to be heated to a high temperature, particularly by heating.
- the temperature of the hot water slightly higher, the alkaline solution at room temperature can be mixed into the hot water.
- stable operation of the exhaust gas temperature reduction device can be performed.
- the present invention has excellent practical utility.
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- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Chimneys And Flues (AREA)
- Treating Waste Gases (AREA)
Description
Claims
Priority Applications (6)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1020007003991A KR100345408B1 (ko) | 1999-01-18 | 1999-12-20 | 열수를 이용한 배출가스 감온방법 및 그 장치 |
EP99959931A EP1065444B1 (en) | 1999-01-18 | 1999-12-20 | Method for reducing the temperature of exhaust gas utilizing hot water |
DE69942997T DE69942997D1 (de) | 1999-01-18 | 1999-12-20 | Verfahren zur Reduzierung der Abgastemperatur mittels Warmwasser |
US09/639,662 US6523811B1 (en) | 1999-01-18 | 2000-08-16 | Method and device for temperature reduction of exhaust gas by making use of thermal water |
US10/301,734 US6712343B2 (en) | 1999-01-18 | 2002-11-22 | Method and device for temperature reduction of exhaust gas by making use of thermal water |
US10/756,417 US6841138B2 (en) | 1999-01-18 | 2004-01-14 | Method and device for temperature reduction of exhaust gas by making use of thermal water |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP884799 | 1999-01-18 | ||
JP11/8847 | 1999-01-18 |
Related Child Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
US09/639,662 Continuation US6523811B1 (en) | 1999-01-18 | 2000-08-16 | Method and device for temperature reduction of exhaust gas by making use of thermal water |
Publications (1)
Publication Number | Publication Date |
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WO2000042359A1 true WO2000042359A1 (en) | 2000-07-20 |
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ID=11704153
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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PCT/JP1999/007162 WO2000042359A1 (en) | 1999-01-18 | 1999-12-20 | Method and device for reducing temperature of exhaust gas utilizing hot water |
Country Status (5)
Country | Link |
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EP (1) | EP1065444B1 (ja) |
KR (1) | KR100345408B1 (ja) |
DE (1) | DE69942997D1 (ja) |
TW (1) | TW418305B (ja) |
WO (1) | WO2000042359A1 (ja) |
Families Citing this family (8)
Publication number | Priority date | Publication date | Assignee | Title |
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TW539828B (en) * | 2001-08-17 | 2003-07-01 | Nippon Oxygen Co Ltd | Cooling method and apparatus of emission gas with high temperature, and burning handling apparatus |
KR101013447B1 (ko) * | 2003-11-21 | 2011-02-09 | 모영환 | 구근 수확기 |
KR100837612B1 (ko) * | 2007-05-30 | 2008-06-12 | 이선영 | 반건식 반응탑용 염화수소· 황산화물 제거장치 |
CN103953936A (zh) * | 2014-05-04 | 2014-07-30 | 杨志军 | 一种可控制废气中污染物排放的烟囱 |
CH710092A1 (de) * | 2014-09-10 | 2016-03-15 | Robert Stucki | Verfahren zur raschen Abkühlung von Abgasen und Einspritzkühlvorrichtung. |
FI20146081A (fi) | 2014-12-10 | 2016-06-11 | Evac Oy | Jätteenkäsittelylaitteisto |
KR102146647B1 (ko) * | 2020-02-24 | 2020-08-20 | 임창호 | 열교환장치가 구비된 폐기물의 친환경 처리시스템 |
KR102146646B1 (ko) * | 2020-02-24 | 2020-08-20 | 임창호 | 폐기물의 친환경 처리시스템 |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5560894A (en) | 1992-09-16 | 1996-10-01 | Hokkaido Electric Power Co., Inc. | Process for treatment of exhaust gas |
JPH09187615A (ja) * | 1996-01-12 | 1997-07-22 | Babcock Hitachi Kk | 水蒸気凝集集塵装置及び集塵方法 |
JPH09250722A (ja) * | 1996-03-14 | 1997-09-22 | Mitsui Eng & Shipbuild Co Ltd | 廃棄物処理装置 |
Family Cites Families (2)
Publication number | Priority date | Publication date | Assignee | Title |
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US4804521A (en) * | 1986-11-07 | 1989-02-14 | Board Of Regents, The University Of Texas System | Process for removing sulfur from sulfur-containing gases |
NZ308045A (en) * | 1995-05-30 | 2000-01-28 | Thermal Energy Internat Inc | Flue gas scrubbing and waste heat recovery system |
-
1999
- 1999-12-20 EP EP99959931A patent/EP1065444B1/en not_active Expired - Lifetime
- 1999-12-20 WO PCT/JP1999/007162 patent/WO2000042359A1/ja active IP Right Grant
- 1999-12-20 DE DE69942997T patent/DE69942997D1/de not_active Expired - Lifetime
- 1999-12-20 KR KR1020007003991A patent/KR100345408B1/ko active IP Right Grant
- 1999-12-21 TW TW088122568A patent/TW418305B/zh not_active IP Right Cessation
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5560894A (en) | 1992-09-16 | 1996-10-01 | Hokkaido Electric Power Co., Inc. | Process for treatment of exhaust gas |
JPH09187615A (ja) * | 1996-01-12 | 1997-07-22 | Babcock Hitachi Kk | 水蒸気凝集集塵装置及び集塵方法 |
JPH09250722A (ja) * | 1996-03-14 | 1997-09-22 | Mitsui Eng & Shipbuild Co Ltd | 廃棄物処理装置 |
Non-Patent Citations (1)
Title |
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See also references of EP1065444A4 * |
Also Published As
Publication number | Publication date |
---|---|
KR20010015759A (ko) | 2001-02-26 |
DE69942997D1 (de) | 2011-01-13 |
KR100345408B1 (ko) | 2002-07-24 |
EP1065444A1 (en) | 2001-01-03 |
EP1065444A4 (en) | 2009-08-26 |
EP1065444B1 (en) | 2010-12-01 |
TW418305B (en) | 2001-01-11 |
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